About Environmental Law

Welcome to the home page for Environmental Law, the nation’s oldest law review dedicated solely to environmental issues. Environmental Law is a premier legal forum for environmental and natural resources scholarship. Environmental Law is published quarterly by the students of Lewis & Clark Law School, 10015 S.W. Terwilliger Blvd., Portland, OR 97219, in the Spring, Summer, Fall, and Winter. The views expressed in the volumes do not necessarily reflect those of the editorial boards.

Getting to Here: Bioregional Federalism

By Wes Nicholson*

Within some complex systems, structures not determined at the top level or planned from the outset may nevertheless develop over time as emergent properties arising as a result of the self-organization of the system. Market economies are one such species of complex system. Environmental problems are among the byproducts of modern market economies. Accordingly, environmental problems are byproducts of complex, self-organizing systems.

This Comment posits that a complex, self-organizing system for establishing environmental policy would be more competent to thoroughly police environmental problems than a command‑and‑control system for establishing environmental policy. Proceeding, this Comment suggests that the establishment of boundaries of legal effect along environmentally significant lines, structured to exploit a sense of “place,” could result in a system under which environmental policy might self-organize. Such a “Bioregional Federalism,” related to but distinct from existing notions of bioregionalism, ecosystem management, and watershed management, could provide a systemic basis for self-organizing environmental policy.

This Comment concludes with an extended thought experiment exploring how Bioregional Federalism might be achieved.

 

I. Introduction

In the face of socioeconomic activity, the environment doesn’t take care of itself. Environmental degradation seems to be the default path of modern society absent conscious ameliorative efforts. Such conscious effort expended in pursuit of more environmentally protective policies can mitigate environmental degradation, but the cost in political capital can limit the scope, duration, and effectiveness of those policies. As a result, environmental problems emerge more quickly than they can be thoroughly policed. Our approach toward establishing environmentally protective policies leaves us chronically playing the part of a harried bureaucrat, running down the road after the problem, paperwork in hand.

This Comment posits that our system for establishing environmental policy has a structural problem that exacerbates all of our environmental problems, but that a structural mechanism may exist that could address this underlying structural problem. That structural mechanism lives in the overlap of two seemingly disparate political philosophies, one a product of the modern environmental movement, the other as old as the United States itself. The pairing may amount to a case of politics making strange bedfellows. However, there is evidence to suggest that the citizens of this country may be receptive to cross-ideological solutions to our pressing national problems.[1]

This Comment is speculative and exploratory in nature. Part II identifies our environmental problems in general as byproducts of a complex system. Part III first summarizes the philosophy of bioregionalism, as well as its more practically-minded relatives, ecosystem management and watershed management, then proposes a structural mechanism to mitigate these complex-system byproducts. Part IV is an extended thought experiment exploring how that structural mechanism, implementing a politics of place, might be achieved. Reflections on all of this follow in Part V.

II. Our Complex, Systemic Environmental Problem

A. The Persistent Difficulty of Environmental Problems

Generally speaking, environmental problems are a natural consequence of human industry. A business will have an environmental impact to one degree or another in the simple course of doing business.[2] The impact a business has upon the environment is not present as a force guiding its decisions in the same way as other forces acting on it, such as the need to secure funding, gain customers, and in general grow the business with a view to profits. At the same time, environmental impacts are not present as a force guiding governmental decisions in the same way as other forces faced by those in government, such as the need to discern and establish policies both proper and feasible on behalf of one’s constituency, most often in a partisan environment (and, perhaps, with an eye to preserving one’s own position and interest in government).[3]

Admittedly, a business may seek to become green, embracing business practices or developing products with an eye to reducing environmental impact. Admittedly, there are statutes and regulations outlining environmental policies, groups organized to petition the government for redress regarding environmental grievances, and factions in the electorate for whom environmental policy informs their votes—and thus pressures elected office-holders—to one degree or another.[4] However, all of this requires force of will to maintain. The green practices a business may embrace, or the development of environmentally minded products, may be subject to change in the face of conflict with more immediate interests of the business. Similarly, absent sustained political pressure, desirable environmental policies may never come to pass. Even where stated governmental environmental policies are at issue, countervailing political pressures may result in those environmental policies being given short shrift at enforcement time. Altruism is constantly subject to headwind forces.

At the same time, the difficulty of addressing many environmental problems is complicated by their cross-jurisdictional nature.[5] When the policies of more than one state or jurisdiction contribute to an environmental problem, the political will of all states or jurisdictions involved must be brought to bear in order to coordinate, negotiate, and reach agreement.[6] Thus, there is also a persistent barrier to entry for solutions to cross-jurisdictional environmental problems.

With respect to governmental policy, the forces set against altruism, as well as cross-jurisdictional barriers to entry, sap the will behind environmental policies. Assuming that industry will always be with us, environmental problems will always be with us. The establishment and enforcement of environmental policies will in turn always be hindered by dependence upon continuing political will.

B. Complex Systems, Self-Organization, and Emergent Properties

Complexity theory observes that some systems in which multitudes of independent actors are governed by simple rules may not only
possess surprising structural complexity, but may also be capable of self‑organization and self-regulation.[7] Such systems may have properties that are not direct results of the particular set of rules in the system, but that instead emerge as indirect, iterative, cumulative consequences of the operation of the system under that particular set of rules over time.[8]

A number of phenomena serve as examples of emergent properties of self-organizing, complex systems. Biodiversity may be seen as an emergent property of life under forces of evolution over vast spans of time—as one species succeeds and becomes plentiful, other species can succeed by relying on it as food, and the balance between populations of predator and prey becomes self-regulating over time.[9] The variety of languages may be seen as an emergent property of linguistic evolution among multitudes of peoples over time, constrained by an ingrained nature of grammar acting as the simple rules out of which complexity may arise.[10] The Internet in its current abundance came to be not because a government decreed its structure, but rather emerged because certain building blocks became available (URLs, servers, and site hosting services) and individuals, compelled by their own self-interest (ranging from hobby to profit) each built up one small part of it.[11] Even the Constitution may be seen to have implemented a system having emergent properties: Power is separated at the federal level into the three branches,[12] counting by design on the jealous tendencies of each branch to guard its own power to serve as a check on power’s inherent self‑aggrandizing nature,[13] an arrangement which is (mostly) self-regulating, and under its constraints, our complex government has evolved.

Similarly, a free market secures contracts and property rights, and the resulting system in its startling variety provides a mechanism—an imperfect mechanism, to be sure, but still an effective mechanism—by which employment, material wealth, and prosperity are created and distributed, generally speaking, for the greater part of its constituent members.[14] The  system does not specifically mandate these results. Instead, interestingly, a free market exploits the self-interest of individual actors therein, and the results emerge from the self-organizing system as it operates.[15] By relying on the inherent force of human self-interest, no force of will on the part of government is required in order to guarantee, by dictate, specific economic benefits. Instead, society seems guided as if by an “invisible hand” to act in such ways as to ultimately provide them.[16]

These benefits do not magically appear without any effort by any party. Indeed, to establish and run a business is a continuing act of will. However, the will involved is not the force of will exercised by a top-level actor (such as a government), but is rather the force of will of many actors distributed within the system, as guided by self-interest. Thus, in a market economy, from the perspective of top-level actors, solutions to economic problems appear to be self-organizing. That is, to a certain extent, economic problems seem to solve themselves.

C. Self-Organizing Environmental Policy

Our environmental problems are also the aggregate results of the acts of a multitude of independent actors. Individuals, businesses, and government may not set out to directly cause environmental impacts. Instead, they are byproducts of our social system. Since our social system fundamentally establishes a free market, those environmental impacts may be understood largely as being byproducts of a self-organizing, complex system. In other words, our complex, systemic problem is that our environmental problems as a whole are an emergent property of a complex, self-organizing system—a free market. Accordingly, it would be unsurprising if a command-and-control system for establishing environmental policy proved to be no more competent to thoroughly police those environmental problems than a command-and-control economy would prove to be in keeping pace with the underlying free market itself.

However, what if there was some force that our social system could exploit—analogous to the force of self-interest in a market system—that could guide the establishment of environmental policy? If it could be found, such a force could provide the basis for a systems-theory version of fighting fire with fire, or setting a thief to catch a thief. If the system establishing environmental policy could exploit such a force, perhaps an “invisible green thumb” could be set to tame the “invisible hand.” Doubtless, environmental policy would still require acts of will. However, if such a force could be exploited, from the perspective of top-level actors, solutions to environmental problems might appear to be self-organizing. Under such conditions, environmental problems might seem to solve themselves.

III. Exploiting Place Toward Self-Organizing Environmental Policy

In searching for a force to exploit in establishing self-organizing environmental policy, the philosophy of bioregionalism would be a profitable first stop. Bioregionalism maintains that political interests should be aligned with environmental boundaries.[17] Under the bioregionalist view, the inherently greater concern people are capable of having for their own immediate environment, as opposed to the concern people are capable of having for the environment in general, can act as a force for more environmentally sound policies.[18] Political decisions would therefore inherently come to take environmental considerations into account, as a result of living, so to speak, more directly in the “here” in which we find ourselves.[19] If this is true, then if bioregionalism were established, perhaps environmental policy could become self-organizing. However, bioregionalism as presently envisioned is extremely politically problematic.

A. The Bioregional Vision

Over twenty years ago, Kirkpatrick Sale summarized a vision for a social order capable of resolving the severe environmental stresses that characterize the modern world.[20] Under this social order, called bioregionalism, humanity would become “dwellers in the land,” approaching the environment with an admiration and respect born of “understand[ing] place, the immediate specific place where we live.”[21] This understanding would derive from knowing the constituent elements of the environment, understanding the limits to development that the environment can tolerate, and appreciating the relationship between human societies and the environment.[22] Ultimately, under a bioregional social order, the boundaries of social power would shift from political boundaries that have no particular relationship to the environment to bioregional boundaries existing in harmony with the environment.[23]

In the simplest case, bioregionalism might be conceived as the redrawing of political boundaries along more environmentally directed lines.[24] However, the extent and ambition of the bioregional vision described by Sale encompasses much more than a mere redrawing of boundaries. Sale described bioregionalism as being profoundly different from what he dubbed the “industrio-scientific paradigm.”[25]

As envisioned, bioregionalism is bundled with extreme changes to the social, political, and economic order. First of all, in a bioregion reoriented toward goals of conservation, stability, and cooperation, market structures would be abolished.[26] Economic activity would be communally directed and planned,[27] property would be communally owned,[28] and labor would be essentially selfless and community-directed, “performed without the idea of a wage return or individual benefit, indeed largely without the notion of ‘work’ at all.”[29]

Further, in such a bioregion, governance would be radically decentralized and organized around relatively small numbers of people (ranging in size from one thousand to ten thousand),[30] and would potentially aggregate into larger “confederate bodies.”[31] Such societies would be nonhierarchical, resembling tribal societies,[32] and the fundamental social values of some of those societies might depart disturbingly from traditional American or even western norms.[33]

Finally, the social fabric under bioregionalism would be vastly changed. Massive population dispersal would be undertaken in the course of establishing symbiotically dependent rural and urban areas.[34] Fashions would cease to be driven by the new and would instead be driven by
slow-to-change “images of sustenance and maintenance.”[35] Moral codes would be reoriented such that actions causing severe ecological harm would be classified on the order of murder and treated accordingly.[36] Even limited bioregional warfare, on the off chance that it were to occur, would be conducted in an environmentally cognizant, environmentally friendly way.[37]

As a practical matter, the achievability of any of these hard facets of the described bioregional vision lies between hard to imagine and flatly unrealistic. Beyond these hard facets, however, lie soft facets—attitudes and aesthetic trappings—that deepen the gulf between the vision and much of the body politic.

Beginning with appearances, a certain melodrama runs through the vision, from the description of the alternative to the industrio-scientific paradigm (“to become ‘dwellers in the land’”[38]), to the characterization of the scientific worldview as “our god,”[39] to the statement that “[t]he effect of scientific technology . . . has been to put a vast psychic distance between humans and nature,”[40] to his ultimate message that “[i]t behooves us . . . to give up those unearthly, demonic practices that threaten in so many ways the fundamental forms of life.”[41] Perhaps the vision is merely intended to be communicated to a fairly small audience, as a matter of preaching to the choir. However, the ideologically attuned presentation is likely to prove discordant to others.

Further “soft” facets of the vision may be even more difficult for the temperamentally skeptical to take. The vision evinces a fairly uncritical reverence of tribal life (both of Native Americans and of early or tribal societies elsewhere) that seems informed by “noble savage” sentiment.[42] At the same time, the vision greatly disparages the modern way of industry, economy, and society,[43] and presents something like a bioregional order as practically necessary to stave off impending environmental Armageddon.[44]

Of particularly grievous impact to the vision is its presentation, as a spiritual matter, of a necessity to preserve Gaea: not the colloquial “mother earth,” a “mother” only figuratively speaking, but rather “the earth mother,” a living entity whose personification is meant literally.[45] As the vision puts it, “We must try to learn that [Gaea] is, in every real sense, sacred, and that there is therefore a holy way to confront her and her works, a way of awe and admiration and respect and veneration that simply will not permit despoliation or abuse.”[46] The vision would seem to require that religious devotions be radically altered on the road to bioregionalism.

Other features of the vision can give a reader pause. It tends to acknowledge the difficulties inherent in many of his policy proposals, but then, having acknowledged the difficulties, it brushes lightly past them.[47] The work is dated, as well. The vision was captured in the mid-1980s, before the fall of the Berlin Wall, let alone the fall of the Soviet Union. Accordingly, its reliance upon such hard-socialist or communist standbys as economic planning is understandable. On the other hand, in light of the subsequent real-world failures of just the sorts of social models that are part and parcel of it, such policy prescriptions do not further endear the bioregional vision to modern audiences.

Under Sale’s bioregional vision, a simple redrawing of boundaries along environmentally friendlier lines is weighed down by a heavy cargo-load of far-left socioeconomic policy programs. To those already in agreement with most aspects of the vision, it may well sound both plausible and attractive. Accordingly, perhaps a small subset might rally behind the vision as stated. However, those not already in agreement will find much about which to be dismissive. Given that the supporting coalition would likely be thin, at best, the vision as it stands is little more than a pipe dream. A more widely palatable bioregional vision, if it could be found, would be required to make place a feasible force to consider exploiting toward self-organizing environmental policy.

B. Bioregionalism’s Cousins

The philosophy of bioregionalism did not arise in isolation from the rest of the world, and the same sorts of concerns that inform bioregionalism have informed similar notions, of which some have had more mainstream success. In the search for a more widely palatable bioregional vision, it may be instructive to examine two of bioregionalism’s cousins: ecosystem management and watershed management.

1. Ecosystem Management

a. Defined

Ecosystem management approaches land management policy from a regional ecosystem perspective. Ecosystem management views non‑ecosystem boundaries (such as state lines that might divide an ecosystem) as obstacles that must be overcome in the course of managing ecosystems, which are seen as units that are far more fit for analysis than traditional states.[48] Ecosystem management is characterized by increased interagency cooperation (including consultation and coordination), analysis of the impact of resource management proposals on ecosystems, commitment to preserving biodiversity, and commitment to preserving the aesthetic integrity of the environment.[49] Notable principles of ecosystem management include collaborative decision building, organizational change, and operating under a systems perspective.[50] Ecosystem management recognizes that people are part of an ecosystem and that human needs will play some role in the management of ecosystems.[51]

Ecosystem management is seen as a mechanism to deal with the mismatch between administrative boundaries and “meaningful ecological boundaries.”[52] It is seen as a means of addressing complicated problems,[53] of accommodating nondevelopment interests in lands,[54] and of holistically dealing with the full range of known environmental stressors.[55]

b. History and Current Practices

The roots of ecosystem management may be traced back at least to the late 1800s, when worries arose about the future of the nation’s natural resources in the face of rapid development.[56] In 1891, the Forest Reserve Act,[57] as modified by the later Organic Act,[58] provided “broad management authority” of public forest lands.[59] In 1905, Gifford Pinchot, the head of the Division of Forestry within the United States Department of Agriculture at the time, established the early principles of “multiple use and sustained yield management,” called “wise use,” under which lands were to be managed “from the standpoint of the greatest good of the greatest number in the long run,” although “good” was seen as primarily from the perspective of development, not what would modernly be seen as environmental or aesthetic concerns.[60]

The perception of what uses are “good” changed with the Multiple-Use Sustained-Yield Act of 1960[61] to include such things as recreational and aesthetic uses.[62] In the 1970s, “development” uses became further restricted.[63] In the 1960s and 1970s, both Yellowstone and the Great Lakes, respectively, were the subject of early ecosystem management efforts.[64] From these roots, “ecosystem management” as a formal idea arose in the 1980s and came to prominence in the 1990s.[65]

As of 1990, the federal government was beginning to experiment with ecosystem management.[66] The National Environmental Policy Act (NEPA)[67] was seen as imposing procedural requirements, if not substantive requirements, toward ecosystem management,[68] a position that was seemingly validated by the Supreme Court.[69] NEPA regulations were seen as requiring an accounting for the “cumulative impact” of the sorts of development proposals under consideration that might impact an ecosystem, leading to an evaluation of the aggregate impact upon the ecosystem of multiple similar development proposals.[70] NEPA regulations were also seen to require an assessment of “the impact of resource management decisions on shared ecosystems,” although courts were seen to have not “been eager to expand NEPA obligations beyond traditional jurisdictional boundaries.”[71]

By 1996, United States Forest Service regulations had incorporated ecosystem management principles,[72] and at least eighteen federal agencies were exploring ecosystem management.[73] In addition, 105 independent ecosystem management efforts were underway at various locations around the country,[74] primarily managed at the local level and directed toward specific problems.[75] States were also experimenting with ecosystem management.[76]

c. Prescriptions

Based on the available ecosystem management experiences, emphasis has been placed on making sure that nondevelopment uses are not lost among development uses in determining which uses should go forward.[77] One commenter saw a synthesis of concern for development and concern for ecosystem integrity, concluding that “[m]aintaining [v]iable [e]cosystems” would best serve development interests in the long run.[78] The importance of accounting for the effects of cumulative uses of the land was noted.[79]

Finally, the administrative nature of ecosystem management implies that the region being managed must be administrable. Interestingly, watersheds have been identified as among the more easily defined sorts of ecosystem, which may make them advantageously administrable.[80]

d. Problems

As it stands, ecosystem management is problematic. Without clear federal guidance, “ecosystem management” has had a range of meanings, particularly diverging among “biocentric” (directed toward environmental preservation) and “anthropocentric” (directed toward serving society) meanings.[81] Some perceive that ecosystem management could drift backward into “wise use,” with its attendant focus on social exploitation of environmental resources, unless it consciously directs itself toward environmental preservation.[82] Lack of funding for ecosystem management has been an issue.[83] The fact that nonprofits are deeply involved in many ecosystem management efforts has been seen as a point of concern with respect to “institutional design and accountability.”[84] Ecosystem management has also come under fire for radically departing from traditional governmental approaches involving fixed boundaries,[85] for being based on false notions that ecosystems can be nonarbitrarily defined,[86] and because the federal government is not a credible implementer of ecosystem management practices.[87]

Ecosystem management remains plagued by unresolved issues including vague policy goals, difficulties defining ecosystems, and difficulties defining the size and the position within a jurisdictional hierarchy of areas to be administered.[88] Significantly, ecosystem management still encounters difficulties accounting for “the interests and positions of numerous actors, both inside and outside of government.”[89] Despite the efforts of ecosystem management to overcome the misalignment of ecosystem and political boundaries, such problems remain. Decision makers “often face incredible political or administrative hurdles.”[90] The “numerous land management planning processes initiated by different federal and state agencies” waste precious time and resources.[91] Despite the best of intentions, lack of cooperation and “administrative red tape” remain problematic.[92] Coordination problems among federal and state participants have not disappeared.[93]

Interestingly, in a survey of ecosystem management efforts, the five most-cited outcomes were “procedural in nature.”[94] That’s a lot of procedure to move through before getting to results. Put another way, the problems of ecosystem management would seem to be centrally procedural in nature.

2. Watershed Management

a. Defined

Watershed management may be seen as one type of ecosystem management where the ecosystem in question is a watershed. Watershed management focuses on the water flowing into a river and the land from which that water flows.[95] Watersheds are seen as particularly apt ecosystems to serve as focal points for management efforts.[96] Although watersheds are much more concretely definable than other sorts of ecosystems, there is some variance as to what they encompass. In one sense, watersheds are basically river drainage basins.[97] However, watersheds may also be defined to include the soil and plants of the drainage basin, as opposed to (for example) the mere existence of a sloped contour of land down which water will run.[98] More finicky definitions distinguish between what might be called a “watershed proper” and other portions of a drainage basin, such
as catchments.[99]

As does ecosystem management, watershed management wrestles with the sorts of problems that arise when political boundaries are not aligned with watershed boundaries, such as cross-boundary coordination problems and interjurisdictional problems.[100] Watershed management is addressed to the full range of watershed stressors, such as timber harvesting, grazing, mining, and water diversions,[101] from the premise that if management is not undertaken at the watershed level, stressors in one part of a watershed might impact some other part of the watershed.[102]

b. History and Current Practices

As with ecosystem management, the roots of watershed management may be traced back to the late 1800s.[103] John Wesley Powell advocated that the American West be organized on the basis of watersheds.[104] “Watershed values”—specifically, the prevention of “destructive floods that result from inadequate forest cover”—were the basis for the Timber Culture Act of 1873.[105] Later, the President’s ability to reserve national forests was created by the Forest Reserve (or Creative) Act of 1891,[106] and the subsequent Forest Service Organic Act of 1897[107] declared that forest reserves were “established . . . to improve and protect the forest within the boundaries[] [and] for the purpose of securing favorable conditions of water flows.”[108] Interestingly, the Supreme Court’s decision more than eighty years later in United States v. New Mexico[109] found that water yield was the principal aim of the establishment of the National Forest system.[110]

Around 1900, the concept of “unified river basin management” took hold.[111] Unified river basin management, as the name suggests, was a watershed-level management philosophy, although one primarily directed toward development ends.[112] The years between 1900 and 1990 can be divided into three periods. In the first period, from 1900 to 1933, river basin management was oriented toward development uses, such as flood control, irrigation, and power generation.[113] Federal legislation established large projects in watersheds for development purposes.[114] Comprehensive watershed management legislation was considered but never adopted.[115]

In the second period, from 1933 to 1965, river basin management was oriented toward uses associated with economic improvement, such as hydropower.[116] Comprehensive watershed management legislation was considered again, during the New Deal, but not adopted,[117] and was considered and passed over yet again in the Truman and Eisenhower administrations.[118]

In the third period, from 1965 to 1990, a promising approach to cross‑jurisdictional river basin management was attempted by the Water Resources Planning Act of 1965 (WRPA).[119] In the end, this approach failed, largely because the provisions of the Act prevented it from exercising any real authority in cases of conflict with existing federal or state law.[120] Before failing, the Water Resources Council (established by the WRPA) reported that watershed management should be conducted by that level of government of the most appropriate scale.[121] At the same time, “watershed” was established as a coequal use among multiple uses for national resources planning purposes.[122]

c. Prescriptions

Since a watershed is impacted by uses within the river basin, watersheds (and watershed management) are important in general in multiple-use management analyses,[123] serving as an indicator of the “health of the land.”[124] Laws impacting watershed management are many and are related in complicated ways.[125] The abilities of a watershed management effort to cross political barriers[126] and establish cooperation among the relevant agencies[127] is important to effective watershed management.

One commentator has called for mandatory ecosystem and watershed management,[128] active local participation in watershed management projects,[129] and more effective implementation structures.[130] Another commentator has called for an embedded hierarchy of watershed management programs at various levels of “scale” in the hierarchy of a watershed (the way small streams feed into larger streams, or the way small governmental units such as counties are related to larger governmental units such as states),[131] as well as for local authority trumping federal authority on watershed management requirements.[132] The Committee on Watershed Management of the National Research Council has called for flexibility and responsiveness to local control[133] and “an era of flexible federalism” in which state and local governments would have substantial control over watershed management programs.[134] The Committee has also noted that coordination and cooperation will continue to be difficult to achieve unless real authority is vested in watershed management programs, and that in the meanwhile, the ad hoc arrangements that have characterized watershed management to this time may be the best arrangement possible.[135]

d. Problems

As with ecosystem management, watershed management efforts have their share of problems. Mission definition—whether development, or preservation, or both—is a source of difficulties.[136] There are difficulties defining the “watershed” to be managed.[137] Questions of whether an effort should be watershed management or ecosystem management also arise.[138]

Involvement on the part of the federal government brings problems as well. The “strong federal presence” required to enforce the management plan may not be appropriate and may act as a magnet for opposition, provoking “strong resistance.”[139] Finally, fragmented responsibility and dispute resolution methods in the event of interagency turf battles drag down watershed management programs.[140]

Again, as with ecosystem management, the misalignment of political boundaries and watershed boundaries is a major problem. It appears to be a larger problem for watershed management than for ecosystem management. Perhaps the relatively more definable nature of watershed boundaries, and therefore the more concrete nature of watershed management programs, clarifies boundary misalignment problems. Watershed management efforts are “difficult to create and, when established, tend to lack political viability.”[141] Perverse incentives may be inherent in the structure of some watershed management regions.[142] Cross-boundary coordination and cooperation is hampered by “frequent disagreements . . . with regard to water resources issues.”[143] Larger regions may see greater institutional conflicts and political rivalries.[144] Lack of system-wide policy coordination reduces watershed management effectiveness, leading to potential endangerment of the watershed.[145] The lack of alignment between watershed boundaries and political boundaries has negative political, institutional, and funding ramifications.[146]

Various levels of government jealously guard their spheres of authority, which hinders watershed management efforts.[147] Policy-wise, watershed management can be most effective if it impacts an entire river basin; but for large river basins, watershed management efforts impact and involve more stakeholders, which can lead to decreased cooperation and turf battles.[148] Finally, watershed management efforts under no federal coordination or direction (of the sort seen to date) can lead to a bewildering mess of various management schemes.[149]

C. A Different Bioregional Vision

When political jurisdictions and environmentally significant geographical partitions are not the same, environmental problems crop up. Initially, those problems are due to lack of coordination and cooperation among the various jurisdictions. It seems, however, that problems due to cross-jurisdictional governance exist even under modern ecosystem management and watershed management efforts. The bioregional vision of the 1980s is a nonstarter.  In the search for a more widely palatable bioregional vision that could exploit place toward self-organizing environmental policy, is there anything left? Perhaps the bioregional vision can be retooled. What if bioregionalism were stripped down to an essential constituent part? Posit a different bioregional vision, in which it is arranged to redraw political boundaries such as state lines to align them with environmentally significant partitions. Posit that this arrangement establishing bioregionally organized states is almost entirely structural and procedural in nature. In other words, the arrangement would purely concern itself with redrawing state boundaries, and would be utterly agnostic to specific, substantive matters of environmental policy. Such matters would include not only the many politically contentious facets of Sale’s bioregional vision, but even the question of where policy lines should be drawn between “biocentric” and “anthropocentric” values. Instead, the authority to make decisions regarding substantive matters of environmental policy would simply be granted to bioregionally organized states. What could be said about such an arrangement?

First of all, lacking the hard and soft facets of the original bioregional vision, the arrangement would be more palatable outside of the original vision’s narrow, sympathetic audience. There would be no radical reengineering of the fundamental nature of society, no quasi-religious aesthetic baggage—just the framing of the governing structure of society as squarely as possible with respect to the environment. (At the same time, although the bioregionally organized states would not be forced to adopt any of the hard or soft facets laid out by Sale, they would be free to do so under this different bioregional vision.)

Furthermore, the theories behind ecosystem management and watershed management suggest that even a relatively procedural change, such as establishing bioregionally organized states, could yield environmental benefits. Indeed, ecosystem management and watershed management are predicated on just such an outcome: Establishing bioregionally oriented states should have an inherent positive effect because the match between ecosystem and government jurisdiction, or between watershed and government jurisdiction, would be made more perfect, thus lowering potential barriers to entry to the establishment of environmentally protective policies.

In fact, a realignment of boundaries might address many of the problems observed under ecosystem management and watershed management programs. In bioregionally organized states, many vexing issues would become moot, or less pressing. There would be no need to repeatedly and artificially assemble interested parties, as must be done under ecosystem management and watershed management efforts. Rather, all interested parties in a jurisdiction would already have clear means of support for their involvement by virtue of the ordinary, usual, and traditional mechanisms for state governance. Accordingly, ad hoc management efforts would no longer need to depend upon the service—perhaps the altruistically rendered volunteer service—of interested parties since each bioregionally organized state would already have an infrastructure of representative government. There would be no need to coordinate and agree upon the “mission” of the management effort before the management effort could get underway, the continuously operative default mission being to choose between the range and mix of development and preservation uses available to the ecosystem or watershed. The question of funding would reduce to how much funding is given for any internal land management purpose, as opposed to rounding up impromptu sums in order to implement externally driven management efforts. The system of government need not radically change to mitigate observed procedural problems with management efforts; only the boundaries of the government need be any different than what has come before.

To be certain, environmentally favorable outcomes under such an arrangement would not be specifically guaranteed. That is to say, when choosing between development and preservation, a bioregionally organized state could pick a mix of uses less than one hundred percent preservation, since there is no accounting for the will of the people. However, that is true even presently. It would seem that, if anything, the playing field would be tilted more in favor of environmentally sensitive results than the status quo. Cross-jurisdictional barriers to entry for more environmentally minded policy would be minimized, and instead of needing to fight a procedural headwind, environmentally minded policies would have the wind at
their back.

In addition to the minimization of cross-jurisdictional barriers to entry, another force would likely affect environmental policy in each bioregionally organized state. Observation of the “NIMBY” (“Not In My Back Yard”) phenomenon suggests that jurisdictions resist development uses that may have environmental impacts within their borders.[150] In a bioregionally organized state, each decision of that state that could impact its associated parcel of the environment would result in the same bioregionally organized state living with the costs and benefits of that decision. A nationwide system of bioregionally organized states could result in an unbroken coast-to-coast patchwork quilt of backyards, each backyard encompassing an environmentally significant unit in which the NIMBY phenomenon would supply an inherent force toward environmentally protective policy. From the perspective of complexity theory, then, the redrawing of political boundaries in line with environmentally significant partitions could exploit forces related to place. Those forces—such as the NIMBY phenomenon, and reduced barriers to entry for environmentally minded policies—might create an invisible green thumb, by virtue of which solutions to environmental problems would be self-organizing; again, not in the sense that solutions would require no force of will, but rather in the sense that the top-level of the system need not specifically direct the shape and nature of those solutions to bring them to fruition. In so doing, the establishment of bioregionally organized states may provide a systemic mechanism to address our complex, systemic environmental problem. Under such a system, environmental problems might be adequately policed as, or before, they arise. Most significantly, while shedding various politically disadvantageous traits of the original bioregional vision, the establishment of bioregionally organized states would retain at least one highly politically advantageous trait. The original bioregional vision encompasses a decentralization of authority from a federal government to more local levels. This is in harmony with the modern federalist argument: Local control is better control.[151] Accordingly, not only might an arrangement of bioregionally organized states appeal to a wider segment of the left-hand end of the political spectrum, but adeptly presented, it could authentically appeal to a broad segment of the right-hand end, too; and an embrace wide enough to reach both ends of the spectrum might also encompass the vast swath in-between. A “grand bargain” marrying a bioregional arrangement so defined, and a federalist arrangement as modernly understood, could make this different bioregional vision—Bioregional Federalism—feasible, resulting in a system which is more sensitive to “the immediate specific place where we live.”[152] In establishing self-organizing environmental policy, Bioregional Federalism could guide our society to inherently live in a more environmentally responsible manner in the “here” in which we find ourselves.

Well.

How do we get “here”?

IV. Getting to Here

The redrawing of state boundary lines in an arrangement implementing Bioregional Federalism would constitute a change of extreme magnitude. How could such an arrangement be made maximally feasible?

As a preliminary matter, as discussed above, one fundamental problem of defining regions along environmental lines for any purpose is that such lines are inherently difficult to draw. Any bioregional boundary redrawing arrangement would therefore have to determine what should be the basis for defining the bioregions. Should they be defined by the range and mix of species found therein, for example? Alternatively, should they be defined by climate? Watersheds seem to be the most administrable method of defining bioregions. Therefore, the most feasible approach would probably be to define bioregions on the basis of watersheds.[153]

What other factors might theoretically shape the feasibility of an arrangement to redraw political boundaries along bioregional lines?

A. General Factors Impacting Feasibility

1. Constitutionality

As a threshold matter, one fundamental factor impacting the feasibility of an arrangement implementing Bioregional Federalism would be arguments about under what conditions the arrangement is constitutional at all. Could such an arrangement be validly enacted merely by federal statute? The Constitution stipulates:

New States may be admitted by the Congress into this Union; but no new State shall be formed or erected within the Jurisdiction of any other State; nor any State be formed by the Junction of two or more States, or Parts of States, without the Consent of the Legislatures of the States concerned as well as of the Congress.[154]

Given the clear text of the Constitution, if a bioregional arrangement were statutorily based, state boundary lines could not be redrawn with respect to any states refusing to participate in the arrangement.

Moreover, even with respect to states agreeing to participate, a statutorily proposed arrangement to implement bioregionally oriented states might provoke counterarguments that the arrangement is inherently unconstitutional. A general formalistic counterargument could be phrased in a number of ways. It might be argued that in the course of modifying state boundaries, the House of Representatives would cease to “be composed of Members chosen every second Year by the People of the several States,”[155] because subsequent to implementing a bioregional arrangement, one or more of “the several States” to which the text refers would no longer exist. An analogous argument might be made with respect to senators.[156] Furthermore, if a bioregional boundary redrawing resulted in adjustment to the jurisdictional boundaries within the federal judiciary, it might also be argued that the judges in any jurisdictions so affected might not be “hold[ing] their Offices during good Behaviour,”[157] because the changes to the boundaries of their jurisdictions constitute a removal of office. Essentially, these general counterarguments would maintain that the nature and substance of either the states or the federal government is changing in some way that subtly calls into question whether the structure of the states or the federal government under the new arrangement is constitutional at all.

A specific version of the general counterargument would refer to the language at the end of Article V that limits the range of permissible constitutional amendment by providing, inter alia, that “no State, without its Consent, shall be deprived of its equal Suffrage in the Senate.”[158] If a new arrangement is seen to have deprived a state of its equal suffrage in the Senate, then the arrangement’s constitutionality may be questioned.

If judicial review of the arrangement were sought on such grounds, the judiciary would have recourse to interpretive approaches that would remove such obstacles. For example, in the case of the general counterargument, a court could simply decide that the House of Representatives is, in fact, composed of members chosen by the citizens of the several states, even if that set of states has changed. Similarly, in the case of the specific counterargument regarding Article V, a court could simply decide that while the states have changed, if each new state has equal suffrage in the Senate, then the mere change from one set of states to another does not violate Article V.

Even given the flexibility of judicial review, a constitutional amendment may make a boundary redrawing arrangement more feasible, as any problematic constitutional provisions could be cast as having been either explicitly or implicitly altered by the amendment process. Amendment could allow a bioregional arrangement to apply even to holdout states.
In addition, amendment would lend strength to jurisprudential interpretations concluding that the arrangement merely and permissibly adjusts the states upon which constitutional provisions depend, rather than impermissibly dispossessing them. That additional support may help to overcome even the specific counterargument under Article V.

On the other hand, constitutional amendment requires overwhelming political will, which would reduce the feasibility of arrangements rooted in amendment. However, for purposes of clarity of discussion, it may be easiest to assume that the arrangement is established through constitutional amendment.

2. Degree of Change and Divisibility

Beyond constitutionality, other fundamental factors that would affect the feasibility of a bioregional arrangement would be, in a broad sense, the degree of change involved and the severability of the arrangement’s provisions.
Generally speaking, in any political matter, the smaller the change involved, the less political will is required to make the change. This is the same perspective that would judge the enactment of Sale’s bioregional vision as stated to be inconceivable, whereas a stripped-down, re-tuned bioregionalism focused solely on changing boundaries may be judged more feasible. If the changes involved even in a bioregional arrangement could be made smaller, or parceled into smaller pieces, they may be made
more feasible.

Divisibility of the arrangement would also impact its feasibility. To the extent that the changes involved can be applied piecemeal, the success of the enterprise as a whole may not be subject to the failure of any of its constituent elements. Additionally, if any portion of a bioregional arrangement could be enacted, at least some of the benefits of the arrangement may begin to accrue.

What other factors might shape the feasibility of a bioregional arrangement?

B. Specific Factors Impacting Feasibility

1. Changes to the Number of States

If those changes that are smallest are most easily accepted,
a bioregional arrangement preserving the number of states would be more feasible. A geographical region exerts influence within the federal government in two places: 1) in each house of the Legislature, and 2) in the number of electors used to elect the President.[159] If the states in a particular geographical region were to dissolve and re-form as a different number of states, the influence of that region within the federal government would either increase or diminish. In either case, replacement with a different number of states would be a source of discontentment with the arrangement and would reduce the political will in support thereof.

Consider the case in which an arrangement would cause the states in a region to re-form as a larger number of states. First, the Representatives associated with that region would shift within the region, as each new state’s share of the House of Representatives is settled. This consequence might be the least troublesome because, while the ratio of representatives to citizens might change for any subregion, the change to the region’s proportion of the House would likely be marginal.

However, a second consequence would be likely to have significant impact: If the number of states were to increase within a region, that region would gain more seats in the Senate. Not only would this increase the region’s influence in the Senate itself, but it would also result in increased influence in the presidential election process, as that region would have more electors than before. States outside the region would have their influence diluted, and would therefore be less likely to accept an arrangement which could include such a consequence.

There is a related difficulty in the case in which an arrangement would cause the states in a region to re-form as a smaller number of states. Again, representatives would shift within the region, but the change to the region’s proportion of the House would likely be marginal. However, the region itself would be faced with diminished influence in the Senate and the presidential election. States in that region would therefore be less likely to accept an arrangement that could include such a consequence.

An arrangement increasing or decreasing the total number of states might preserve the proportion of federal influence exerted by each region over the Senate, if the increase or decrease were uniformly applied, such as a proportional increase or decrease applied nationwide. For example, if each existing state were replaced by two new states in a bioregional arrangement, the resulting doubling of the number of states, and thus the doubling of the number of senators, would not change the proportion of any region’s influence over the Senate.

However, such a change may still encounter second-order problems. First of all, if an arrangement changed the number of senators (or, for that matter, the number of representatives), then the way in which business proceeds in the legislature would change. Procedures that have evolved and developed to accommodate the current number of members might need to change to accommodate a new number of members. Furthermore, the part played by each congressperson in “the life of the nation” would change if the size of the house in which he or she sits were to increase or decrease, which might provoke resistance to the arrangement. For example, each senator, currently in a position of high federal influence, would be less influential if there were twice as many as there are currently.

Finally, if the number of representatives did not change but the number of senators did (or if the two numbers changed by different ratios), the balance of power between relatively more populous regions and relatively less populous regions in determining the outcome of presidential elections would change, and could provoke resistance. For example, if the number of states increased, then the total proportion of the electoral college vote related to the number of senators would increase, increasing in turn the influence in the electoral college of regions whose fraction of federal political influence is governed more by the number of states therein than upon by the population therein.

2. Piecemeal Adoption Among the States

Allowing some regions to electively redraw their associated state boundaries without all regions doing so would increase the divisibility, and therefore the feasibility, of a bioregional arrangement. Boundary redrawing within any one region would not have to wait on the completion of a holistic boundary redrawing scheme in all regions. Delay might arise in a holistic arrangement where a contentious boundary redrawing in one region is held up by political interests. Delay might also arise where political interests in one region hold up boundary redrawing in another region. At any rate, the proliferation in the number of parties interested in the shape of the entire arrangement would increase the opportunity for contention.

3. Changes in Legal Authority and Changes in Law

Presuming that the boundaries of a state had been redrawn, what would be impacted? State legislatures pass statutes, state administrative agencies promulgate rules, and a state’s judiciary digests and interprets those statutes and rules.[160] However, the principle of least change would counsel that minimum change coincide with a new boundary arrangement. To force each new state to absorb massive changes of law over broad regions contained therein would represent precisely the sort of large change that should be avoided for the sake of feasibility.

Indeed, maintaining existing law upon changing boundaries would be consistent with the intent of the arrangement. An arrangement implementing Bioregional Federalism need not seek to establish environmentally infallible policies at the outset; rather, it would be forward looking, being designed to make future policies in a bioregionally arranged government more environmentally sound. It would be sufficient for boundary redrawing activities to merely establish new governmental authorities to create new policies, while retaining old policies until those new policies could be developed. Thus, if each subpart of a new state were to maintain the statutory, regulatory, and judicial law from whichever state previously contained that subpart, and if changes to the law of the new state as a whole were only incorporated incrementally as time moved forward, an undesirable extent of change could be mitigated.

4. Regions of Federal Legal Effect

Policies with environmental impact are not solely determined at the state level. At the federal level, the legislative branch makes laws, the executive branch promulgates rules, and the judicial branch creates precedent,[161] any of which could amount to or contribute to policies having environmental impact. In the bioregional vision, policies set at the federal level should also respect bioregional boundaries. For example, a constitutional amendment to establish a bioregional structure in federal policy-making bodies could be severed from any activities to reconstitute states along bioregional lines.

Even so, it is conceivable that bioregionally oriented boundaries that might be used to set policy at the federal level might not be the same as those used to set policy at the state level. Some current states contain many watersheds, and states subsequent to a bioregional arrangement may well also contain multiple watersheds or “lengths” of watershed; and there may be no reason that watershed-based boundaries of federal policy would necessarily be arranged to contain the same watersheds.

However, allowing watershed-based boundaries of federal policy to differ from watershed-based boundaries of state policy would run counter to the intent of the bioregional arrangement. If different federal policy-making agencies defined regions of federal legal effect with no thought to state boundaries or even regions defined by other agencies, the citizens of any given bioregionally oriented state might be forced to split their attention between multiple regions defined by, for example, the United States Environmental Protection Agency, the United States Army Corps of Engineers, the United States Bureau of Land Management, and the United States Fish and Wildlife Service, in order to competently interact with those various federal agencies in pursuit of sound environmental policy on behalf of their state.

It would be in greater harmony with the bioregional arrangement if the citizens of a single state would not have to divide their attention to policy matters between multiple regions of federal legal effect. Thus, any redrawing of boundaries of federal legal effect in a national bioregional arrangement ought to respect bioregionally oriented state boundaries.

5. Intrastate Bioregionalist Structure

Even if legal boundaries at the state level and federal level were aligned with respect to watersheds, there are other legal boundaries that would not be—namely, county and city boundaries, and also administrative boundaries within states. An amendment severable from the broader bioregional arrangement could address this, with reference to Article IV, Section 4 of the Constitution, by requiring that a “Republican Form of Government” mandates bioregionally oriented county boundaries as well (such as county boundaries determined with respect to watersheds).

There would be a potential problem with judicial enforcement of intrastate bioregional boundaries so determined: The Supreme Court held in Baker v. Carr[162] that claims related to the Guaranty Clause present nonjusticiable political questions.[163] In doing so, the Court relied on a couple of earlier cases. In the first case, Luther v. Borden,[164] the Court reasoned that since Congress must determine whether or not a state has a republican form of government before the state may enter the union, the responsibility for enforcing the Guaranty Clause rests with Congress.[165] In the second case, Minor v. Happersett,[166] the Court reasoned that since the Guaranty Clause does not spell out what it means by “Republican Form of Government,”
it has to look elsewhere to find out what that means, and concluded that the states have a duty to understand what that means in order to be able to supply it.[167]

These nonjusticiability concerns may disappear in the case of the aforementioned amendment to adjust the Guaranty Clause. First, under the amendment, new states could be admitted to the union not in the Article IV sense, but rather in the sense of being either “formed or erected within the Jurisdiction of any other State,” “formed by the Junction of two or more States,” or some combination of the two.[168] There is no addition of territory as implied by being “admitted,” merely a shifting.[169] Beyond that, the amendment itself could elaborate on what is meant by “Republican Form of Government,” in particular as it would apply to parties seeking judicial review with respect to bioregionally determined intrastate boundaries. Therefore, the amendment may be valid and sufficient grounds for the Court to adjust its Guaranty Clause doctrine.

6. Federalism: The Grand Bargain

Decentralization of governmental power is a strong theme of bioregionalism.[170] The basic idea is that local communities are best able to implement policies to look after the health of their own environmental regions.[171] This notion is cousin to current sentiments regarding centralized government power on the other end of the political spectrum. If a bioregional constitutional arrangement were looking for allies among a broader range of voters, a constitutional amendment to strengthen the decision-making authority of state governments in matters traditionally left to the federal government could be the key to establishing feasibility.
An amendment increasing state control of matters impacting environmental policy might increase support for the broader arrangement.

C. A Thought Experiment: Iterative Two-State Boundary Redrawing

1. Hypothesis

An arrangement that seeks to impose a specific bioregional structure from on high would be politically difficult, requiring as it would the sort of widespread agreement that has proven procedurally problematic in ecosystem management and watershed management. On the other hand, what may be a difficult question for a nation of states to resolve—how to determine bioregional boundaries over a vast geographical expanse—may be far easier for small sets of individual states to resolve in consultation and negotiation amongst themselves. If such negotiations could be carried out iteratively, for example, by dealing with boundaries between small sets of states independently, with the aim of growing a bioregional arrangement from the bottom up instead of imposing one from the top down, a bioregional arrangement might become more feasible.

a. State Representation in the Boundary-Redrawing Process

Assuming an iterative boundary-redrawing process, who should be involved in the consultations and negotiations? A fitting answer would be to have the existing states, or representatives of them, negotiate. Tying the decision-making process to states would have an added advantage of providing additional legitimacy at the level at which legitimacy would be needed, and therefore improving feasibility; to the extent that control over the actual process would be retained close to the people, support for the process would likely increase.

Presuming that negotiators representing the states were to direct the decision-making process, who ought those negotiators be? If they are left to be chosen by the governments of the states, those already holding positions in the government may be high on the list of candidates. However, the participation of such people in the decision-making process may be tainted by a desire to safeguard their own fortunes in government.

Article I, Section 6, of the Constitution contains a provision to prevent legislators from being positioned to exert unseemly influence:

No Senator or Representative shall, during the Time for which he was elected, be appointed to any civil Office under the Authority of the United States . . . ; and no Person holding any Office under the United States, shall be a Member of either House during his Continuance in Office.[172]

A similar provision to prevent negotiators acting on behalf of states in the decision-making process from being entangled in government (at either the state or the federal level) would help to ensure that those negotiators would be of, by, and for the people of the state.

b. A Two-State Method for Boundary Redrawing

Assuming that states are to be involved in the negotiations, and presuming that it would be advantageous to preserve the number of states, how should the negotiations proceed? Of the myriad ways to determine bioregions, watersheds have advantages due to their concreteness, but a watershed-based scheme is not without challenges.

First, at what regional scale should watersheds serve as guidance, and what sort of guidance should they provide? The continental United States does not contain an intuitively obvious set of forty-eight watersheds to be used as the basis for forty-eight bioregionally oriented states. Furthermore, consider the most prominent watershed in the United States: the Mississippi River. The Mississippi defines borders of nine states, and
its tributaries, such as the Missouri River and the Ohio River, define borders of more.[173] To both contain the entire Mississippi River watershed in one state and preserve fifty states would not only imply a state with a far greater share of federal political power than any current state, but would require a process by which a large number of states would need to be allocated to other regions in order to preserve their existence.

Such conditions might be less problematic if there were some way to split a watershed among more than one state. On the other hand, preventing the division of environmental boundaries is the general motivation behind an arrangement implementing Bioregional Federalism in the first place.
Could watersheds be split in a way that would not make a hash of the broader goals of the arrangement?

The general problem of allowing a water feature, such as a river, to serve as a political boundary is that all states sharing the river must coordinate to obtain effective environmental policy regarding the same stretch of river. This may be distinguishable from a scenario in which a single river flows through more than one state. In the latter scenario, “upstream” and “downstream” portions of a watershed could be spread between two different states, and one state acting alone would at least have sole discretion to set and enforce environmental policy with respect to the portions of the watershed draining from both sides into the associated portion of the river’s length. The resulting state boundaries would at least be more in line with the broader goals of the arrangement than current state boundaries. Interestingly, since the Constitution provides for extending judicial review to “Controversies between two or more States,”[174] if responsibility for the watersheds feeding into discrete lengths of a river were clearly apportioned, it may be easier to conceptualize addressing environmental controversies between states—for example, over water quality—through existing judicial mechanisms.[175]

Therefore, states might be preserved in a way that would not moot the larger bioregional arrangement if, in the course of arriving at the arrangement, the states were allowed to segment a watershed if required in order to “partition” lengths of a river. For example, for a given length of river bordered by any two states, a negotiation among those two states could establish an “upstream” portion of the river and a “downstream” portion of the river such that, for each portion, all land draining into that portion of the river (i.e., the watershed associated with that portion of the river) would reside in one state. Such a provision would accommodate bisection of a river in a manner aligned with watershed flow, allowing even large rivers, such as the Mississippi, to be split among multiple states.

Second, what specific procedures could constitute a reasonable process for determining new boundaries? This a question of fair division: How could all states in a region come up with a plan to fairly divide that region among themselves using watersheds as a guide? Consider the Mississippi River as an example again, and the nine states whose borders are, in some portion, defined by it. Should negotiators for all nine states gather together to discuss a new arrangement of boundaries? How would consensus be reached among nine parties? Any given length will be of little interest to most parties and of fierce interest to a few. Given that, who should propose the new set of boundaries? In determining a proposed new set of boundaries, what would ensure that the proposing party be both sufficiently interested in lengths of remote consequence and sufficiently disinterested in lengths of immediate consequence to make neutral and fair proposals regarding the full length of the watershed? Unless one state’s negotiators are given some special status, wouldn’t negotiators from each state be likely to make their own proposal, resulting in up to nine distinct proposals? How could states adequately evaluate a large number of likely divergent proposals and come to awell-grounded consensus on any one
of them? If these questions are then extended to include the many states that don’t directly border the Mississippi River, but drain into its tributaries, the difficulties explode.

The assumption that each state would be primarily concerned with those lengths of rivers most immediately tied to its boundaries suggests a solution. Assuming that a river defines a boundary between states, there will be a length of that river sufficiently small that it defines the boundary of only two states. At that granularity, if those two states could come up with some way to avoid splitting that watershed—unless to bisect it in a manner aligned with watershed flow—other states in the watershed may well not care. Additionally, if only two states are involved in a discussion to redraw a shared boundary, an easy answer to the fair division problem is available: one state divides, and the other state chooses.

Therefore, if the redrawing of political boundaries is broken down into a series of two-state fair-division problems, a complicated multistate fair‑division problem—one that may not be feasibly surmountable—could
be sidestepped.

c. A Method for General Boundary Redrawing

Assuming a two-state boundary-redrawing arrangement, how could it be incorporated into a continent-wide boundary-redrawing arrangement? What if iterations of the two-state fair-division arrangement are not sufficient to handle all cases? Congressional involvement in a continent-wide arrangement could help to smooth things out. First, Congress could enumerate the sets of boundaries between states that currently are not guided by watersheds. The list of boundaries not so guided is likely to include almost all existing boundaries, since it would include any boundaries described in part by a river or the shore of a lake, and any boundaries described in part by a straight line running latitudinally or longitudinally. This could define the range of redrawing activities to occur. Next, Congress could select the sets of boundaries to redraw, and the order of redrawing them, such that the related two-state negotiations could proceed simultaneously, and Congress could direct the whole process in order to conclude it on a certain timeline.

It could be important for the process to have a timeline—if the national will demands that the nation move in a bioregional direction, it would be unsatisfying if the process unfolded so slowly that its ultimate completion is called into question. However, some interstate negotiations may be complex enough, or the negotiators may be intransigent enough, that specific boundary negotiations may not be completed in a timely manner.

In order to handle cases in which states cannot come to agreement because of intransigence, but also to handle any case in which the redrawing activities are stalled (perhaps due to unforeseen conditions that may prohibit fair division), it could be beneficial to include a catch-all
“escape clause” giving Congress the ability to redraw a state boundary if the bordering states themselves are not able to do so. This might occur if two states were to realize that their existing watersheds would only result in a lopsided “fair division,” at which point the states might signal to Congress their resignation in the effort. Alternatively, if each two-state negotiation were allotted a set amount of time, the inability of two states to arrive at a “fair division” solution within that time might trigger the “escape clause” and cause responsibility for that specific redrawing activity to be handed over to Congress—which could be a powerful motivator to the states involved to complete the negotiation on their own. In such ways,
an “escape clause” provision could provide for timely resolution, through one mechanism or another, of all redrawing activities.

In a similar vein, it could be beneficial for Congress to take
time to study the broader arrangement before setting individual
two-state arrangements into motion. It may be that ordering the two-state arrangements in one way would lead to more tractable boundary resolution than ordering them in another way. However, random selection of two-state arrangements would be the means least amenable to
“gaming the system,” or exerting undue influence over the proceedings to any one state’s advantage. Therefore, if Congress were allowed to order the proceedings, it might be prudent to limit its ability to do so to such ordering that would minimize nontractable two-state arrangements.

d. Timeline

There is no reason that the mere close of negotiations in any particular two-state arrangement should imply that the new bioregionally oriented states thereby determined are ready to pick up their respective mantles of governance. Even if a newly created state government did not need to absorb changes in law over some portion of its regions, the new state may not have the legislative, executive, and judicial structure in place to promulgate any new policy. Therefore, some time ought to be allotted after creation of new boundaries for provisions and institutions of new governments to be created and prepare for governance.

e. Potential Amendments

Following are a set of hypothetical Amendments drafted with the above matters in mind, in which existing States choose representatives
to negotiate, as “States-in-Waiting,” in the establishment of new watershed‑based States.

AMENDMENT 1[176]

Section 1. When two States seek to redraw their boundaries in the manner provided for by this Amendment, said States sharing a boundary that splits a watershed in a manner described by this Amendment, the Legislatures of each State must Consent to the redrawing and report that Consent to the Congress; but no Consent of Congress shall be required to form or erect either new State resulting therefrom, and those new States shall be deemed admitted by the Congress into this Union in the time and manner described by
this Amendment.

Section 2. Before beginning the redrawing activities, the two States involved shall specify a date by which the redrawing activities will be concluded; but in no event will the amount of time from the Consent of the States to the end of the redrawing activities exceed four years.

Section 3. The citizens of each State involved shall choose, by apportioned vote, five persons to negotiate on behalf of that State, as a State-in-Waiting. All such negotiators shall meet the qualifications for service in the Senate of the United States; shall not occupy any civil Office which shall have been created under the Authority of either the United States or the patron State; and shall not be a Member of the House of Representatives of the United States, the Senate of the United States, or any legislative body of the patron State.

Section 4. Each State-in-Waiting involved will begin the redrawing activities with partial custody of the existing boundaries of its patron State. The two States-in-Waiting involved shall negotiate with each other with respect to the boundaries over which they each have partial custody in order to arrive at two redrawn sets of State boundaries, including a new boundary dividing the States; but no redrawn State boundary shall in any part split a watershed, unless to bisect it in a manner aligned with watershed flow. After reasonable negotiation, one State-in-Waiting, identified by chance, shall propose two new sets of redrawn State boundaries; and the other State-in-Waiting shall assign partial custody of the two sets of redrawn State boundaries to each of the two States-in-Waiting involved as it so chooses.

Section 5. No change in boundary should imply a change of legal authority at any geographical point until ten years after the resolution of State boundaries along watershed lines, at which point new boundaries shall attain legal effect.

Section 6. No change in boundary or legal authority should imply a change of law at any geographical point unless a newly constituted legal authority so deems, except that a State Constitution shall pass from each State to its associated State-in-Waiting. At that point, any legal authority whose sphere of authority contains law from more than one previous State may have free initial choice of law from any such previous source, in a manner consistent with the degree of discretion given to it in its institutional role.

AMENDMENT 2[177]

Section 1. Congress shall identify any State boundary that in any part splits a watershed, unless to bisect it in a manner aligned with watershed flow, as a State boundary to be redrawn.

Section 2. Within one year of passage of this Amendment, Congress shall determine the complete list of State boundaries to be redrawn, and shall determine therefrom an amount of time allowed for each phase of the general redrawing activities sufficient to permit all State boundaries to be redrawn, reserving sufficient time for itself to redraw any intractable boundaries; but the entire time from passage of this Amendment to completion of the redrawing of all State boundaries shall not exceed ten years.

Section 3. Congress shall study the general redrawing activities, and shall identify any boundaries that cannot tractably be redrawn through two-state negotiation unless some portion of the general redrawing activities proceed in an identifiably constrained order. In no event shall Congress take more than one year to determine the set of such boundaries and the ordering required to make them tractably redrawable by the States.

Section 4. Congress and the States-in-Waiting shall undertake the general redrawing activities in a series of phases, each phase comprising the activities in Section 5, until all State boundaries have been redrawn, or until the only remaining boundaries are not tractably redrawable by negotiation between States-in-Waiting.

Section 5. Subject to modification where required based on identifiable ordering constraints described in Section 3, Congress shall select through chance a State boundary to be redrawn, and in that manner continue selecting State boundaries to be redrawn subject to the following limits and constraints: Congress shall accommodate redrawing activities initiated by any set of two States but still in progress by including those boundaries among the first selection; No State-in-Waiting shall be involved in the redrawing of more than one of its boundaries in any one phase of the general redrawing activities; If a boundary chosen through chance is not tractably redrawable, that boundary shall be passed over until a subsequent phase; and Selection of boundaries in any one phase shall end when no State-in-Waiting with a tractably redrawable boundary remains. Once a set of boundaries to be redrawn has been selected, the redrawing activities will proceed as described in Amendment 1.

Section 6. If a negotiation does not end by the time allotted within the phase as set by Congress, the boundary in question will be deemed wholly intractable by the States, and will be removed from consideration in the general redrawing activities, to be reserved for resolution by Congress.

Section 7. At the end of the general redrawing activities, Congress shall redraw boundaries that were not tractably redrawable by the States in whatever manner it so chooses, taking care that the new boundaries do not in any part split a watershed, unless to bisect it in a manner aligned with watershed flow

Section 8. Once all State boundaries have been redrawn, custody of the final boundaries of each State-in-Waiting will be turned over to its patron State.

AMENDMENT 3[178]

Section 1. Congress shall not establish or suffer any boundary of federal legal effect—legislative, executive, or judicial—that divides a State; nor shall Congress establish or suffer any boundary of federal legal effect that in any part splits a watershed, unless to bisect it in a manner aligned with watershed flow, or unless that would prevent a boundary from being properly determined on the basis of population.

Section 2. Congress shall have ten years after the resolution of State boundaries along watershed lines to modify existing boundaries of federal legal effect in accordance with this Amendment.

AMENDMENT 4[179]

Section 1. In the United States, with respect to the several States, a Republican Form of Government shall be a form of government in which no boundary between counties, nor any boundary of State legal effect—legislative, executive, or judicial—shall in any part split a watershed, unless to bisect it in a manner aligned with watershed flow, or unless that would prevent a boundary from being properly determined on the basis of population.

Section 2. Each State shall have ten years after the determination of county boundaries along watershed lines to ensure a Republican Form of Government within that State.

AMENDMENT 5[180]

No policy that may affect the environment in a given region will have legal effect unless it is established both by the State government associated with that region and the federal government.

2. Experiment

How might a boundary-redrawing arrangement unfold under these rules? Following are two test cases of specific iterations of two-state boundary redrawing according to the arrangement established by the amendments above.

a. Negotiating States: Oregon and Washington


Figure 1: Oregon and Washington

As seen in Figure 1, the border between Oregon and Washington is prominently defined by the Columbia River. The starting point would be to examine the region in terms of its watersheds. To a rough approximation, where two water features are separated on this map, some geographic feature divides them such that one side of the divide drains through a watershed into one water feature, and the other side of the divide drains through another watershed into the other water feature.

Figure 2: Oregon and Washington, with
Approximated Watershed Divisions

 

 

In Figure 2, approximated watershed divisions in the region of the Columbia River have been added (see the light dashed lines). Under the “one state divides, and the other state chooses” mechanism described in the Amendments, if one state-in-waiting proposed a new set of state boundaries establishing a northern state encompassing all of the Columbia River (although perhaps not all its watersheds), the other state-in-waiting would likely seek to claim that northern state, since it would not merely contain all the Columbia, but would include politically, socially, and economically key territory, such as the areas around the northern Willamette River (including Portland) and the greater Seattle-Tacoma metropolitan area.

Figure 3: Oregon and Washington, with Approximated
Watershed Divisions and Proposed New Boundaries

 

Therefore, self-interested proposals would likely look to establish a boundary that bisects the Columbia in a manner aligned with watershed flow. In that event, a couple of different arrangements might be considered: a first arrangement including a redrawn state encompassing both the Willamette River watershed and the watershed containing the Seattle-Tacoma area, but consciously attempting to limit the geographic area of that state in order to make the remaining state as large as possible (see the heavy dotted line in Figure 3); and a second arrangement including a redrawn state encompassing the Willamette River watershed, but not the Seattle-Tacoma watershed, and dividing up the remainder of the states as fairly as possible in that context (said fair division being likely to allocate more land to the Willamette River region, given the size in population and financial terms of the Seattle-Tacoma area with respect to the Portland area) (see the heavy dashed line in Figure 3). The second arrangement might be more likely, since each set of negotiators would likely prefer at least one area of high population, given that two are available.

b. Negotiating States: Tennessee and North Carolina

Figure 4: Tennessee and North Carolina

 

 

As seen in Figure 4, the border between Tennessee and North Carolina is not defined by a prominent river. Instead, it is a case where the existing border largely appears to already exist between watersheds. In this case, an adjustment of the border to not split watersheds except in a manner aligned with watershed flow might merely amount to shifting the existing border (see the heavy dotted line and heavy and dashed line in Figure 5).

Figure 5: Tennessee and North Carolina, with Approximated Watershed Divisions and Proposed New Boundaries

Precisely which new boundary line would be agreeable to both states would depend upon how closely the existing boundary line hews to a watershed division. If the watershed division is such that it is primarily to the east of the existing boundary line, a first arrangement compensating on the northern end of the new boundary for land “lost” by North Carolina on the southern end of the new boundary might be more likely. On the other hand, if the watershed division is primarily to the west of the existing boundary line, a second arrangement compensating on the northern end of the new boundary for land “lost” by Tennessee on the southern end of the new boundary might be more likely.

3. Conclusions

The largest drawback of an iterative two-state arrangement implementing Bioregional Federalism is that it may not satisfy what might be called a “bioregionalist aesthetic.” The states that result from this process will have boundaries that have shifted; but under the constraints of both preserving fifty states and centrally involving the states in the redrawing exercises, each state may be related to more than one watershed, and include some portion of, but perhaps not all of, any one of those watersheds. This is not as theoretically pleasing as a clean, one-to-one mapping of watershed to unit of political control would be. Not only that, but once the process is complete, the boundaries will have changed, but the vertices in the “network” of boundaries—the corners between the states—will be the same; and if there was no reason to trust that borders defined by water features or by latitude or longitude lines would lead to a harmonization between politics and environmental concerns, there may similarly be no reason to trust that the vertices between them would, without more, be harmonious themselves. Finally, the range of watersheds (and perhaps portions of watersheds) in a new state might not have a clean relationship to some of the other potential measures of a bioregion, such as climate conditions or species mix and distribution.

One possible partial cure would be to initiate a process in which more than two states would negotiate a new arrangement at once. This would have the advantage of potential flexibility even at the vertices. However, as discussed above with respect to the example of states in the Mississippi River watershed, the fair division problem becomes much more complicated once it involves more than two parties, especially when (as would be the case here) it is not a mere matter of divvying up an area, but rather divvying it up into geographically intact parts.

Another possible partial cure would be to wipe the slate clean and not worry about preserving fifty states. An arrangement so based would involve much more significant change, and would therefore require more social agreement before it could become feasible. A middle ground might be for Congress to wipe the slate clean but commit itself to finding fifty regions, which would preserve the number of states while allowing for more direct conformance to a “bioregionalist aesthetic.” However, either case would hand Congress a massive political and logistical problem and demand that Congress solve it, which would require a great deal of trust in its institutional competence, and which may reduce the feasibility of
an arrangement.

On the other hand, even if the amendments above led to an arrangement on the “warty” side of the “bioregionalist aesthetic,” it would still be less “warty” than what exists now. Given the multiple ways in which bioregions might be drawn, it is already certain that there is no such thing as a perfect set of bioregional political boundaries. Perhaps the arrangement would be only a step, but it may be a step in the right direction—although the question would remain of whether the step is significant enough to justify the pain involved in taking it.

V. Reflections

In exploring the establishment of bioregionally oriented states as a means of establishing self-organizing environmental policy, this Comment makes no claims of infallibility. With luck, it points out some of the major forces that would shape such an arrangement and some features that might make the arrangement more feasible in light of those forces. Even lacking the hard and soft aspects of the original bioregional vision, Bioregional Federalism alone would seem to involve changes of such extreme magnitude as to make even a maximally-feasible bioregional arrangement seem implausible. Hopefully, this Comment may serve to suggest by way of example (albeit perhaps by poor example) that such things are thinkable.

Whatever the strengths of Bioregional Federalism may be, the prospect of addressing our complex, systemic environmental problem is appealing.
If a system could be established in which environmentally protective policies were self-organizing, environmental problems might seem to solve themselves. At the same time, absent some mechanism in support of self‑organizing environmental policy, a command-and-control system for establishing environmental policy may be inadequate to deal with the environmental impacts that are the byproducts of a complex system—meaning, the byproducts of our market economy. This may in turn force unhealthy political reactions to environmental problems.

As tends to be true for political matters in general, environmental policy to correct environmental impacts will be, to the extent left to political solution, defined by partisanship, and will not be strongly related to rational, broadly undertaken discourse.[181] Under such conditions, environmental impacts may beget environmentally sensitive yet partisan responses, needlessly increasing political animosity in the process. Ugly thought and word may build upon ugly deed to the detriment of potentially more harmonious solutions, until the environmental situation becomes dire enough that shocking and extreme measures are imposed. Perhaps the most important aspect of self-organizing environmental policy would be its service as a bulwark securing freedom from its own potential excesses.

There may be real environmental value to Bioregional Federalism in achieving self-organizing environmental policy, but any realistic proposal would require much further thought. There would certainly be legal effects and consequences, some no doubt profound, that this Comment has not suspected. No course of action that is ill-thought-out can claim the auspices of wisdom. Accordingly, to any who may be intrigued by the potential of self‑organizing environmental policy in general, or by the potential of this different bioregional vision in particular, this Comment issues a call to armchairs.



* Form & Style Editor, Environmental Law, 2008–2009; Member, Environmental Law, 2007–2008; J.D. 2009, Lewis & Clark Law School; S.B. 1996, Massachusetts Institute of Technology. All underlying maps are derived from U.S. Geological Survey, U.S. Dep’t of the Interior, National Atlas of the United States of America: Rivers and Lakes (2003), available at http://www-atlas.usgs.gov/printable/images/pdf/outline/rivers_lakes.pdf. Comments and questions may be directed to the author at wesley09@lawalumni.lclark.edu. The author thanks Professor Steve Kanter and Professor Peter Nycum for guidance and feedback regarding earlier drafts of this Comment. The author also thanks the staff of Environmental Law for their rigorous and gracious editorial assistance. Finally, the author wishes to thank his parents, Wes and Sue Nicholson, for their care; his sister, Jeanette Wiersma, for times shared; his children, James and Blakeley, for providing the reasons; and his wife, Pamela, who makes all things possible.

[1] President Barack Obama, Inaugural Address (Jan. 20, 2009) (transcript available at Posting of Macon Phillips to the White House Blog, President Barack Obama’s Inaugural Address, http://www.whitehouse.gov/blog/inaugural-address (Feb. 20, 2009, 13:27 EST) (last visited Apr. 18, 2010)) (“On this day, we come to proclaim an end to the petty grievances and false promises, the recriminations and worn-out dogmas that for far too long have strangled
our politics.”).

[2] Richard York et al., Footprints on the Earth: The Environmental Consequences of Modernity, 68 Am. Soc. Rev. 279, 279 (2003).

[3] See, e.g., Posting of John M. Broder to The Caucus, Climate Change Bill Is in Doubt, http://thecaucus.blogs.nytimes.com/2010/01/20/climate-change-bill-is-in-doubt (Jan. 20, 2010, 18:55) (last visited Apr. 18, 2010) (discussing significant scaling back of energy and climate change legislation pending in Congress in order to “focus[] more on job-creating technologies than on limiting climate-altering pollution”). See generally David R. Jones, Position Taking and Position Avoidance in the U.S. Senate, 65 J. Pol. 851, 851 (2003) (discussing how the roll-call votes in the Senate are “significantly related to factors such as diversity of constituents’ opinions, pursuit of higher office, electoral marginality, retirement decisions, and visibility within the institution”).

[4] See, e.g., National Environmental Policy Act of 1969, 42 U.S.C. §§ 4321–4347 (2006); Sierra Club, Environmental Law Program, http://www.sierraclub.org/environmentallaw (last visited Apr. 18, 2010) (describing the legislative and judicial efforts of one organization working on environmental issues).

[5] See George Francis, Ecosystem Management, 33 Nat. Resources J. 315, 344 (1993) (“‘Ecosystem management’ poses a special challenge to boundaries. Boundaries associated with jurisdictions, administrative districts, and ownerships artificially transect ecosystems. While the international boundary is important for historical and other reasons, in the case of the Great Lakes it has also served as a perceptual and psychological boundary, impeding the development of a shared understanding of a major bioregion.”).

[6] See id.; see also Robert W. Adler, Addressing Barriers to Watershed Protection, 25 Envtl. L. 973, 991–92 (1995) (“[W]ater resource programs logically should be organized according to watershed boundaries. Politically, however, this has been difficult because each level of government guards its authority jealously. . . . [A]s described by the Natural Research Council Restoration Committee: ‘ . . . The politics and consensus building required for integrated resource management of the resource are often as complex as the ecosystem itself.’”); Charles  H.W. Foster, Bioregionalism: Cooperation to Live By, Alb. L. Envtl. Outlook, Winter 1996, at 13, 15 (“A heritage of intergovernmental mistrust seemed to dim any hope for true multi-jurisdictional action . . . .”); Michael V. McGinnis, On the Verge of Collapse: The Columbia River System, Wild Salmon and the Northwest Power Planning Council, 35 Nat. Resources J. 63, 65 (1995) (“In many respects, the plethora of entities, interests and individuals responsible for developing restoration strategies creates additional problems for a comprehensive ecosystem restoration effort.”); Paul S. Weiland & Roberto O. Vos, Reforming EPA’s Organizational Structure: Establishing an Adaptable Agency Through Eco-Regions, 42 Nat. Resources J. 91, 98 (2002) (“Human boundaries confound efforts to manage human-environment relations. To overcome the problems associated with such boundaries, it is necessary for people and institutions to cooperate. Cooperation to protect or enhance the natural world is only possible after parties have agreed that cooperation is necessary and specified the nature and extent of such cooperation. This agreement may be elusive due to value differences and scientific uncertainty.”).

[7] See Stuart Kauffman, At Home in the Universe: The Search for Laws of Self‑Organization and Complexity 8 (1995).

[8] See id. at 24 (stating, with respect to the author’s theory about the chemical nature of life, “If true, then life is not located in the property of any single molecule—in the details—but is a collective property of systems of interacting molecules. . . . Life, in this view, is not to be located in its parts, but in the collective emergent properties of the whole they create”).

[9] Id. at 115 (“But while the biosphere as a whole is supracritical, . . . the individual cells that make up the biosphere must be subcritical . . . . This, I will try to persuade you, is the source of the creative tension that brings about the ever-increasing diversity of the biosphere.”).

[10] See Jack Cohen & Ian Stewart, The Collapse of Chaos: Discovering Simplicity in a Complex World 174 (1994) (“Language exploits, and may even have arisen from, a trick that our brains seem to find natural in any case.”).

[11] See Fed. Commc’ns Comm’n, History of Communications—Internet: Common Standards, http://www.fcc.gov/omd/history/internet/common-standards.html (last visited Apr. 18, 2010) (discussing the “explosive growth” of the Internet upon the formal decommissioning of ARPANET in 1990 and charting the growth in the number of internet hosts from 100,000 in 1990 to 1,000,000 in 1992); Nat’l Acad. of Eng’g, History of the Internet, http://www.nae.edu/cms/
8743.aspx (last visited Apr. 18, 2010) (detailing the use of the internet to “search thousands of databases and libraries worldwide in several languages, browse through hundreds of millions of documents, journals, books, and computer programs,” as well as to follow news, shop online, and pay bills); Ian Peter, History of the World Wide Web, http://www.nethistory.info/
History%20of%20the%20Internet/web.html (last visited Apr. 18, 2010) (discussing the “massive growth” of the Internet “[e]very year from 1994 to 2000” and the development from being “mainly used for displaying information” to including some 750,000 commercial sites showing “the power of the web as a sales medium”).

[12] U.S. Const. art. I, § 1; id. art. II, § 1; id. art. III, § 1.

[13] Akhil Reed Amar, Five Views of Federalism: “Converse-1983” in Context, 47 Vand. L. Rev. 1229, 1237 (1994).

[14] See generally Cheyney C. Ryan, Yours, Mine, and Ours: Property Rights and Individual Liberty, 87 Ethics 126, 127–28 (1977).

[15] See generally Adam Smith, Wealth of Nations 400 (J.M. Dent & Sons Ltd. 1977) (1776) (explaining the relationship between promoting one’s own self-interest and the interest
of society).

[16] See id. (“By preferring the support of domestic to that of foreign industry, he intends only his own security; and by directing that industry in such a manner as its produce may be of the greatest value, he intends only his own gain and he is in this, as in many other cases, led by an invisible hand to promote an end which was no part of his intention.”).

[17] Foster, supra note 6, at 13.

[18] Id. at 14.

[19] See Kirkpatrick Sale, Dwellers in the Land: The Bioregional Vision 97 (1985) (“Even if we haven’t modern experience to ratify it entirely, the logic certainly suggests that because bioregional governance stands in a direct and vital relation to the natural environment and its resources, and because it can deal with a population of cultural and ecological homogeneity, it can do more effectively for the populace those things that governments are supposed to do.”).

[20] See generally id. at ix–x, 37 (describing the modern state of environmental crisis resulting from “an industrio-scientific worldview”).

[21] Id. at 42.

[22] See id.

[23] See id. at 55–59, 66 (discussing various hierarchical “scales” at which the environment can be partitioned into regions); id. at 97 (“[B]ecause bioregional governance stands in a direct and vital relation to the natural environment and its resources, and because it can deal with a population of cultural and ecological homogeneity, it can do more effectively for the populace those things that governments are supposed to do.”).

[24] Id. at 94–95.

[25] See id. at 50.

[26] See id. at 82 (“[T]he marketplace of our traditional capitalist economy, with its emphasis on competition, exploitation, and individual profit, needs to be phased out.”).

[27] See id. at 76 (explaining in regard to a bioregion’s efforts to achieve self-sufficient sustainability that “[t]hese kinds of adjustments need not be sudden, or hard, or privative, and they could be planned with great care and sophistication once the bioregional stocks and supplies are fully known.”); id. at 79 (“Self-sufficiency . . . is not the same thing as isolation, nor does it preclude all kinds of trade at all times. It does not require connections with the outside, but within strict limits—the connections must be nondependent, nonmonetary, and noninjurious—it allows them.”).

[28] See id. at 84–85 (“[T]here would be a sense that the wealth of nature is the wealth of
all—people should not be able to own the land, or its ores, or its trees, any more than they can own the sky and its clouds—and whatever is taken from Gaea’s realm is not to be hoarded and used for personal glory but distributed and used for regional benefit.”); id. at 85 (“Ownership . . . might logically be in community rather than regional or individual hands . . . .”).

[29] Id. at 84.

[30] Id. at 94–95.

[31] Id. at 96 (explaining that among communities in a bioregion, “possibly some kind of political deliberative and decision-making body would eventually seem to be necessary”).

[32] See id. at 97–102. “Hierarchy and political domination would have no place; systems of ruler-and-ruled, even of elected-president-and-electing-people, are nonecological. . . . No leader, no ruling committee, no oligarchy, only citizens performing necessary roles . . . .” Id. at 101.

[33] See id. at 104–10 (“Bioregional diversity . . . does not mean that every community in a bioregion . . . would construct itself along the same lines, evolve the same political forms. Most particularly it does not mean that every bioregion would be likely to heed the values of democracy, equality, liberty, freedom, justice, and the like, the sort that the liberal American tradition proclaims. . . . Different cultures could be expected to have quite different views about what political forms could best accomplish their bioregional goals, and . . . those forms could be at quite some variance from the Western Enlightenment-inspired ideal.”).

[34] See id. at 113–16 (indicating that for cities of more than an “upper limit” of 250,000 people, “there seems to be no sensible choice but to break down the current multimillion-people cities both by dividing them into smaller cities . . . and by resettling them into different-sized communities in the surrounding region,” and that this “population relocation” would affect one-fifth of the U.S. population among 48 cities).

[35] Id. at 119.

[36] See id. at 120 (“Greatest opprobrium, and presumably punishment, would attend those acts that are most violent and disruptive, that cause severe or permanent damage to the ecosystem, no matter what supposed economic or material benefits they may offer—such as murder or clearcutting or species extinction or the introduction of the gypsy moth.”).

[37] See id. at 127.

[38] Id. at 41.

[39] Id. at 21.

[40] Id. at 22.

[41] Id. at 192.

[42] See id. at 60–61 (discussing “American Indian habitation in bioregional patterns” as a demonstration of the firm grounding of the bioregional vision since “it is a concept inherent in the cultures of age-old peoples who knew the ways of nature best”); id. at 81–85 (stating that “what we take for granted in our market system . . . is really a rather recent development,” and that “the simple economies of most societies before the modern age . . . seem to have much that a bioregional society could learn from,” perhaps as a result of the nature of such social systems whereby “no activity is undertaken that is not a custom or a ritual or a spontaneous part of social congress, and where seldom does anyone have to be forced or coaxed to perform it”); id. at 99–101 (describing “preliterate cultures” as lacking such unsavory elements as “those ‘organized stratifications’ we have become accustomed to in the industrial world,” meaning hierarchical relationships).

[43] See, e.g., id. at 28 (“[T]he economy is based precisely on the concepts of exploitation, productivity, and growth.”); id. at 29 (characterizing industrialized agriculture as “reckless”); id. at 48 (describing the notion in industrial society “of controlling and remaking the world in the name of a global monoculture” and characterizing industrial economy as “imperiling” humanity).

[44] See id. at 12–37 (“I take what little comfort I can . . . from the belief that we have at our grasp the instrument—the philosophy, if you will—by which to begin to rescue . . . our beleaguered species, creating for ourselves . . . an ecological worldview with which to replace the scientific worldview . . . that has so imperiled us. That instrument, that philosophy, is the bioregional vision.”); id. at 192 (advocating the implementation of the bioregional vision “[b]ecause what other choice, really, do we have?”).

[45] See, e.g., id. at 3–11 (“In all the long stretch of human history . . . the people of this planet saw themselves as inhabitants within a world alive.”); id. at 183–92 (“And so, after all, the Greeks seem to have been right. There is no real doubt about it: the earth, the biosphere, is alive, ‘a living creature, one and visible, containing within itself all living creatures.’”).

[46] Id. at 41–42.

[47] See id. at 48–49 (noting that the bioregional vision “is so at odds with the conventional way of looking at the world nowadays that it must strike most people at first as either too limiting and provincial, or quaintly nostalgic, or wide-eyed and utopian, or simply irrelevant—or all of those,” and while continuing to describe the improbabilities involved, concluding that he is “certain that in the bioregional paradigm we have a goal, a philosophy, and a process” that is “not only necessary for the continuation of our species, but is also desirable and possible”); id. at 179 (“The bioregional project, then, certainly has its full measure of dreams of things that never were; yet when properly understood in its totality, it is not in any sense fantastical, chimerical, quixotic, or illusory. I do not suggest that it is inevitable or fated, or that once begun it could not be frustrated and defeated; just that it is without doubt possible.”). Ironically, Sale writes, “[T]he bioregional project has the virtue of realism. It does not demand any elaborate wrenching of the physical or human conditions of the world we know, any fantastic alterations of nature-as-it-is or people-as-they-are.” Id. at 177.

[48] See Robert B. Keiter, NEPA and the Emerging Concept of Ecosystem Management on the Public Lands, 25 Land & Water L. Rev. 43, 43 (1990) (“Modern science has revealed that dynamic, complex ecological processes are a vital and important part of the natural environment, and that neither biological processes nor environmental phenomena respect conventional boundary lines. Indeed, virtually all of the natural resources found on the public domain are part of ecosystems that extend beyond established legal boundaries.” (footnote omitted)); id. at 45 (“The evolving concept of ecosystem-based management is still in its formative stages and remains rather ill-defined. As a general principle, ecosystem management views public lands and resources from a regional or resource system perspective; it regards natural phenomena, such as watersheds, airsheds and wildlife habitats, as the appropriate focus for management decisionmaking. . . . In short, management priorities—set in accordance with ecological principles—should transcend jurisdictional boundaries and reflect an overarching commitment to an integrated public domain.”).

[49] See id. at 47–50.

[50] Richard Haeuber, Setting the Environmental Policy Agenda: The Case of Ecosystem Management, 36 Nat. Resources J. 1, 4–5, 26–27 (1996) (noting that “a generally accepted set of [ecosystem management] principles, or components, has emerged” out of past regional-scale management efforts that have not been consciously “ecosystem management,” with these principles being sustainability, systems perspective, broad spatial and temporal scales, humans as ecosystem components, socially defined goals and objectives, collaborative decision building, organizational change, adaptive management, monitoring, and data collection).

[51] See Scott W. Hardt, Federal Land Management in the Twenty-First Century: From Wise Use to Wise Stewardship, 18 Harv. Envtl. L. Rev. 345, 392 (1994) (“As a result of our dependence on resources harvested from our environment, human society is a significant force in shaping the world’s environment and must be considered part of the ecological community being managed. . . . Consequently, human use of natural resources and the creation of human-induced successional stages should be considered an appropriate element of ecosystem management . . . .” (footnotes omitted)).

[52] See id. at 393 (“To manage ecosystem viability effectively, federal land managers . . . will need to adjust the geographic areas over which they make multiple use decisions since administrative boundaries seldom reflect meaningful ecological boundaries.”).

[53] See Haeuber, supra note 50, at 2 (“The generation of environmental issues now upon us, however, are defined by greater political, economic, social, and even cultural, complexity. They include difficult scientific questions, such as appropriate scales for resource management; thorny administrative matters, such as inter- and intra-governmental relations; political controversies surrounding land use planning and property rights; the problems involved in restructuring of natural resource-based economies; and the cultural underpinnings of ranching, logging, fishing and other traditional resource dependent communities.”).

[54] See Jack Ward Thomas, Foreword to Ecosystem Management: Applications for Sustainable Forest and Wildlife Resources, at ix, x (Mark S. Boyce & Alan Haney eds., 1997) (“Emergence of ecosystem management is a consequence of conflicts over how we manage our public lands. The American public will no longer tolerate commodity-production priority for managing our national forests and other public lands; neither can we afford to exclude commodity users from public lands and support a human population of 5.6 billion people.”).

[55] See Steven L. Yaffee et al., Ecosystem Management in the United States: An Assessment of Current Experience 9–11 (1996) (listing “anthropogenic ecosystem stresses,” including hydrologic alteration; land conversion to urban use; agricultural practices; disruption of fire regime; nonpoint source pollution; grazing and range management; timber and forest management; land conversion to agricultural uses; recreation; point source pollution; mining; and overfishing, overhunting, or overcollecting).

[56] See Hardt, supra note 51, at 350 (“An affirmative policy of federal land management began evolving in the late nineteenth century only after a century of uncontrolled exploitation of the public domain created broad public concern that the rate of exploitation, if left unchecked, would rapidly deplete the nation’s resource base.”).

[57] Act of Mar. 3, 1891, ch. 561, 26 Stat. 1095, repealed by Federal Land Policy and Management Act of 1976, Pub. L. No. 94-579, 90 Stat. 2743.

[58] Forest Service Organic Administration Act of 1897, ch. 2, 30 Stat. 11, 34–36 (codified as amended at 16 U.S.C. §§ 473–482, 551 (2006)).

[59] See Hardt, supra note 51, at 353–55.

[60] See id. at 355–58 (quoting Gifford Pinchot, Breaking New Ground 261 (commemorative ed., Island Press 1998) (1947)).

[61] 16 U.S.C. §§ 528–531 (2006).

[62] Hardt, supra note 51, at 351 (noting that the limited multiple use policies of the late 1800s have changed in two major ways: 1) “multiple use” has expanded to cover more uses, such as recreation and aesthetic uses, and 2) requirements have been introduced for comprehensive management and noncommodity use management).

[63] Jan G. Laitos & Thomas A. Carr, The Transformation on Public Lands, 26 Ecology L.Q. 140, 149–50 (1999) (“During the heyday of the multiple-use management era (1930–1970), commodity uses of federal lands were dominant. In the 1970s, however, new environmental laws (triggered by a burgeoning environmental movement) led to growing restrictions on the traditional extractive uses of public lands.” (footnote omitted)).

[64] Haeuber, supra note 50, at 4 (“Regional scale resource management approaches have been evident in the United states for quite some time. For example, the Great Lakes Water Quality Agreement, signed in 1972 and revised in 1978, established the principles and process for a functioning regional [ecosystem management] approach. Similarly, land and resource managers in the Greater Yellowstone Ecosystem region have experimented with elements of an [ecosystem management] approach for nearly 30 years, beginning with establishment of the Greater Yellowstone Coordinating Committee in the early 1960s.” (footnote omitted)).

[65] J.B. Ruhl, Ecosystem Management, the ESA, and the Seven Degrees of Relevance, 14 Nat. Resources & Env’t 156, 157 (2000) (“Threads of scientific research and commentary consistent with the ecosystem management theme extend back well into the 1980s, but until the early 1990s writers did not routinely use the phrase ‘ecosystem management’ as a term of art with which readers were generally expected to be familiar.”).

[66] Keiter, supra note 48, at 44 (“[F]ederal land management officials are beginning to take initial, cautious steps to design meaningful transboundary management programs that protect shared ecosystems . . . .”).

[67] National Environmental Policy Act of 1969, 42 U.S.C. §§ 4321–4307f (2006).

[68] Keiter, supra note 48, at 44–45 (concluding that NEPA does not “impose[] a legal obligation on federal land managers to protect shared ecosystem resources,” but also concluding that “as a procedural matter,” NEPA “compels land managers to view their actions from an ecological perspective, even if it does not require them to adopt the most ecologically sensitive course of action”).

[69] Id. at 48 (“[W]hile NEPA insures ‘process’ coordination among neighboring federal land management agencies, it does not insure meaningful substantive coordination sensitive to transboundary ecological realities. Nonetheless, the courts have proven particularly sensitive to interagency disagreements or disputes when reviewing NEPA claims.”); see also Robertson v. Methow Valley Citizens Council, 490 U.S. 332, 353 (1989).

[70] See Keiter, supra note 48, at 51 (“In sum, NEPA contemplates that serial development proposals will be analyzed aggregately at the outset and not after the agency has committed itself to a course of action.”).

[71] See id. at 51–52.

[72] See Hardt, supra note 51, at 393 (“Forest Service regulations currently direct that regional and forest plans be based upon the ‘[r]ecognition that the National Forests are ecosystems and their management for goods and services requires an awareness and consideration of the interrelationships among plants, animals, soil, water, air, and other environmental factors within such ecosystems.’” (alteration in original) (quoting 36 C.F.R. § 219.1(b)(3) (1992))).

[73] Haeuber, supra note 50, at 2 (“Ecosystem management . . . is a prominent recent policy alternative proposed to address this new generation of issues. At least 18 federal agencies currently are exploring the concept of ecosystem management and its implications for their activities. Each of the major land and natural resource management agencies has drafted policy guidance regarding ecosystem management approaches.” (footnote omitted)).

[74] Yaffee et al., supra note 55, at xvi (stating, in addition to cataloging 105 ecosystem management efforts in the United States and analyzing the available results, that “[t]he intensity of the debate over ecosystem management at times has hidden a simple reality: People on the ground . . . are already actively engaging in ecosystem management experiments. . . . Few are managing at the ecosystem scale, but most are taking an ecosystem approach to
resource management”).

[75] See Haeuber, supra note 50, at 23 (“As currently developing, [ecosystem management] is a spontaneous manifestation of local level concerns, needs and desires for the future. It is less rational planning than an ‘organic’ process characterized by mutation and natural selection of solutions that develop and evolve at different rates and in diverse ways in many areas around the country.”).

[76] Yaffee et al., supra note 55, at 40 (“Since much of the rhetoric associated with ecosystem management in recent years has come from federal officials, it was surprising to discover how much activity is under way at the state level. State agencies are being innovative. . . . Several states are attempting to use ecosystem management as a philosophy underlying their overall approach to resource management.”).

[77] See Hardt, supra note 51, at 392–93 (“To render federal land use decisions within an ecosystem management framework, multiple use decisions should proceed simultaneously at two levels. First, based upon a complete inventory of current environmental conditions and natural resources, federal land managers should apply known ecological principles to establish the maximum level of disturbance that can be allowed within the management area without destroying the viability of the ecosystem. Second, an interdisciplinary team of land managers should, through federal land planning processes and based upon public input, determine the appropriate mix of uses that will be allowed within the ecosystem viability ceiling. While the ecosystem viability ceiling should be a nonpolitical, scientific determination, the second decisionmaking stage, which might be called the ‘lifestyle prong,’ clearly requires political decisions based upon public preferences . . . . It is critical, however, that the lifestyle decision not override the ecosystem viability determination and that short-term lifestyle decisions not cause long-term ecological damage.”).

[78] Id. at 391–96 (concluding that the principle of “[m]aintaining [v]iable [e]cosystems” should govern when evaluating public lands policies between multiple potential uses). “Only by maintaining the health of this country’s ecosystems can federal land managers ensure that they are providing the greatest good for the greatest number over the long run.” Id. at 391.

[79] Keiter, supra note 48, at 50 (“Meaningful ecosystem-based management must be concerned with the cumulative regional impacts accompanying federal land and resource management decisions. Most resource management decisions inevitably cause environmental impacts that reach beyond established boundaries, affecting adjacent and sometimes distant lands, usually through common resource systems.”).

[80] Hardt, supra note 51, at 394–95 (“Defining the appropriate ecological area over which management decisions should be made is complex. . . . Consequently, in defining a management area, the objective should be to establish ‘administrative ecosystems’ so that the primary energy and nutrient links within a given biological community are managed comprehensively. Several commentators have suggested that watersheds should define ecologically based management areas.” (footnote omitted)).

[81] See Haeuber, supra note 50, at 5–6; Yaffee et al., supra note 55, at xv (“[T]he dialogue often has bogged down in arguments over ‘just what is ecosystem management’ and ‘what are its goals.’”).

[82] Yaffee et al., supra note 55, at 44 (“[E]cosystem management is not management toward any end. Rather, it seeks to protect and restore the ecological integrity of landscapes while building sustainable economies and effective organizational and decision-making structures.”).

[83] Id. at xii–xiii (noting funding problems as significant hurdles in the way of cooperative ecosystem management efforts).

[84] Lee P. Breckenridge, Nonprofit Environmental Organizations and the Restructuring of Institutions for Ecosystem Management, 25 Ecology L.Q. 692, 693 (1999) (noting that while “nonprofit organizations may often provide important transformative frameworks” toward ecosystem management ends, “[n]ot all nonprofit organizations will work effectively to restore and maintain ecologically viable natural systems, . . . and the increasing reliance on nonprofit organizations raises important issues concerning institutional design and accountability”).

[85] See Allan K. Fitzsimmons, Defending Illusions: Federal Protection of Ecosystems 34–39 (1999) (“Using ecosystems as a geographic basis for government authority, therefore, represents a radical departure from our national experience with establishing the spatial boundaries guiding the application of government power.”).

[86] See id. at 46–48 (stating that among the “geographic fraternity[,] . . . most reject the idea that regions are actual objects on the landscape”); id. at 48–56 (noting that climate, vegetation, and soil are all problematic bases for mapping ecosystems).

[87] See id. at 240–43 (“Only through national land use planning and management can the federal government ensure that the public obtain newly fabricated rights to ecosystem integrity . . . . The notion that a Washington bureaucracy can rationally plan or direct land use decision making to achieve . . . ‘optimal land use decisions’ rests on a false assumption and posits in government a wisdom and an ability that neither our government nor any others have ever demonstrated. . . . What evidence is available that a Washington bureaucracy is capable of either making or guiding intelligent land use decisions for the nation? The total amount of knowledge and information that people use in making such decisions is beyond calculation. . . . People make land use decisions that reflect constantly changing economic, social, and environmental circumstances. Their judgments factor in new developments in science, technology, and other ingredients that contribute to the functioning of society. Decisions reflect individual choices and ideas about how to better the lives of those making them. How is it possible for a central authority to accumulate all the knowledge and data needed to make sound land use decisions, much less comprehend what it collects? How can a bureaucracy sort out the needs of tens of millions of individuals and tens of thousands of communities and make benevolent land use decisions on that basis? Because of the enormity and complexity of the task, they could not do so even if they wanted to. Ultimately, the planners’ decisions would be driven by the political signals they receive from the interests that keep them in power and by their own desires to expand their programs and budgets rather than by the views of the public from which they would be isolated and to which they would be accountable.” (footnote omitted)).

[88] Haeuber, supra note 50, at 5–7.

[89] Id. at 7.

[90] Yaffee et al., supra note 55, at xii–xiii (“Natural resource managers, project coordinators, and decision makers on the ground are struggling against imposing odds to make land management work. They have little direction and often face incredible political or administrative hurdles.”).

[91] Id. at 41 (“By requiring more collaborative work from diverse stakeholders with often conflicting interests, ecosystem-based approaches to land management run head-on into the problems commonly associated with human relations and group decision making. . . . Many current policies make it difficult to practice effective ecosystem management. Participation in numerous land management planning processes initiated by different federal and state agencies consumes the limited time and resources available to nongovernmental stakeholders. Multiple, independent planning processes often make it difficult to take a larger-scale perspective.”).

[92] Id. at 33 (“Problems associated with agencies were reported by 31 percent of the respondents, with the largest portion describing institutional obstacles including a lack of interagency coordination and cooperation and administrative red tape. In many cases, these issues were unavoidable given the need to involve all affected stakeholders and the resulting complexities of multiple decision making layers . . . . [J]urisdictional conflicts between agencies were the source of several problems, despite the good intentions of individuals within those agencies or of project coordinators.”).

[93] Laitos & Carr, supra note 63, at 218–20 (concluding that “the promise of ecosystem management as a long-term public land management strategy is problematic” for many reasons: 1) the inherent difficulty in defining “ecosystem management,” 2) the tension between “biocentric” and “anthropocentric” policy goals, 3) establishing ecosystem boundaries,
4) insufficient data, and 5) coordination problems “among all interested parties—federal, state, and private”). On the other hand, one commentator has concluded that all levels of government—local, state, and federal—are mismatched with respect to the scale of ecosystem management projects, either being underinclusive or overinclusive with respect to any particular ecosystem, and that ecosystem-based management efforts are therefore the proper solution. Bradley C. Karkkainen, Collaborative Ecosystem Governance: Scale, Complexity, and Dynamism, 21 Va. Envtl. L.J. 189, 212–17 (2002) (arguing that, with respect to “the demands of ecosystem management,” governments at all levels of hierarchy are mismatched: Local governments are underinclusive, requiring coordination “at a larger geographic scale,” and lack resources and expertise; state governments are sometimes underinclusive and sometimes overinclusive, depending upon the state; and the federal government “is almost certainly too big and too remote from the highly variable, locally situated, complex interdependencies that comprise ecosystems to assume sole or even principle responsibility for managing them”). Under this view, presumably, ecosystem management should therefore go forward despite the hardships, as the most feasible alternative.

[94] Yaffee et al., supra note 55, at 23 (“While one-third of the projects reported specific ecological results, the five outcomes cited most frequently can be viewed as procedural in nature.”). The five most frequently cited outcomes were 1) improved communication and cooperation (74%), 2) development of management plan (62%), 3) development of decision-making structures (56%), 4) change in approach to land management (50%), and 5) ongoing restoration activities (46%). Id. at 23 fig.13.

[95] George Cameron Coggins, Watershed as a Public Natural Resource on the Federal Lands, 11 Va. Envtl. L.J. 1, 13–14 (1991) (noting that protection of watershed resources necessarily involves three considerations: 1) maintenance of instream flow, 2) protection of the riparian zone near streams, and 3) protection of the uplands beyond the riparian zone, which affects the largest area of land).

[96] Comm. on Watershed Mgmt., Nat’l Research Council, New Strategies for America’s Watersheds, at ix (1999) (“[W]atersheds are logical divisions or regions of the natural landscape, and for some purposes they are ultimately the best framework to use for management.”); Coggins, supra note 95, at 45 (“[I]t is logically inescapable that watershed is the key, integrative public resource.”); id. at 44 (“All resource uses are dependent on the system in which water and watershed values are integral parts.”).

[97] Coggins, supra note 95, at 13 (“Literally, watershed is the area drained by a river or river system, including riparian zones and uplands.” (footnote omitted)).

[98] Id. at 44 (“Although the term watershed technically denotes a geographic area, in congressional contemplation it more resembles an entire system with multiple productive capabilities. The system has soil, water, vegetative and other biotic components, all of which interact to stabilize, maintain and enhance each other and the system itself. Without water, the other components will suffer and die.”).

[99] J.A. Stanford & J.V. Ward, Management of Aquatic Resources in Large Catchments: Recognizing Interactions Between Ecosystem Connectivity and Environmental Disturbance, in Watershed Management: Balancing Sustainability and Environmental Change 91, 93 (Robert J. Naiman ed., 2002) [hereinafter Watershed Management] (“In the United States, the term watershed is often misused in the context of river basin research and management. By proper definition, the watershed is the ridgeline or elevation contour that delimits drainage basins or catchments. The catchment is bounded by the watershed, and since water flows downstream from the watershed through the catchment, thereby integrating influences of natural and human disturbances within the catchment, we use the watershed as the natural ecosystem boundary.”).

[100] William Goldfarb, Watershed Management: Slogan or Solution?, 21 B.C. Envtl. Aff. L. Rev. 483, 483 (1994) (“The trend toward watershed management is a response to the following fundamental legal-institutional problems of water resources management: A) Transboundary water management problems; B) Implications of federalism and separation of powers; and C) Variability of water law among political units.”).

[101] Bob Doppelt et al., Entering the Watershed: A New Approach to Save America’s River Ecosystems 18–23 (1993) (listing dangers to watershed ecosystems such as logging, transportation infrastructure, grazing, mining, urbanization, point and nonpoint pollution, overharvest, and introduction of exotic species); Coggins, supra note 95, at 19–21 (citing timber harvesting, associated road building, extensive grazing, mining, mineral leasing, water diversions, and intensive motorized recreation as threats to watershed quality).

[102] Doppelt et al., supra note 101, at xxv–xxvi (“Watersheds are ecosystems composed of a mosaic of different land or terrestrial ‘patches’ that are connected by (drained by) a network of streams. In turn, the flowing water environment is composed of a mosaic of habitats in which materials and energy are transferred and, therefore, connected through biologically diverse food webs. Human activities can result in the fragmentation and disconnection of the habitat patches if management is not planned and implemented from an ecosystem and watershed perspective.”).

[103] See Jon Cannon, Choices and Institutions in Watershed Management, 25 Wm. & Mary Envtl. L. & Pol’y Rev. 379, 391 (2000).

[104] Id. (“In the late nineteenth century, John Wesley Powell advocated that settlement in the arid west be organized within ‘“hydrographic basins,” or watershed units . . . rather than by the prevailing township and county system.’ Reflecting the dominant values of his time, Powell’s proposal was designed to facilitate publicly controlled development of water resources for irrigation . . . [,] not to protect the ecological health of aquatic systems.” (first alteration in original) (quoting Donald Worster, Rivers of Empire 138 (1941))).

[105] Timber Culture Act of 1873, ch. 277, 17 Stat. 605 (1873) (repealed 1891); see Coggins, supra note 95, at 4.

[106] See Coggins, supra note 95, at 4.

[107] 16 U.S.C. §§ 473–478, 551 (2006).

[108] Id. § 475; see Coggins, supra note 95, at 4–5. By “water flows,” Congress meant “watersheds.” Id.

[109] 438 U.S. 696 (1978).

[110] See id. at 712–13; Coggins, supra note 95, at 5.

[111] Goldfarb, supra note 100, at 486 (“Watershed management’s closest antecedent is the concept of ‘unified river basin management,’ which has been influential in the water resources management community since approximately 1900.”).

[112] Id. at 486–87.

[113] Id. (noting that, of the three periods in “the evolution of unified river basin management,” the first period, 1900–1933, was characterized by “[m]ultipurpose, basinwide water resources development” that was oriented toward “flood control, municipal water supply, irrigation, hydroelectric power generation, recreation, and water quality improvement”).

[114] Adler, supra note 6, at 1005 (“[M]assive federal spending on large, structural water projects to optimize and ‘manage’ the use and value of water for human benefits [is] reflected in laws such as the Reclamation Act of 1902, the Federal Power Act of 1920, and the Flood Control Act of 1936.” (footnotes omitted)).

[115] Id. at 1005–06 (“The idea of integrated river basin water policy was developed during the Progressive Era in a series of reports issued by various commissions under Theodore Roosevelt’s Administration: the 1908 Inland Waterways Commission, the 1909 National Conservation Commission, the 1912 National Waterways Commission, and the authorized but never formed 1917 Newlands Commission. All proposed many of the same elements present in today’s watershed proposals, such as coordination of the goals and functions of federal water agencies, comprehensive water quality and quantity planning, . . . and comprehensive evaluation of all issues from a basinwide perspective.” (footnote omitted)). These watershed proposals—never adopted—were directed by multiple-use concerns. See id. at 1006.

[116] Goldfarb, supra note 100, at 486–87 (noting that, of the three periods in “the evolution of unified river basin management,” the second period, 1933–1965, was characterized by “regional socioeconomic development through publicly-owned hydropower”).

[117] Adler, supra note 6, at 1007–08 (“A broader view of comprehensive river basin planning returned during the New Deal, in proposals by the National Planning Board, the Water Resources Committee of the National Resources Commission . . . , and the National Resources Planning Board . . . . As with Progressive Era proposals, the New Deal agencies suggested a ‘comprehensive approach integrating all resources into a unified, balanced program’ . . . . These proposals resembled today’s watershed proposals somewhat more closely than Progressive Era versions with their increased recognition of the link between land development (including deforestation) and water resources degradation caused by increased erosion and runoff.” (footnotes omitted) (quoting Norman Wengert, A Critical Review of the River Basin as a Focus for Resource Planning, Development, and Management, in Unified River Basin Management 9, 12 (Ronald M. North et al. eds., 1981))). However, these proposals—again, aside from the Tennessee Valley Authority, never adopted—were “fundamentally rooted in human use of water and economic development.” Id. at 1008.

[118] Id. at 1008–09 (“[T]he continued promotion of river basin planning by the Truman and Eisenhower Administrations . . . . resulted in the Hoover Commission proposal in 1949 to combine most federal water programs into a single cabinet-level department; Truman’s 1950 Water Resources Policy Commission report, which proposed joint federal-state river basin commissions to address both water quality and quantity planning and management; and Eisenhower’s Presidential Advisory Commission on Water Resources Policy, which . . . proposed independent project review through plans prepared by basin-level committees. . . . These proposals mirrored their predecessors’ focus on river basins and basin drainage areas as logical planning entities, but continued as well the underlying purpose of basin planning—to promote the development of water projects.” (footnotes omitted)). None of these proposals were adopted. Id. at 1009.

[119] 42 U.S.C. §§ 1962–1962d (2000); see also Goldfarb, supra note 100, at 486–87 (noting that, of the three periods in “the evolution of unified river basin management,” the third period,
1965–1990, was characterized by the rise and fall of the federal Water Resources Council as a mechanism for supervising and implementing cross-jurisdictional river basin development plans).

[120] Adler, supra note 6, at 1009 (describing the WRPA as coming from “Congress and both a republican and a democratic President”). This Act, while mentioning conservation of water and related land resources, “focused primarily on optimum water resource use and development, with only passing mention of conservation or protection.” Id. at 1011. The WRPA (as well as the Water Resources Council and River Basin Commissions created by its titles I and II, respectively) failed, arguably due to its express declining of “any impact on existing federal, state, or interstate laws, compacts, or other authorities, regardless of consistency with the goals of [the WRPA] or the outputs of the planning process.” Id. at 1011–12.

[121] Id. at 1013 (noting that, before its demise, the Water Resources Council under the WRPA issued a report whose findings included that “the development, management, and protection of water resources should be controlled by the level of government closest to the problem and most capable of representing the interests involved”).

[122] Coggins, supra note 95, at 17 (“Watershed is a coequal multiple surface use, to be managed for sustained yield, under the 1960 Multiple-Use, Sustained-Yield Act and [the Federal Land Policy and Management Act].” (footnote omitted)); see also Multiple-Use Sustained-Yield Act of 1960, 16 U.S.C. § 528 (2006); Federal Land Policy and Management Act of 1976,
43 U.S.C. § 1732 (2006).

[123] Coggins, supra note 95, at 18 (“Theoretically, all multiple use management decisions should be premised on coordinated consideration of the effects of the proposed action on all resources. Watershed should be the key element in such consideration, because all other uses ultimately depend on the quality, quantity, and stability of the soil and water—the essence of the watershed resource.” (footnote omitted)).

[124] Id. at 45–46. (“Watershed management should entail consideration of all resources and values of the federal lands and the relationships between them. . . . Many if not most federal land managers long have realized that the proper focus of multiple use, sustained yield management should not be on mineral claims, campgrounds, timber contracts, or other isolated management functions, but rather on the overall health of the land that generates such human benefits. Watershed should be viewed as the embodiment of that ‘health’ concept.”).

[125] Adler, supra note 6, at 991 (“It is difficult to imagine a political and institutional system as complicated and fragmented as that used for protecting and managing water resources in the United States—a system that has been described as ‘similar to a marbled cake, with several levels of government intermingled in an irregular pattern.’ . . . Thus, several institutional imperatives support the need for watershed-based approaches[,] . . . [including] political fragmentation—the overlapping and conflicting division of responsibilities among multiple levels of government and agencies.” (footnote omitted) (quoting William Whipple, Jr., Future Direction for Water Resources, in Water Management in the 21st Century 9, 10 (A. Ivan Johnson & Warren Viessman, Jr. eds., 1989))).

[126] Robert J. Naiman, New Perspectives for Watershed Management: Balancing Long-Term Sustainability with Cumulative Environmental Change, in Watershed Management, supra note 99, at 3, 6 (“Watershed issues require coordination on a scale seldom achieved in human societies. . . . This level of concentration on a single goal demands that socioeconomic and political barriers be crossed efficiently and effectively.”).

[127] Stanford & Ward, supra note 99, at 114–15 (“Local and regional fragmentation of management authority is guaranteed to result in interference management . . . . If human disturbances are to be managed for the purpose of maintaining natural ecological connectivity at the catchment scale, management agencies must cooperate to minimize interferences.”).

[128] Doppelt et al., supra note 101, at xxx–xxxii (calling for a range of federal activity—including consolidation of federal policy-making authority, “[e]cosystem and watershed-level planning by all federal agencies,” and “ecosystem-based watershed protection program[s] for all federal land-management agencies”—as necessary “[t]o implement the new protection and restoration approach”).

[129] Id. at 34 (calling for “the active participation of local communities in implementing” comprehensive watershed protection and restoration).

[130] See id. at 62–63 (“[S]uccessful watershed restoration programs require the active involvement and support of local communities and citizens. . . . Most of the daily decisions that affect riverine systems are made at the local level. It is the local communities that are most directly harmed by degraded riverine conditions . . . , and it is the local communities that will be asked to give up the most perceived economic gain to protect and restore a river. . . . Hence, local communities must be actively engaged in bottom-up efforts to restore riverine systems and biodiversity. . . . [F]or citizens to take charge of their own destiny and to be willing to forgo perceived economic gains requires something more than just desire. It requires empowerment, effective new incentives, the removal of disincentives, [and] effective implementation structures.”).

[131] See Adler, supra note 6, at 1091 (“[T]he largest watershed units, probably at the basinwide scale, should address issues of regional planning, assessment, and coordination, to ensure that the program properly acknowledges and addresses regional impacts and connections, and to establish the broadest level of regional goals and objectives.”
(footnote omitted)).

[132] Id. at 1104 (“[T]here remains the question of federal consistency with state and regional watershed programs and requirements. . . . Yet many past consistency provisions have been weak or equivocal, giving discretion to federal agencies to avoid state or regional requirements. . . . [T]here is no reason why, once states and regions adopt watershed protection requirements designed to meet national as well as regional aquatic ecosystem restoration and protection goals, federal activities should not be subject to those requirements in full.” (footnote omitted)).

[133] Comm. on Watershed Mgmt., supra note 96, at 2 (“The environmental, social, and economic diversity of the United States dictates that one standard solution is unlikely to be useful in all parts of the country. . . . Any well-designed national policy for watershed management must maintain great flexibility to accommodate these natural and human variations and allow significant local control and input to decisions.”).

[134] Id. at 3–4 (“Organizations for watershed management are most likely to be effective if their structure matches the scale of the problem. . . . A major barrier to effective watershed management for large basins in the past has been limitations on the transfer of powers. The various levels of government in the United States developed historically with specific authorities and powers, and most governmental entities are unlikely to give up those powers to some larger all-encompassing organization. . . . Partnerships among levels of government and various agencies are required for effective watershed management. The era of a large, dominant federal government must give way to an era of flexible federalism where the federal government maintains a role but allows state and local governments to assume substantial rights and responsibilities for watershed management.”).

[135] Id. at 204 (“The historical development of governmental organizations in the United States dictates a certain distribution of powers among levels and among agencies within the same level. Watershed management through newly defined organizations will not succeed unless there is a transfer of powers from those established agencies, often an unlikely scenario. Therefore, watershed management in the United States is often best accomplished through partnerships of existing agencies that work together in ad hoc arrangements for
particular watersheds.”).

[136] Coggins, supra note 95, at 10 (“The most basic definitional problem raised by the [watershed-related] statutes is whether the aim of watershed resource management should be production or protection, or both.”).

[137] Goldfarb, supra note 100, at 484–85 (“Regional solutions to water resources management problems are also frustrated by the difficulty of defining a water resources problem-shed in a way that will both promote holistic problem-solving and elicit political support. . . . The arduous political task of regional institution-building is further exacerbated by [the Environmental Protection Agency’s] strategy of adopting an ad hoc, esoteric definition of ‘watershed.’”).

[138] Adler, supra note 6, at 1093–94 (“[N]o agreement yet exists on a single framework for environmental boundaries. Hydrological purists continue to advocate programs based on watershed boundaries, while aquatic ecologists now suggest that watershed ecosystems reflect more accurate ecological boundaries. But ecological boundaries often cannot be identified with precision . . . . There is probably no single answer to this paradox, as is illustrated by the fact that no single ecosystem delineation is more ‘correct’ than others.” (footnote omitted)).

[139] Id. at 1095 (“When aquatic ecosystems cross so many state and international boundaries, a strong federal presence is essential to ensure that progress and goals are reasonably equal around the country. Yet uniform federal regulation of land use will continue attracting significant opposition, and is not appropriate in all cases.”); id. at 1102 (“Historical precedent, along with increasing opposition to anything federal in scope or origin, tends to suggest that watershed programs should be voluntary and flexible. Previous efforts to establish a nation-wide system of watershed management failed, in part due to strong resistance to mandatory federal programs in the areas of land and water use and also to perceived federal control over these domains.”).

[140] Comm. on Watershed Mgmt., supra note 96, at 10–11 (noting that a recurrent theme appearing “throughout the committee’s deliberations” was that “fragmentation of responsibility and lack of clarity about how to resolve disputes caused by conflicting missions among federal agencies inhibits the success of the watershed approach” ).

[141] Goldfarb, supra note 100, at 484 (“American political boundaries do not, for the most part, correspond to water resources problem-sheds. Most water resources problems are transboundary in nature, i.e., intermunicipal, interstate, or international. In the American political system, regional political institutions are difficult to create and, when established, tend to lack political viability. Thus, there is rarely a single competent institution with legal jurisdiction over a water resources problem of regional dimension.” (footnotes omitted)).

[142] Id. (“In addition, water resources problems such as interbasin transfers of water transcend even recognized regional boundaries. This institutional situation creates the traditional incentive for one jurisdiction to solve its own development problems without regard to spillover water resources effects on neighboring jurisdictions . . . . In this process of cost externalization, tragedies of the commons are often overlooked.”).

[143] Id. at 485 (“Myriad governmental institutions at the international, federal, interstate, state, substate regional, and local levels of government play significant roles in managing water resources. Institutional rivalries, conflicting or overlapping jurisdictions, diverse constituencies, and other factors cause frequent disagreements among these institutions with regard to water resources issues.”).

[144] Id. at 498 (“Problem-based regions may be conterminous with the problems to be solved, but such regions themselves raise institutional difficulties: 1) the larger the region, the more institutions and interest groups must be included in problem-solving, thus intensifying institutional conflicts and political rivalries; and 2) the larger the region, the greater is the possibility that only the federal government, which may be far removed from the problem area and lack political credibility there, will be capable of devising and imposing a solution.”).

[145] See Doppelt et al., supra note 101, at 59 (“Effective watershed restoration also requires greatly improved system-wide policy coordination and consistency. On many rivers, 30 to 40 public agencies have programs entrained that affect the watershed. Each agency has different legislatively established missions and goals. . . . These interests fail to communicate with one another, and their activities and policies are almost never coordinated so that the integrity of the riverine system is maintained. New mechanisms are needed to move beyond the piecemeal management pattern evident on every riverine system nationwide so that systemwide planning, coordination and consistency can be realized.”).

[146] Comm. on Watershed Mgmt., supra note 96, at 5 (“Watersheds as geographic areas are optimal organizing units for dealing with the management of water and closely related resources, but the natural boundaries of watersheds rarely coincide with political jurisdictions and thus they are less useful for political, institutional, and funding purposes.”).

[147] Adler, supra note 6, at 991–92 (“[W]ater resource programs logically should be organized according to watershed boundaries. Politically, however, this has been difficult because each level of government guards its authority jealously. Instead, control over water resources is divided between federal, state, and local governments.” (footnote omitted)).

[148] Id. at 1088–89 (“[W]atershed programs should proceed at the scale of whole river basins or other broadly defined hydrological regions . . . . Watershed programs of broad regional scale, however, face significant political and institutional problems. Large watersheds usually cross more political boundaries (local, state, or national), resulting in greater need for intergovernmental coordination. . . . [E]ach new player complicates institutional and political problems and increases the possibility of turf battles, conflicting goals and values, and other parochial behavior. Problems range from the logistical challenge of coordinating a large number of governmental and nongovernmental entities, to the more fundamental difficulty of identifying and accommodating the needs of many regional interests, including diverse social, economic, and environmental interests.” (footnotes omitted)).

[149] Id. at 1103 (“[S]ome standardization would help avoid the very confusion, gaps, and conflicts that [voluntary] watershed programs are designed to address. Disparate watershed programs around the country likely would adopt divergent approaches to the issues of scale, boundary, mission, and control addressed above. Programs could overlap, conflict, or seek conflicting goals. Inefficiencies could occur due to overlapping jurisdictions, and individual programs would lose economies of scale. While flexibility is desirable to foster creative solutions appropriate to individual sites, management anarchy can be counterproductive.”).

[150] Peter P. Swire, The Race to Laxity and the Race to Undesirability: Explaining Failures in Competition Among Jurisdictions in Environmental Law, 14 Yale L. & Pol’y Rev. (Symposium Issue) 67, 80, 106 (1996) (“Understanding the Race to the Bottom and NIMBY in this way helps us understand important patterns in local environmental decisions, where people’s ‘back yards’ are especially noticeable. Either the Race to the Bottom or NIMBY, or both, might occur in a particular setting. Where the benefits of development are salient—with visible and concentrated benefits to industry and politicians—then public choice effects tend toward laxity. Where the costs of development are salient—with visible and concentrated costs on neighbors and consequent effects on politicians—then public choice effects tend toward strictness.”).

[151] Larry Kramer, Understanding Federalism, 47 Vand. L. Rev. 1485, 1499 (1994) (“[S]tate regulation is sometimes justified on the ground that it encourages regulatory innovation, the idea being that state and local governments have incentives to experiment with regulatory policy to attract capital and taxpayers—acting, in Justice Brandeis’ famous phrase, as ‘laboratories’ of democracy.” (citing New State Ice Co. v. Liebmann, 285 U.S. 262, 311 (1932) (Brandeis, J., dissenting))).

[152] See Sale, supra note 19, at 42 (emphasis added).

[153] See id. at 57 (“A watershed—the flows and valleys of a major river system—is a particularly distinctive kind of georegion, more easily mapped than most . . . .”).

[154] U.S. Const. art. IV, § 3, cl. 1.

[155] Id. art. I, § 2, cl. 1.

[156] See id. amend. XVII, cl. 1 (“The Senate of the United States shall be composed of two Senators from each State, elected by the people thereof . . . .”).

[157] Id. art. III, § 1.

[158] Id. art. V (“The Congress . . . shall propose Amendments to this Constitution, or, on the Application of the Legislatures of two thirds of the several States, shall call a Convention for proposing Amendments, which, in either Case, shall be valid to all Intents and Purposes, as Part of this Constitution, when ratified by the Legislatures of three fourths of the several States, or by Conventions in three fourths thereof, as the one or the other Mode of Ratification may be proposed by the Congress; Provided . . . that no State, without its Consent, shall be deprived of its equal Suffrage in the Senate.”).

[159] See id. art. I, § 2, cl. 1; id. art. I, § 3, cl. 1; id. art. II, § 1, cl. 2 (delegating representatives, senators, and electors on a state-by-state basis).

[160] See, e.g., Or. State Archive, Oregon State Bluebook: State Government, http://bluebook.state.or.us/state/index.htm (last visited Apr. 18, 2010) (explaining the branches of the Oregon state government, as well as their functions and powers).

[161] See generally U.S. Const. arts. I–III.

[162] 369 U.S. 186 (1962).

[163] Id. at 218–25 (“We shall discover that Guaranty Clause claims involve those elements which define a ‘political question,’ and for that reason and no other, they are nonjusticiable. In particular, we shall discover that the nonjusticiability of such claims has nothing to do with their touching upon matters of state governmental organization.”).

[164] 48 U.S. (7 How.) 1 (1849).

[165] See Baker, 369 U.S. at 220 (“Under this article of the Constitution it rests with Congress to decide what government is the established one in a State. For as the United States guarantee to each State a republican government, Congress must necessarily decide what government is established in the State before it can determine whether it is republican or not. And when the senators and representatives of a State are admitted into the councils of the Union, the authority of the government under which they are appointed, as well as its republican character, is recognized by the proper constitutional authority. And its decision is binding on every other department of the government, and could not be questioned in a judicial tribunal.” (internal quotation marks omitted) (quoting Luther, 48 U.S. at 42)).

[166] 88 U.S. (21 Wall.) 162 (1874).

[167] See Baker, 369 U.S. at 222–23 n.48 (“The guaranty is of a republican form of government. No particular government is designated as republican, neither is the exact form to be guaranteed, in any manner especially designated. Here, as in other parts of the instrument, we are compelled to resort elsewhere to ascertain what was intended. The guaranty necessarily implies a duty on the part of the States themselves to provide such a government. All the States had governments when the Constitution was adopted. In all the people participated to some extent, through their representatives elected in the manner specially provided. These governments the Constitution did not change. They were accepted precisely as they were, and it is, therefore, to be presumed that they were such as it was the duty of the States to provide. Thus we have unmistakable evidence of what was republican in form, within the meaning of that term as employed in the Constitution.” (internal quotation marks omitted) (quoting Minor, 88 U.S. at 175–76)).

[168] See U.S. Const. art. IV, § 3, cl. 1.

[169] See id.

[170] See Sale, supra note 19, at 91 (“The ecological law with which bioregional politics would logically begin is decentralism, centrifugal force, the spreading of power to small and widely dispersed units.”).

[171] See id. at 94–95.

[172] U.S. Const. art. I, § 6, cl. 2.

[173] U.S. Geological Survey, U.S. Dep’t of the Interior, National Atlas of the United States of America: Rivers and Lakes (2003), available at http://www-atlas.usgs.gov/printable/
images/pdf/outline/rivers_lakes.pdf.

[174] U.S. Const. art. III, § 2, cl. 1.

[175] See Charles W. Watson, Recent Cases, Environmental Law—Cause of Action Under Federal Common Law for Pollution of Interstate Waters, 77 Dick. L. Rev. 451, 454–56 (1972) (“Mr. Justice Douglas . . . held [in Illinois v. City of Milwaukee, 406 U.S. 91 (1972),] that federal common law controls the pollution of interstate waters. . . . Mr. Justice Douglas held that the legislative efforts [to] reduce the pollution of interstate waters and the express declaration of the federal policy of protecting the rights of the states to control pollution had established a right in an aggrieved state to abate a public environmental nuisance under the federal common law. . . . The federal common law as fashioned by the federal district courts will replace the various state laws in the area of interstate water pollution. Although the federal judges are to act largely on their own ‘informed judgments,’ uniformity is established in the sense that all actions brought in the district courts will be resolved according to the same body of federal common law . . . . The Supreme Court has long recognized that it possessed the jurisdiction to adjudicate the equitable rights of states in common waters. In addition, a state may enjoin another state from using common waters so as to create a nuisance to the citizens of the aggrieved state.” (footnotes omitted)).

[176] Amendment 1 describes a two-state method for boundary redrawing as severed from any general boundary-redrawing method and includes time limits for the redrawing process, restrictions on the negotiating parties to prevent conflicts of interest, the drawing of bioregionally oriented state boundaries on the basis of watersheds or bisected watersheds, the fair-division mechanism presented to the two states, and periods of time before the results of the negotiation are given effect.

[177] Amendment 2 describes a general boundary-redrawing method as coordinating an iterated series of two-state, boundary-redrawing negotiations as described in Amendment 1 and includes congressional ordering of boundary redrawing and setting of boundary-redrawing timelines, as well as provisions for boundaries not tractably redrawable by negotiation between States-in-Waiting.

[178] Amendment 3 describes the formation of bioregionally oriented boundaries of federal legal effect subsequent to a general boundary-redrawing method, and harmonizing bioregionally oriented federal boundaries with the bioregionally oriented state boundaries resulting from the general boundary-redrawing method.

[179] Amendment 4 describes the clarification of “Republican Form of Government” to require that boundaries within bioregionally oriented states, such as county boundaries, be themselves bioregionally oriented.

[180] Amendment 5 describes a grand bargain by which federal environmental policy must agree with environmental policy established by related bioregionally oriented states.

[181] See The Federalist No. 10, at 73–74 (James Madison) (Clinton Rossiter ed., 1961)
(“The latent causes of faction are thus sown in the nature of man; and we see them everywhere brought into different degrees of activity . . . . A zeal for different opinions concerning religion, concerning government, and many other points, as well of speculation as of practice; an attachment to different leaders ambitiously contending for pre-eminence and power; or to persons of other descriptions whose fortunes have been interesting to the human passions, have, in turn, divided mankind into parties, inflamed them with mutual animosity, and rendered them much more disposed to vex and oppress each other than to co-operate for their common good. So strong is this propensity of mankind to fall into mutual animosities, that where no substantial occasion presents itself, the most frivolous and fanciful distinctions have been sufficient to kindle their unfriendly passions and excite their most violent conflicts.”).

Brief for Natural Resources Defense Council as Amici Curiae Supporting Respondent, Monsanto Co. v. Geertson Seed Farms, No. 09-475 (U.S. Apr. 5, 2010)

By Craig Johnston*

Monsanto Co. v. Geertson Seed Farms is a case in which the Supreme Court is considering the propriety of an injunction the Ninth Circuit affirmed which precludes Monsanto from selling a form of genetically-modified alfalfa (known as Roundup Ready alfalfa or RRA) until the United States Department of Agriculture (USDA) complies with the National Environmental Policy Act (NEPA). The district court determined that the USDA, through its Animal and Plant Health Inspection Service (APHIS), had violated NEPA by failing to complete an environmental impact statement (EIS) before deregulating RRA. Neither Monsanto nor the United States appealed this aspect of the district courts opinion.

Instead, the only element of the case that is still at issue is the propriety of the district courts injunction. In seeking to overturn that injunction, Monsanto argues at the Supreme Court level, for the first time, that the sufficient likelihood of irreparable injury requirement dictates that a threatened harm, no matter how serious, must be preponderantly likely to occur before a court has the equitable power to enjoin conduct giving rise to that threat. It is this issue that Professor Johnston addresses in this brief for the Natural Resources Defense Council.

 

No. 09-475

IN THE SUPREME COURT OF THE UNITED STATES

MONSANTO COMPANY, ET AL., PETITIONER

v.

GEERTSON SEED FARMS, ET AL., RESPONDENT

On Writ Of Certiorari

To The United States Court Of Appeals

For The Ninth Circuit

 

BRIEF FOR AMICI CURIAE

NATURAL RESOURCES DEFENSE COUNCIL,

PROF. CRAIG N. JOHNSTON,

PROF. MICHAEL C. BLUMM,

PROF. DAVID W. CASE,

PROF. JAMISON E. COLBURN,

PROF. WILLIAM F. FUNK,

PROF. DAVID K. MEARS,

PROF. PATRICK A. PARENTEAU,

PROF. JOHN T. PARRY,

PROF. MELISSA A. POWERS, AND

PROF. MARY C. WOOD,

IN SUPPORT OF RESPONDENTS

 

[*Ed. note: The Table of Contents and Attorney Contact Information were omitted from this online-only version.  Please see the print version of Vol. 40, Issue 2 for the complete version] 

INTEREST OF THE AMICI CURIAE[1]

Amici curiae are a national environmental organization and ten law professors. The Natural Resources Defense Council, which has 1.2 million members and supporters, uses law and science to secure a safe and healthy environment for all living things. The amici law professors are teachers and students of environmental law, and have a longstanding interest in how the principles of equitable relief are applied in environmental cases.

The amici believe this is a case where respondents have readily met the traditional “likelihood of irreparable injury” requirement. The district court and court of appeals both expressly applied that test and found that irreparable injury was likely to occur. No good cause exists for this Court to revisit that factbound ruling. Petitioners, however, seek in their brief to inject a new legal issue, not raised below, by suggesting that the “likelihood” standard requires a rigid application of a “more likely than not” test for the probability of harm, irrespective of its potential magnitude. This case
does not provide the appropriate vehicle to consider the validity of this
newly-proffered test, not passed on by the courts below. In any event, the proposed standard is without merit. Should the Court decide to address the issue, it should therefore squarely reject the proffered standard. The sole purpose of this amicus submission is to address this issue in case the Court decides to consider it.

A further description of the amici is set forth in an Appendix to this brief.

SUMMARY OF THE ARGUMENT

It is hornbook law that courts may issue injunctions only where there is a likelihood of irreparable injury. See, e.g., Winter v. Natural Res. Def. Council, 129 S. Ct. 365, 375 (2008) (dicta), and City of Los Angeles v. Lyons, 461 U.S. 95, 111 (1983) (requiring a “sufficient likelihood” of such injury). Monsanto Co. (“Monsanto”) argues that this formulation denies courts the power to issue injunctions in response to threatened harms, no matter how serious their potential consequences, unless those harms are more than 50% likely to materialize. Brief for Monsanto (“Petr.’s Br.”) 33, 41-47. This argument wrongly assumes that the term “likelihood” connotes “more likely than not” in this context. It also ignores the basic principle that whether a threatened harm is “sufficiently likely” turns on both the probability of its occurrence and the severity of its consequences should it occur.

Monsanto’s reading of the traditional equitable test is both illogical and ahistorical. Under its approach, for example, courts would be unable to enjoin the maintenance of severe fire hazards in residential areas if the risks of conflagration were “only” 40%. Similarly, a court would be powerless even where a simple injunctive order might be all that is required to preclude a 50% chance that a lethal virus would be introduced to New York City’s
water supply.

As will be shown below, the courts of equity long have used both public and private nuisance principles to halt conduct and address conditions posing serious threats to the public weal, regardless of whether the feared harm was more likely than not to come to fruition. While at first there were not many cases, their numbers have increased over the years. Where the threats have been sufficiently serious, the courts have simply deemed the circumstances giving rise to them to be nuisances, which in turn has enabled them to issue injunctive relief where necessary to achieve equity. In case after case, the courts have applied these dynamics without requiring that the harm be preponderantly likely to occur. In effect, where faced with sufficiently serious threats of irreparable harm, courts have recognized that the threats themselves constitute a likely and enjoinable injury, under bedrock principles of equity jurisdiction.

That courts show an increasing tendency to focus on the overall significance of the relevant threats, rather than solely on the likelihood that the feared consequences will come to pass, is fully consistent with the Restatement (Second) of Torts. It also comports with both modern principles of risk assessment and the analysis that this Court and others have applied in related contexts. And finally, it closely tracks an analogous development in environmental law, the advent of the so-called “imminent hazard” provisions that Congress patterned on public nuisance principles.

In the face of this longstanding history and legal evolution, Monsanto reads this Court’s opinion in Winter as mandating a significant reworking of the basic principles of equitable jurisdiction. Petr.’s Br. 41-47. Winter, however, is far too slender a reed to support such a major change. Indeed, Winter not only fails to signal any such change, it expressly embraces traditional principles. Moreover, it contains no holding at all regarding the irreparable injury requirement.

We of course recognize that judicial enforcement of the statute at issue in this case, the National Environmental Policy Act, 42 U.S.C. § 4321, et seq. (“NEPA”), focuses on the procedures it prescribes. This does not mean, however, that this Court should discount its congressionally-articulated substantive goals when considering the presence of irreparable injury. Congress intended for NEPA to influence governmental decision-making profoundly. To effectuate this goal, Congress required agencies to undertake extensive analysis whenever their actions may “significantly affect” the environment, see 42 U.S.C. § 4332(2)(C) and 40 C.F.R. § 1501.4. That the potential for such effects was intended to trigger action only serves to emphasize why the “likelihood of irreparable injury” requirement should not be deemed to require a more-likely-than-not standard. This Court should honor Congress’s intent that potentially significant environmental risks be examined by ensuring that federal courts have the broad equitable discretion to determine, in appropriate cases, that an agency’s failure to comply with NEPA poses a sufficient threat of harm to constitute a likelihood of irreparable injury, even if that harm is not preponderantly likely to occur.

ARGUMENT

I.                       THE COURTS OF EQUITY LONG HAVE HAD THE AUTHORITY TO ISSUE INJUNCTIONS IN THE FACE OF SIGNIFICANT THREATS.

a.     The history of the common law fully supports the idea that courts may address situations that pose unreasonable harm of injury, and that they may issue injunctions in response to those threats.

Under the common law, courts long have had the power to issue injunctions in the face of significant threats, regardless of whether the threatened harms were at least 51% likely to come to fruition. In these cases, all plaintiffs have been required to show is that the conduct poses a significant threat to the public health, safety, or welfare. They have not been required to show a preponderant likelihood that the threat will result in the feared consequences. The circumstances themselves, if sufficiently threatening, constitute a nuisance and give rise to a claim for injunctive relief.

This power may be most apparent in the realm of public nuisance law. This Court traced the history of the equitable power to address these nuisances in Mugler v. State of Kansas, 123 U.S. 623 (1887):

“In regard to public nuisances,” Mr. Justice Story says, “the jurisdiction of courts of equity seems to be of very ancient date, and has been distinctly traced back to the reign of Queen Elizabeth. The jurisdiction is applicable, not only to public nuisances, strictly so called, but also to purprestures upon public rights and properties. . . . In case of public nuisances, properly so called, an indictment lies to abate them, and to punish the offenders. But an information also lies in equity to redress the grievance by way of injunction.” 2 Story, Eq. Jur. §§ 921, 922. The ground of this jurisdiction in cases on purpresture, as well as of public nuisances, is the ability of courts of equity to give a more speedy, effectual, and permanent remedy than can be had at law. They can not only prevent nuisances that are threatened, and before irreparable mischief ensues, but arrest or abate those in progress, and, by perpetual injunction, protect the public against them in the future; whereas courts of law can only reach existing nuisances, leaving future acts to be the subject of new prosecutions or proceedings. This is salutary jurisdiction, especially where a nuisance affects the health, morals or safety of the community. Though not frequently exercised, the power undoubtedly exists in courts of equity to protect the public against injury. [Citations omitted].

Id. at 672–73 (emphasis added); see also United Steelworkers of Am. v. United States, 361 U.S. 39, 60 (1959) (citing English public nuisance cases involving injunctions as far back as 1587). Additionally, this Court long has recognized that public nuisance doctrine embraces both health and other environmental protection concerns. Georgia v. Tenn. Copper Co., 206 U.S. 230 (1907) (deeming air pollution a public nuisance because of its impacts on both forests and public health in a neighboring state); see also Ariz. Copper Co. v. Gillespie, 230 U.S. 46, 56–57 (1913) (water pollution deemed a public nuisance), and New Jersey v. City of New York, 283 U.S. 473 (1931) (same).

In most nuisance cases, both public and private, the relevant conduct or conditions already have given rise to harm, and thus it is often easy for courts to find a sufficient threat of future harm. That was certainly true in Tennessee Copper, Arizona Copper, and City of New York. In other cases, however, the threat is present but has not yet given rise to harm. Where the courts have deemed such threats sufficiently serious, however, they have not hesitated to find that the conduct or condition constitutes a nuisance, without inquiring into whether the threatened harms were more likely than not to materialize. As early as 1799, for example, upon finding that certain houses in which the defendant was storing sugar were structurally unsound, the chancellor in London v. Bolt, 5 Ves. Jun. 129, 31 Eng. Rep. 507 (Ch. 1799), relied on public nuisance doctrine to issue an injunction preventing the defendant from adding any additional sugar. Similarly, in R. v. Vantandillo, 4 M. & S. 73, 105 Eng. Rep. 762 (K.B. 1815), the court determined that carrying a child with smallpox along a public highway constituted a public nuisance, without any finding regarding the likelihood that this conduct would cause harm to anyone else.[2]

In this country, the earliest cases recognizing that a significant risk could in itself constitute a nuisance arose in the context of private nuisance law. In Tyner v. People’s Gas Co., 132 Ind. 408, 31 N.E. 61 (1892), for example, the Indiana Supreme Court overruled a demurrer where the defendant was intending to use nitroglycerin to “shoot” a well on its property, which the plaintiff alleged would pose a serious, but unquantified, risk of explosion, thus endangering both the plaintiff and his family. The court stated that:

It is settled by our own decisions that the erection or the maintaining of anything that is injurious to health . . . , so as essentially to interfere with the comfortable enjoyment of life or property, constitutes a private nuisance. To live in constant apprehension of death from the explosion of nitroglycerin is certainly an interference with the comfortable enjoyment of life. Injunction is the proper remedy for an injury of this kind.

31 N.E. at 62. Similarly, in Ferry v. City of Seattle, 116 Wash. 648, 303 P. 40 (1922), the Washington Supreme Court affirmed a lower court injunction prohibiting the construction of a dam where it would pose an unacceptable risk to neighboring property owners. Here also, neither the plaintiff nor the court quantified the risk. In its analysis, though, the court explicitly factored in the magnitude of the consequences when discussing their probability:

The test as to whether a structure of the proposed character is to be declared a nuisance turns on whether the complaining property owners are under a reasonable apprehension of danger, and the question of the reasonableness of the apprehension turns again, not only on the probable breaking of the reservoir, but the realization of the extent of the injury which would certainly ensue; that is to say the court will look to consequences in determining whether the fear existing is reasonable. For instance, if the reservoir were being built in some place where, should it break, the resultant damage would be merely to property which could adequately be recompensed, the court would be more apt to hesitate in declaring it a nuisance than where, should a break occur, not only property of immense value would be destroyed, but many lives would be lost
as well.

Id. at 662.

Early treatises also recognized the need to apply a sliding scale regarding the likelihood of the harm in situations in which the consequences may be severe. As early as in 1919, Pomeroy’s Treatise on Equitable Remedies provided that:

. . . On the one hand, a mere possibility of a future nuisance will not support an injunction; it must be probable. On the other hand, the plaintiff . . . does not need to establish this probability by proof amounting to a virtual certainty that the nuisance will occur, nor even proof which establishes it beyond a reasonable doubt; it is sufficient if he show that the risk of its happening is greater than a reasonable man would incur. And the balance between these two rules will be affected by the seriousness of the nuisance feared, the strength required for the plaintiff’s proof diminishing somewhat as the greatness of the apprehended damage increases.

Pomeroy, A Treatise on Equity Jurisprudence and Equitable Remedies, Vol. 5, § 523, p. 4398 (1919) (emphasis added).

By the middle of the 20th century, courts were applying this logic in the public nuisance context. In Harris Stanley Coal & Land Co. v. Chesapeake & Ohio Railway Co., 154 F.2d 450 (6th Cir. 1946), cert. denied, 329 U.S. 761 (1946), a railroad appealed the district court’s denial of an injunction through which the railroad sought to preclude a mining company from removing pillars of coal that were designed to support the surface of the land. Id. at 452. The lower court had found that there was a “possibility or even probability that the mountain side would slip or subside,” but nonetheless denied the injunction. Id. The Sixth Circuit reversed, emphasizing the seriousness of the potential consequences:

If the threatened injury to the railroad right-of-way be envisioned merely as the sliding of some of the surface material of the mountain upon the railroad right-of-way necessitating some expense in its removal and in the repair of the roadbed, we might well say that recovery of damages in a suit at law provides adequate remedy. We have here, however, a railroad over which pass trains bearing passengers and freight. Their daily number is not disclosed by the record, and being but a branch line it may be assumed that the traffic is not heavy. Nevertheless, traffic there is, and the effect of a substantial mountain slide upon a passing train might well be catastrophic. It may be that such disaster could occur only upon a concatenation of circumstances of not too great probability, and that the odds are against it. It is common experience, however, that catastrophies occur at unexpected times and in unforeseen places.. . . A court of equity will not gamble with human life, at whatever odds, and for loss of life there is no remedy at law.

Id. at 453; see also County of San Diego v. C.W. Carlstrom, 196 Cal. App. 2d 485, 16 Cal. Rptr. 667 (1961) (finding a fire hazard to be a public nuisance without any quantification regarding the likelihood of a fire).

More recently, the courts have applied this kind of risk-based logic in a broader array of equitable contexts, finding nuisances and authorizing injunctive relief in situations where it has been far from certain that the relevant threat, while significant, was likely to give rise to the feared consequences. Perhaps most tellingly, this Court in Lucas v. South Carolina Coastal Council, 505 U.S. 1003 (1992), implicitly assumed that risk analysis can play a role in determining what constitutes a nuisance. There, in exploring the relationship between takings law and nuisance principles, the Court insisted that “the corporate owner of a nuclear generating plant” could not successfully raise a takings claim “when it is directed to remove all improvements from its land upon discovery that the plant sits astride an earthquake fault.” Id. at 1029. The mere existence of a fault in such a situation would not, of course, make an earthquake more likely than not, let alone create a likelihood of radioactive release. As the Court appeared to recognize, it is the severity of the potential consequences that would make the threat abatable as a public or private nuisance, and hence undermine a takings claim.

Other courts have applied a similar calculus to nuisance cases involving hazardous waste contamination[3] and threats to the public safety from the possibility of gang violence,[4] over-aggressive protesters,[5] and potentially violent demonstrations.[6] In none of these cases did the courts feel the need to quantify the likelihood that the threatened harms would come to pass. After identifying a significant threat to the public weal, they simply found nuisances to exist and issued injunctions designed to abate them.

b. The Restatement (Second) of Torts is fully in accord with
these cases.

The Restatement (Second) of Torts (“Restatement”) expressly contemplates that conduct and conditions giving rise to unreasonable risks of harm are actionable under principles of both public and private nuisance. It further contemplates that courts may enjoin these injuries without first finding a preponderant likelihood that the relevant harm will materialize.

Turning first to public nuisances, the Restatement defines such a nuisance as “an unreasonable interference with a right common to the general public.” Restatement (Second) of Torts § 821B (1977). It further provides that “[c]ircumstances that may sustain a holding that an interference with a public right is unreasonable include [situations in which] the conduct involves a significant interference with the public health, the public safety, the public peace, the public comfort or the public convenience.” Id. Comment b to that section lists “the maintenance of a pond breeding malarial mosquitoes” as an example of an interference with the public health, and “bad odors, dust and smoke” as examples of interferences with the public comfort. Id. § 821B, cmt. b, p. 88. Elsewhere, the Restatement cites pollution leading to a beach closure as yet another example of a public nuisance. Id. § 832, cmt. b, p. 143.

Under the Restatement, an “unreasonable” or “significant” interference with the public health, safety, peace, comfort, or convenience is all that is required. Nothing in the Restatement suggests that public-nuisance plaintiffs must show a preponderant likelihood that someone will actually get sick or suffer a physical injury or some other clear manifestation of harm, either as part of their prima facie case or to establish an entitlement to equitable relief. In the beach closure context, for example, it is presumed that a health threat warranting beach closure is actionable, without any required showing that would-be swimmers face at least a 51% likelihood of becoming ill.

The provisions of the Restatement pertaining to private nuisances apply similar logic. Section 821D defines a private nuisance as a “nontrespassory invasion of another’s interest in the private use or enjoyment of land.” Id. § 821D. Sections 821F and 822 note that the harm must be both “significant” and either “intentional and unreasonable” or “unintentional and otherwise actionable” under either negligence standards or principles of strict liability. Id. §§ 821F and 822, respectively.[7]

It is in the Comments to § 822 that the Restatement makes clear that a significant risk of harm constitutes a cognizable injury under this formulation. Comment g, addressing the unreasonableness requirement in the context of intentional invasions, provides that:

. . . The very existence of organized society depends upon the principle of “give and take, live and let live,” and therefore the law of torts does not attempt to impose liability or shift the loss in every case in which one person’s conduct has some detrimental effect on another. Liability for damages[8] is imposed in those cases in which the harm or risk to one is greater than he ought to be required to bear under the circumstances, at least without compensation.[9]

Id. § 822, cmt. g, p. 112 (emphasis added).

Chapter 48 of the Restatement, which deals specifically with the appropriateness of tort-related injunctions, further illuminates the role that risk plays in both public and private nuisance doctrine. First, § 933(1) indicates that injunctions are available for both committed and threatened torts, depending upon the appropriateness of such issuance as determined by the factors listed in § 936. Id. § 933(1). In turn, § 936(1) contemplates a “comparative appraisal of all of the factors in the case,” including:

(a) the nature of the interest to be protected,

(b) the relative adequacy to the plaintiff of injunction and other remedies,

(c) any unreasonable delay by the plaintiff in bringing suit,

(d) any related misconduct on the part of the plaintiff,

(e) the relative hardship likely to result to defendant if an injunction is granted and to plaintiff if it is denied,

(f) the interests of third persons and of the public, and

(g) the practicability of framing or enforcing the order or judgment.

Id. § 936(1).

In Comment b to Section 933, the Restatement more thoroughly addresses the need to enjoin improbable but serious harms, when it discusses “threatened torts.” There, it speaks in the following terms:

The expression “threatened tort,” as used in Subsection (1) of this Section, contemplates, as a condition for the grant of an injunction, a threat of sufficient seriousness and imminence to justify coercive relief. The seriousness and imminence of the threat are in a sense independent of each other, since a serious harm may be only remotely likely to materialize and a trivial harm may be quite imminent. Yet the two elements must be considered together in the decision of any given case. The more serious the impending harm, the less justification there is for taking the chances that are involved in pronouncing the harm too remote.

Id. § 933, cmt. b, p. 561 (emphasis added). A comment to § 821F both emphasizes this point and makes it specifically applicable to both public and private nuisances:

. . . [E]ither a public or private nuisance may be enjoined because harm is threatened that would be significant if it occurred, and that would make the nuisance actionable under the rule here stated, although no harm has
yet resulted.

Id. § 821F, cmt. b, p. 105.

In short, the Restatement contemplates that the significance of the risk can be considered in determining both whether a nuisance exists and whether injunctive relief is an appropriate remedy. In neither context is it necessary that there be a preponderant likelihood that the threatened harm will come to pass; if the potential harm is particularly serious, the Restatement contemplates that courts will be prepared to guard against even a low likelihood of its occurring.

Finally, once a nuisance has been established, the Restatement does not require a separate showing regarding the likelihood of irreparable injury. Section 936(1) includes the other traditional equitable factors, but not that one. Although this goes unexplained in the Restatement, the only logical conclusion is that the nuisance finding equates to a finding that there is a sufficient likelihood of irreparable injury.[10] This interpretation draws support from § 7 of the Restatement, which distinguishes the concept of “injury” from that of “harm.” The word “injury,” it makes clear, denotes “the invasion of any legally protected interest of another,” as distinct from “harm,” which is used to mean an actual loss or detriment. Id. § 7 (1965). Thus, under the Restatement one can be irreparably injured without having actually been harmed.

c. The tendency of courts to issue injunctions in the face of significant threats comports with sound risk analysis and the approaches that this Court and others have taken in analogous contexts.

If there is one unifying principle in the modern regulatory world, it is that analyzing risk requires an understanding not only of the likelihood of a particular outcome, but also of the severity of its potential effects.
Nat’l Research Council, Science and Judgment in Risk Assessment 4
(1994); School Bd. of Nassau County, Fla. v. Arline, 480 U.S. 273, 287–88 (1987) ( “Arline”).

Ever since Judge Hand first analyzed negligence issues in terms of whether the burden of the relevant precautions was less than the probability of an accident, multiplied by the gravity of the resulting injury, United States v. Carroll Towing Co., 159 F.2d 169 (2d Cir. 1947), courts have increasingly embraced modern risk analysis. This Court expressly embraced the fundamental principles of risk assessment in Arline. As the Court later summarized in Bragdon v. Abbott, 524 U.S. 624 (1998), Arline dealt with the

. . . importance of prohibiting discrimination against individuals with disabilities while protecting others from significant health and safety risks, resulting, for instance, from a contagious disease. In Arline, the Court reconciled these objectives by construing the [relevant statute] not to require the hiring of a person who posed a significant risk of communicating an infectious disease to others.

Id. at 649 (quotation omitted). In Arline, the Court determined that the “significance” inquiry should include:

“[findings of] facts, based on reasonable medical judgments given the state of medical knowledge, about (a) the nature of the risk (how the disease is transmitted), (b) the duration of the risk (how long is the carrier infectious), (c) the severity of the risk (what is the potential harm to third parties) and (d) the probabilities the disease will be transmitted and will cause varying degrees of harm.”

Arline, 480 U.S. at 288 (quoting from a brief filed by the American Medical Association).

This Court also squarely embraced a “significant threats” approach in Helling v. McKinney, 509 U.S. 25 (1993). There, the Court determined that the Eighth Amendment’s “cruel and unusual punishment” standard forbids not only prison conditions that are likely to make a particular inmate ill, but  also those that pose “an unreasonable risk of serious damage to [a prisoner’s] future health.” Id. at 35.

The lower courts have applied similar logic in related contexts. Most significantly, they have adopted risk-based ideas in applying the “likelihood of prevailing on the merits” standard that governs the issuance of preliminary injunctions. In American Hospital Supply Corp. v. Hospital Products Ltd., 780 F.2d 589 (7th Cir. 1986), for example, Judge Posner wrote that:

A district judge asked to decide whether to grant or deny a preliminary injunction must choose the course of action that will minimize the costs of being mistaken. Because he is forced to act on an incomplete record, the danger of a mistake is substantial. And a mistake can be costly. If the judge grants the preliminary injunction to a plaintiff who it later turns out is not entitled to any judicial relief – whose legal rights have not been violated – the judge commits a mistake whose gravity is measured by the irreparable harm, if any, that the injunction causes to the defendant while it is in effect. If the judge denies the preliminary injunction to a plaintiff who it later turns out is entitled to judicial relief, the judge commits a mistake whose gravity is measured by the irreparable harm, if any, that the denial of the preliminary injunction does to the plaintiff.

These mistakes can be compared, and the one likely to be less costly can be selected, with the help of a simple formula: grant the preliminary injunction if but only if P x Hp > (1 – P) x Hd, or, in words, only if the harm to the plaintiff if the injunction is denied, multiplied by the probability that the denial would be an error (that the plaintiff, in other words, will win at trial), exceeds the harm to the defendant if the injunction is granted, multiplied by the probability that granting the injunction would be an error. That probability is simply one minus the probability that the plaintiff will win at trial; for if the plaintiff has, say, a 40 percent chance of winning, the defendant must have a 60 percent chance of winning (1.00 – .40 = .60). The left-hand side of the formula is simply the probability of an erroneous denial weighted by the cost of denial to the plaintiff, and the right-hand side simply the probability of an erroneous grant weighted by the cost of grant to the defendant.

Id. at 593; see also FoodCom Int’l v. Barry, 328 F.3d 300, 303 (7th Cir. 2003). Similarly, the Second Circuit has applied a sliding-scale approach in the same context, requiring “either (1) likelihood of success on the merits or (2) sufficiently serious questions going to the merits to make them a fair ground for litigation and a balance of hardships tipping decidedly toward the party requesting the preliminary relief.” Jackson Dairy, Inc. v. H.P. Hood & Sons, Inc., 596 F.2d 70, 72 (2d Cir. 1979).[11]

d. Congress has recognized the importance of risk analysis in injunctive settings when it codified public nuisance principles
in various environmental laws. Courts have done the same in applying those provisions.

In the environmental realm, risk assessment principles manifest themselves in various ways.[12] The place where Congress has made most apparent its embrace of risk assessment principles specifically in the injunctive relief context is in the so-called “imminent hazard” provisions in several pollution control statutes. See, e.g., 42 U.S.C. §§ 6973, 9606. Congress expressly patterned these provisions on public nuisance principles. See, e.g., S. Rep. No. 96-172., 1st Sess., at 5, as reprinted in (1980) U.S.C.C.A.N. 5019, 5023; see also United States v. Waste Indus., Inc., 734 F.2d 159 (4th Cir. 1984).

Sections 7002(a)(1)(B) and 7003 of the Resource Conservation and Recovery Act, 42 U.S.C. § 6972(a)(1)(B) and 6973, are typical of these provisions. Under these provisions, Congress empowered the courts to issue injunctions, at either citizens’ or the Government’s behest (respectively), whenever the handling or disposal of any solid or hazardous waste “may present an imminent and substantial endangerment to health or the environment.” In keeping with this language, courts have found that Congress authorized relief whenever there is a “reasonable cause for concern that someone or something may be exposed to a risk of harm by a release or a threatened release of a hazardous substance if remedial action is not taken.” Interfaith Comty. Org. v. Honeywell Int’l., Inc., 399 F.3d 248, 259 (3d Cir. 2005) (upholding injunction in a citizen suit).[13] In Reserve Mining Co. v. Environmental Protection Agency, 514 F.2d 492 (8th Cir. 1975), the Eighth Circuit elaborated on this idea in a case involving a predecessor to the Clean Water Act’s current “imminent hazard” provision:

These concepts of potential harm, whether they be assessed as “probabilities and consequences” or “risk and harm,” necessarily must apply in a determination of whether any relief should be given in cases of this kind in which proof with certainty is impossible. The district court, although not following a precise probabilities-consequences analysis, did consider the medical and scientific evidence bearing on both the probability of harm and the consequences should the hypothesis advanced by the plaintiffs prove to be valid.

In assessing probabilities in this case, it cannot be said that the probability of harm is more likely than not. Moreover, the level of probability does not readily convert into a prediction of consequences. On this record it cannot be forecast that the rates of cancer will increase from drinking Lake Superior water or breathing Silver Bay air. The best that can be said is that the existence of this asbestos contaminant in air and water gives rise to a reasonable medical concern for the public health. The public’s exposure to asbestos fibers in air and water creates some health risk. Such a contaminant should be removed.

Id. at 520.

II. WINTER DID NOT ALTER THE TRADITIONAL EQUITABLE REQUIREMENTS FOR AN INJUNCTION.

In Winter, this Court indicated that the Ninth Circuit had erred in determining that any “possibility” of irreparable injury was sufficient to satisfy the irreparable injury threshold in NEPA cases. 129 S. Ct. at 375 (citing, inter alia, Faith Center Church Evangelistic Ministries v. Glover,
480 F.3d 891, 906 (9th Cir. 2007)
). Significantly, however, the Court did not articulate the circumstances in which an actual threat of significant harm can constitute a sufficient likelihood of irreparable injury. Nor did it indicate that it was altering the traditional principles of equitable relief in any way;
to the contrary, the Court’s entire discussion is framed as an application of those basic principles. Id. at 374–82.

Moreover, specifically with regard to the “likelihood of irreparable injury” standard, the Winter Court declined to make any finding regarding whether the plaintiff had met the equitable test. Instead, despite the Navy’s contention that there had been no documented harm to marine mammals during 40 years of similar training in the relevant area, the Court specifically rested its holding on other grounds, concluding that “even if plaintiffs have shown irreparable injury from the Navy’s training exercises, any such injury is outweighed by the public interest and the Navy’s interest in effective, realistic training of its sailors.” Id. at 376.

Monsanto’s argument in this case is wholly premised on the idea that Winter altered the traditional equitable test regarding the likelihood of irreparable injury. See Petr.’s Br. 41–47. Winter, however, did no such thing. The Court’s “irreparable injury” discussion in Winter simply cannot bear the weight Monsanto puts on it.

III. THAT NEPA IMPOSES ONLY PROCEDURAL MANDATES SHOULD NOT UNDERMINE THE ABILITY OF THE COURTS TO ENJOIN ACTIONS THAT WILL LIKELY LEAD TO IRREPARABLE INJURY.

Most environmental statutes contain enforceable substantive mandates. See, e.g., 33 U.S.C. § 1311(b) (Clean Water Act). In that context, it may be that violations of those standards should constitute irreparable harm as a matter of law. This conclusion would seem consistent with United States v. Oakland Cannabis Buyers’ Cooperative, 532 U.S. 483 (2001) (“Oakland Cannabis”). In that case, this Court held that:

. . . [A] court sitting in equity cannot ignore the judgment of Congress, deliberately expressed in legislation. A district court cannot, for example, override Congress’ policy choice, articulated in a statute, as to what behavior should be prohibited. Once Congress, exercising its delegated powers, has decided the order of priorities in a given area, it is . . . for the courts to enforce them when enforcement is sought. Courts of equity cannot, in their discretion, reject the balance that Congress has struck in a statute. Their choice (unless there is statutory language to the contrary) is simply whether a particular means of enforcing the statute should be chosen over another permissible means; their choice is not whether enforcement is preferable to no enforcement at all. Consequently, when a court of equity exercises its discretion, it may not consider the advantages and disadvantages of nonenforcement of the statute, but only the advantages and disadvantages of employing the extraordinary remedy of injunction over other available methods of enforcement. To the extent the district court considers the public interest and the conveniences of the parties, the court is limited to evaluating how such interest and conveniences are affected by the selection of an injunction over other enforcement mechanisms.

Oakland Cannabis, 532 U.S. at 497–498 (internal quotations and footnotes  omitted).[14]

While this Court has determined that NEPA “imposes on agencies duties that are essentially procedural,” Strycker’s Bay Neighborhood Council, Inc. v. Karlen, 444 U.S. 223, 227 (1980), it also has recognized that the statute has broad substantive goals. Id.; see also Robertson v. Methow Valley Citizens Council, 490 U.S. 332, 350–51 (1989). Among its other objectives, Congress sought through NEPA to “assure for all Americans safe, healthful, productive, and esthetically pleasing surroundings.” 42 U.S.C. § 4331(b)(2). That Congress sought to achieve these goals through procedural means does not undermine the seriousness of the goals themselves. As this Court noted:

The sweeping policy goals announced in § 101 of NEPA are [to be] realized through a set of action-forcing procedures that require that agencies take a hard look at environmental consequences, and that provide for broad dissemination of relevant environmental information. . . .

Methow Valley, 490 U.S. at 350 (internal quotations omitted). The Methow Valley Court also noted that “these procedures are almost certain to affect the agency’s substantive decision.” Id.

The plaintiffs in this case have a legal injury and cannot be adequately compensated by monetary damages.[15] Additionally, the real-world threats here at issue are serious and have not been adequately studied, as required by Congress. In situations where, as here, there is a reasonable prospect of significant harm, lower courts should have the discretion to determine whether an agency’s failure to comply with the law entails a sufficient likelihood of irreparable injury to support equitable relief. This is particularly true in the context of a statute such as NEPA, where Congress has expressly recognized “the critical importance of  . . . maintaining environmental quality,” 42 U.S.C. § 4331(a), and “direct[ed] that, to the fullest extent possible: (1) the policies, regulations, and public laws of the United States shall be interpreted and administered in accordance with [NEPA’s] policies. . . .” 42 U.S.C. § 4332.

In other contexts this Court has not hesitated to invoke its equitable powers to address procedural violations in the absence of any affirmative demonstration of a preponderant likelihood of substantive irreparable harm. In Clark v. Roemer, 500 U.S. 646 (1991), for example, the Court dealt with a violation of the “preclearance” provisions in § 5 of the Voting Rights Act of 1965, 42 U.S.C. § 1973c. In that case, the district court had allowed both an election to go forward and the winners to assume their offices (at least provisionally), despite violations of § 5. A unanimous Court reversed, holding that the district court was required to enjoin the illegal election. Id. at 654. The Court did this without any inquiry into whether the plaintiffs had shown that the procedural violation—the State’s failure to obtain preclearance—had led or was likely to lead to any irreparable harm.[16] Instead, the Court announced a nearly automatic rule that injunctions should issue in these contexts:

We need not decide today whether there are cases in which a district court may deny a § 5 plaintiff’s motion for injunction and allow an election for an unprecleared seat to go forward. An extreme circumstance might be present if a seat’s unprecleared status is not drawn to the attention of the State until the eve of the election and there are equitable principles that justify allowing the election to proceed. No such exigency exists here.

Id. at 654–655; see also Branch v. Smith, 538 U.S. 254 (2003).

Of course, NEPA is not the Voting Rights Act. However, NEPA plaintiffs such as Geertson Seed Farms stand to suffer substantive and legally cognizable injuries, which may be avoided if the required procedures are followed. And, as in this case, the real world harms at stake in NEPA cases can be quite significant.[17] Moreover, the NEPA process can and often does make a substantive difference. Again, in Methow Valley this Court deemed that prospect “almost certain.” 490 U.S. at 350. Indeed, as this Court noted in Lujan v. Defenders of Wildlife, 504 U.S. 555, 573 n.7 (1992), it is that very possibility that gives those who live near proposed federal projects redressability for Article III purposes.

Courts have always construed the elements required for equitable relief in a flexible fashion, with due deference to trial court judges. As seen above, the “likelihood of irreparable injury” standard is perfectly well suited to averting substantial risks of significant harm, even absent a preponderant likelihood that the harm will come to pass. In the NEPA context, there may certainly be some cases where the threat of significant harm is so minor that the legal injury any potential plaintiffs could suffer should not, by itself, be deemed to meet the irreparable injury requirement. This case, however, is not one of them.

 

Respectfully submitted,

Allison M. LaPlante

 

APPENDIX

Description of Amici Curiae

The Natural Resources Defense Council is one of the nation’s leading environmental organizations, with 1.2 million members and supporters. Its mission is to safeguard the Earth: its people, its plants and animals and the natural systems on which all life depends.

 

Craig N. Johnston is a professor of law at Lewis & Clark Law School, where he teaches courses in environmental law and environmental enforcement, among other courses. Prof. Johnston also has coauthored casebooks in both environmental law and hazardous waste law.

 

Michael C. Blumm is a professor of law at Lewis & Clark Law School, where he teaches property, legal history and other courses. Professor Blumm has written widely on environmental issues.

 

David W. Case is an associate professor of law at the University of Mississippi, where he teaches civil procedure, contracts, and environmental law. He has also written extensively in the field of environmental law.

 

Jamison E. Colburn is a professor of law at Pennsylvania State University, where he teaches constitutional law, administrative law, and environmental law. He has written widely on administrative and environmental issues.

 

William F. Funk is a professor of law at Lewis & Clark Law School, where he teaches environmental law and other courses. Prof. Funk has coauthored casebooks in constitutional law, environmental law and administrative law.

 

David K. Mears is an associate professor of law at Vermont Law School, where he teaches property and environmental law. Professor Mears also directs the law school’s Environmental and Natural Resources Law Clinic.

 

Patrick A. Parenteau is a professor of law at Vermont Law School, where he is senior counsel to the school’s Environment and Natural Resources Law Clinic. Prof. Parenteau also teaches many courses, including one on environmental litigation.

 

John T. Parry is a professor of law at Lewis & Clark Law School, where he teaches criminal law, civil procedure, and other courses. Professor Parry has also written several books on the law of torture.

 

Melissa A. Powers is an assistant professor of law at Lewis & Clark Law School. Professor Powers teaches torts and energy law, among other courses. She has coauthored a casebook on climate change and the law.

 

Mary C. Wood is the Phillip H. Knight Professor at the University of Oregon School of law. Prof. Wood teaches and publishes in the fields of property, environmental, and Indian law.

 

 


* Professor of Law, Lewis & Clark Law School; B.A., 1978 University of Rochester; J.D., magna cum laude, 1985 Lewis & Clark Law School. Because Professor Johnston is not currently an active member of the Oregon bar, he could not be the counsel of record on this brief. While Ms. LaPlante reviewed the brief before it was filed, Professor Johnston was its author. The author would like to thank Brett Hartl, Ben Luckett, Amy van Saun, Nate Hausman, and Elizabeth Zultoski for their terrific research assistance. Additionally, he would like to thank Niel Lawrence, Nancy Marks, and Professors Allison LaPlante, Tomás Gómez-Arostegui, and Bill Funk for their outstanding comments on prior drafts.

[1] The Government’s written consent to the filing of this brief is on file with the Clerk of this Court. The other parties’ written consents are being submitted with this brief. Pursuant to S. Ct. R. 37.6, amici affirm that this brief was not authored in whole or in part by counsel for a party, and that no monetary contribution to the preparation or submission of this brief was made by any person other than amici or their counsel.

[2] This was a criminal case brought in the King’s Bench, a court which in 1815 could not grant injunctions. We cite it here as an example of another early decision deeming conduct threatening to the public weal to constitute a public nuisance, without either quantifying the risk or concluding that the threatened harm was likely to materialize.

[3] See, e.g., Village of Wilsonville v. SCA Servs., Inc., 77 Ill. App. 3d 618, 635–636, 396 N.E.2d 552, 564 (4th Dist. 1979), aff’d, 86 Ill. 2d 1, 426 N.E.2d 824 (1981) (“The trial court could have determined from the evidence that the harm that would impend because of the danger that hazardous substances might escape was so serious that no justification existed to deny the injunction even though the feared harm was uncertain as to occurrence and, in any event, unlikely to occur until the distant future.”); Wood v. Picillo, 443 A.2d 1244, 1247 (1982) (“According to experts, the chemicals present on defendant’s property and in the marsh, left unchecked, would eventually threaten wildlife and humans well downstream from the dump site.”).

[4] People ex rel. Gallo v. Acuna, 14 Cal. 4th 1090, 929 P.2d 596, 60 Cal. Rptr. 2d 277 (1997).

[5]    See N.Y. State Nat’l Org. for Women v. Terry, 886 F.2d 1339, 1362 (2d Cir.), cert. denied, 495 U.S. 1339 (1989) (“We have no doubt that-absent the requested relief-the health and security of a considerable number of persons was and would be endangered by the demonstrations. Accordingly, the district court correctly found that defendants’ activities constituted a public nuisance, and properly granted the City summary judgment on this claim.”); Hirsh v. City of Atlanta, 261 Ga. 22, 401 S.E.2d 530 (1991).

[6] Wilkinson v. Forst, 832 F.2d 1330 (2d Cir. 1987), cert. denied sub nom. Kelly v. Wilkinson, 485 U.S. 1034 (1988) (authorizing magnetometer searches); but see Christian Knights of the Ku Klux Klan Invisible Empire, Inc. v. Dist. of Columbia, 972 F.2d 365 (D.C. Cir. 1992) (identifying First Amendment constraints that might limit injunctions such as those allowed to stand in Wilkinson).

[7] A comment to the former provision indicates that “significant” means “harm of importance, involving more than slight inconvenience or petty annoyance.” Restatement, supra, § 821F, cmt. c, p. 105.

[8] Although this provision speaks explicitly only to liability for damages, the Restatement makes clear that injunctive relief is available in appropriate cases for private nuisances. See, infra, pp. 18–19. It is perhaps for this reason that the authors of Prosser and Keaton on Torts edited out the words “for damages” when they quoted this passage in their treatise. Prosser and Keaton on Torts, 5th Ed., p. 629 (1984).

[9] Comment k, dealing with unintentional invasions, also focuses on risk. Because that note addresses liability based on negligence theories, however, it emphasizes that “it is the risk of harm that makes the conduct unreasonable.” Restatement, supra, § 822, cmt. k, p. 114.

[10] The only reference to anything like an irreparable harm requirement is in Comment b, which includes a statement that:

. . . Other factors, not here listed, may be considered, as for example, that of the sufficiency of the seriousness and imminence of the threat of tort, discussed in § 933(1), Comment b.

Restatement, supra, § 936(1), cmt. b, p.567. This of course, though, merely replicates the analysis necessary in the first place to determine whether there is a qualifying tort.

[11] Black’s Law Dictionary has gone even further in relaxing the likelihood standard, defining the likelihood-of-success-on-the-merits test as requiring only “a reasonable probability of success in the litigation or appeal.” Black’s Law Dictionary 947 (8th ed. 2004); see also AlliedSignal, Inc. v. B.F. Goodrich Co., 183 F.3d 568, 576 (7th Cir. 1999) (applying an unquantified “substantial likelihood of irreparable harm” test in an antitrust case).

[12] Under some environmental statutes, certain harms are seen as being so serious that our laws speak in absolute terms. The most famous example of this is the Endangered Species Act, under which, as this Court has recognized, in barring harm to endangered species or their critical habitat, “Congress has spoken in the plainest of terms, making it abundantly clear that the balance has been struck in favor of affording endangered species the highest of priorities.” Tenn. Valley Auth. v. Hill, 437 U.S. 153, 194 (1978) (applying 16 U.S.C. § 1536(a)). In other contexts, Congress and/or the agencies that implement the relevant statutes have set substantive standards according to what they deem to be acceptable risk ranges given the perceived severity of the potential adverse effects. Under the Comprehensive Environmental Response, Compensation and Liability Act, 42 U.S.C. § 9601, et seq., for example, the Environmental Protection Agency must clean up sites to a degree that reduces the cancer threat to those living nearby to a risk range of between one-in-ten-thousand (1xl0-4) and one-in-a-million (1×10-6), with the latter standard serving as the “point of departure.” 40 C.F.R. § 300.430(e)(2)(i)(A)(2); see also 42 U.S.C. § 9621(b)(1). In the nuclear context, the Nuclear Regulatory Commission’s design requirements for nuclear power plants contemplate that siting decisions control for “design basis events.” These requirements generally ensure that these facilities will not release significant radiation levels during events (such as aircraft accidents) that are found to have more than a one-in-ten-million chance of occurring. See, e.g., 10 C.F.R. §§ 52.17, 52.79, 100.10, 100.20, 100.21; NUREG-0800, Standard Review Plan for the Review of Safety Analysis Reports for Nuclear Power Plants (SRP), Section 3.5.1.6, “Aircraft Hazards” (Rev. 4, Mar. 2010) (ML070510639), at 3.5.1.6-4 (providing that Part 52 and Part 100 regulations are satisfied “if the probability of aircraft accidents resulting in radiological consequences greater than the 10 [C.F.R.] Part 100 exposure guidelines is less than order of magnitude of 10-7 [one in ten million] per year”).

[13] See also United States v. Conservation Chem. Co., 619 F. Supp. 162, 194 (W.D. Mo. 1985) (applying the same standard under § 106 of the Comprehensive Environmental Response, Compensation, and Liability Act, 42 U.S.C. § 9606).

[14] See also Tenn. Valley Auth. v. Hill, 437 U.S. 153 (1978), and United States v. Mass. Water Res. Auth., 256 F.3d 36, 51 n.15 (1st Cir. 2001). Weinberger v. Romero-Barcelo, 456 U.S. 305 (1982), is not to the contrary. Indeed, a careful reading of it supports this position.
In Romero-Barcelo, this Court upheld the district court’s decision not to enjoin the relevant discharges under § 309(b) of the Clean Water Act, 33 U.S.C. § 1319(b). It did so under the equitable-balancing prong of the injunctive-relief calculus, and in a context in which the relevant violation was procedural—the failure to obtain a permit—not substantive. Id. at
312–19. The Court concluded that “the integrity of the Nation’s waters, . . . not the permit process, is the purpose of the [Clean Water Act].” Id. at 314. The Court did not, however, find an absence of irreparable harm, even though it emphasized the lower court’s finding that that the relevant discharges were not causing any measureable harm to the waters. Id. at 310. The Court underscored the limited nature of its pronouncement in its penultimate paragraph:

. . . The District Court did not face a situation in which a permit would very likely not issue, and the requirements and objective of the statute could therefore not be vindicated if discharges were permitted to continue. Should it become clear that no permit will be issued and that compliance with [the Act] will not be forthcoming, the statutory scheme and purpose would require the court to reconsider the balance it has struck.

Id. at 320 (emphasis added).

[15] See Amoco Production Co. v. Village of Gambell, 480 U.S. 531, 545 (1987) (“[E]nvironmental injury, by its nature, can seldom be adequately remedied by money damages and is often permanent or at least of long duration, i.e., irreparable.”).

[16] In a later case, the Court made clear that the presence or absence of harm is not an issue in preclearance cases:

Nor does it matter for the preclearance requirement whether the change works in favor of, works against, or is neutral in its impact upon the ability of minorities to vote. . . . [P]reclearance is a process aimed at preserving the status quo until the Attorney General or the courts have an opportunity to evaluate a proposed change.

Young v. Fordice, 520 U.S. 273, 285 (1993) (internal citations omitted).

[17] See also Sierra Club v. U.S. Army Corps of Eng’rs., 701 F.2d 1011 (2d Cir. 1983) (Corps was poised to fill in a “highly significant and productive habitat” for striped bass in the Hudson River, which was the second most important contributor of those fish in the Atlantic Coast fishery), Found. on Econ. Trends v. Weinberger, 610 F. Supp. 829 (D.D.C. 1985) (finding that the Army had failed to consider “serious and farreaching” risks relating to the use of pathogenic agents and toxins at a test laboratory), and Sierra Club v. Coleman, 405 F. Supp. 53, 55
(D.D.C. 1975)
 (finding that the Federal Highway Administration failed to adequately address the risks of aftosa, which the record revealed could have resulted in the destruction of 25% of North American livestock if not adequately contained).

BLM’s Retained Rights: How Requiring Environmental Protection Fulfills Oil and Gas Lease Obligations

By Bruce M. Pendery *

There are approximately 39,000,000 acres of federal mineral estate in the eleven western states subject to onshore oil and gas leases issued by the Bureau of Land Management (BLM). The leases grant the lessee the right to extract any oil or natural gas that may be found on the lease. However, the leases make the grant of rights “subject to” a number of reservations of authority to the federal government. The BLM lease provides that these retained rights stem from applicable laws; the terms, conditions, and stipulations in the lease; the Secretary of Interior’s regulations and formal orders in effect when the lease is issued; and regulations and formal orders issued afterward if not inconsistent with the lease rights granted. A BLM regulation makes the lease subject to three further reservations of authority: stipulations; restrictions deriving from specific, nondiscretionary statutes; and reasonable measures the BLM authorized officer might require.
A review of these authorities shows BLM retains substantial rights allowing it to regulate the time, place, and manner of oil and gas development. Development can be conditioned by regulating the timing of operations and the siting and design of facilities, as well as specification of the rates of oil and gas development and production. BLM can suspend operation of leases and can even prohibit development if impacts are substantially different or greater than normal. BLM retains the right to prevent “adverse impacts” by requiring “reasonable measures” to prevent environmental harms. These rights stem from provisions in the Mineral Leasing Act, Federal Land Policy and Management Act, National Environmental Policy Act, Endangered Species Act, Clean Air Act, Clean Water Act, National Historic Preservation Act, other statutes, BLM’s leasing and operations regulations, the terms in the lease itself, and formal orders such as BLM Resource Management Plans, Onshore Oil and Gas Order Number 1, Executive Orders, and Secretarial and Department of Interior Solicitor Orders and Opinions, all of which the lease is made “subject to.” If BLM fully exercises these retained rights it can considerably reduce environmental disturbance due to oil and gas development on the public lands. Means available for exercising these retained rights include requiring phased or paced development, directional drilling, suspension of operations on leases in the interest of conservation of resources, unitization of leases, and a number of best management practices, including placing netting over waste pits to reduce wildlife mortality, requiring “closed-loop” drilling fluid systems to reduce pollution, and requiring mats to be placed on the ground during drilling to reduce drilling impacts, to name a few. This Article argues that given the mandatory, nondiscretionary nature of many of the authorities a federal onshore oil and gas lease has been made subject to, not only does BLM have numerous retained rights, it in fact has an obligation to fully assert them, and several policy changes that could accomplish this are suggested.

 

I. Introduction

There are large areas of the public lands in the western United States that are encumbered by federal oil and natural gas leases. In the eleven western states of New Mexico, Colorado, Wyoming, Montana, Idaho, Utah, Arizona, Nevada, California, Oregon, and Washington—where public lands are an important aspect of land use, economic development, and social structure and culture—there were 404,500,000 acres of federal mineral estate, and over 39,000,000 acres of that estate were subject to federal oil and gas leases in fiscal year 2008.[1]

Given the large areas of public land encumbered by federal onshore oil and natural gas leases, a significant question relates to the “retained rights” enjoyed by the federal government in areas it has leased. This Article posits that the federal government has substantial retained rights allowing it to regulate oil and gas development in order to ensure protection of other resources on the lands it has leased. I define the term “retained rights” to mean powers the federal government maintains and has not ceded regarding public lands management when it issues an onshore oil and gas lease to a private party. As will be explained, the government has retained significant rights to protect the natural environment, including, for example, protection of threatened or endangered species, prevention of air and water pollution, the right to regulate operations in order to conserve surface resources, the ability to protect historic trails and other cultural and archeological resources, and the right to prevent unnecessary or undue degradation of the public lands.

With respect to onshore oil and gas leasing, management of the leasing program and the resulting leases is entrusted to the United States Bureau of Land Management (BLM) within the United States Department of Interior.[2] For purposes of this Article, I will focus on the retained rights enjoyed by BLM on the public lands and the mineral estate that it manages in the eleven western states. Because of my knowledge of and experience in the State of Wyoming, many of the examples that will be presented relate to Wyoming.

BLM manages approximately 175,000,000 acres of surface estate in the eleven western states, as well as the above-mentioned mineral estate.[3] I will not specifically consider leasing in Alaska in this Article because some different legal provisions apply there, particularly in the National Petroleum Reserve in Alaska, but generally the analysis presented here also applies to BLM-managed oil and gas in Alaska.[4] While the focus of this Article will be on BLM and the lands it manages, similar lines of reasoning and the conclusions that will be presented here also apply to the over 158,000,000 acres managed by the United States Forest Service (Forest Service) in the eleven western states because similar leasing rules apply on those lands.[5] For purposes of this Article, I only consider federal onshore oil and gas leasing and leases. I will not consider offshore leasing managed by the Minerals Management Service under the direction of the Outer Continental Shelf Leasing Act.[6]

In the following sections, I will first describe the Mineral Leasing Act[7] and the onshore oil and gas leasing system it created. I will then discuss the terms and conditions of BLM onshore oil and gas leases with an eye toward what those provisions mean relative to BLM’s retained rights. Following that is a discussion of the retained rights BLM enjoys under applicable laws, lease terms and conditions, regulations, and other authorities a BLM oil and gas lease is made “subject to.” Then I will consider general doctrines of contract law that may also help define BLM’s retained rights. Following that is a discussion of issues that might limit BLM’s exercise of its retained rights, such as Fifth Amendment takings claims. Last, I will consider means by which BLM could exercise its retained rights and policy changes it could make, and then argue that not only does BLM enjoy substantial retained rights, it also has an obligation to assert them.

II. Overview of the Mineral Leasing Act

Onshore leasing of federally owned oil and gas is governed by the Mineral Leasing Act of 1920.[8] The leasing system it established, including provision for royalties to be paid on produced minerals, represented a marked departure from the provisions under the General Mining Law of 1872,[9] where minerals and the exclusive right to possession of the land were granted to the first prospector able to “locate[]” a “valuable” mineral on public lands.[10] The leasing system established by the Mineral Leasing Act for many nonmetalliferous minerals provides for a significant increase in governmental control and regulation of mineral disposition and development compared to the self-initiated system under the General Mining Law that applies to hardrock minerals such as “gold, silver, cinnabar, lead, tin,
[and] copper.”[11]

Subject to enumerated exceptions, the Mineral Leasing Act provides that deposits of coal, phosphate, sodium, potassium, oil, oil shale, gilsonite, or gas, and lands containing such deposits that are owned by the United States, “shall be subject to disposition in the form and manner provided by this chapter.”[12] The Act establishes qualifications for holding an oil and gas lease, establishes limits on the aggregate acreage of lease holdings, allows for cancellation and forfeiture of leases, allows for necessary rules and regulations to be prescribed, provides for royalties and other income to the government and disposition of the moneys received, prescribes the maximum size of individual leases and lease term lengths, and makes many other provisions.[13]

Most significantly for purposes of this Article, section 17 of the Mineral Leasing Act provides for leasing of oil and gas. Section 17(a) declares that “[a]ll lands subject to disposition under this [Act] which are known or believed to contain oil or gas deposits may be leased by the Secretary [of the Interior].”[14] Section 17(b) then provides for a competitive leasing system via oral auction where parcels are leased to the “highest responsible qualified bidder.”[15] If no qualified bids are received at competitive auction, lease parcels become available for sale noncompetitively.[16] Under the provisions for noncompetitive leases, “the person first making application for the lease who is qualified to hold a lease under this [Act] shall be entitled to a lease of such lands without competitive bidding.”[17] In addition to specifying the leasing system, section 17 also makes several provisions related to environmental protection.[18]

This system where leases are first offered at competitive auction before becoming available for noncompetitive sale is relatively new. It was established on December 22, 1987, when the Federal Onshore Oil and Gas Leasing Reform Act (FOOGLRA)[19] was enacted. This law is codified in several sections of the Mineral Leasing Act and elsewhere, but the most important amendments for purposes of this review were the amendments to subsections 17(b) through 17(h), which deal with the leasing provisions that have been mentioned and environmental protection measures that will be described in more detail below.[20] Prior to FOOGLRA a different leasing system existed.

Under the pre-FOOGLRA system, competitive leasing only occurred if a lease was in a “known geologic structure” (KGS).[21] Otherwise, if the lands were not in a KGS, a lease could be acquired on a noncompetitive basis.[22] The noncompetitive system allowed for two ways to acquire a lease.
The first was an over-the-counter purchase based on a first-come, first-served system.[23] The second was based on a lottery system called “SIMO.”[24]
Over-the-counter leases were available if the land was not in a KGS, had never been leased, and the lands had not received bids in the lottery system.[25] The lottery system was utilized for lands not in a KGS but where the lands had been previously leased.[26]

This pre-FOOGLRA leasing system turned out to have a number of problems. BLM had difficulty defining KGSs, which lead to uncertainty and abuse, and outright fraud and speculation occurred in the noncompetitive lottery system.[27] It was these problems that led to the enactment of FOOGLRA and the creation of the modern leasing system where competitive leasing is the general rule and noncompetitive leasing only occurs when a qualified bid is not received at a competitive lease sale.[28] The pre-FOOGLRA leasing system, problems that developed under it, and the resulting enactment of FOOGLRA are ably described in three law review articles[29] and in the leading case of Arkla Exploration Co. v. Texas Oil & Gas Corp.[30]

The significance of the pre-FOOGLRA versus post-FOOGLRA leasing systems is that oil and gas leases have been issued under two distinctly different systems, one in existence before 1987 and one after. However, according to officials with BLM there have been no differences in the terms of a competitive versus a noncompetitive lease, whether issued pre- or post-FOOGLRA.[31] There has been only one lease form in use at any particular time.[32] Thus, when the provisions of BLM leases in use during different time periods are discussed below in an effort to discern BLM’s retained rights, there will be no need to distinguish between competitive- and noncompetitive-issued leases, or—for purposes of ascertaining BLM’s retained rights—a need to distinguish between pre- versus post-FOOGLRA leases.[33]

III. The Federal Onshore Oil and Gas Leasing and Development Process

A. The Stages of BLM Oil and Gas Planning, Leasing, and Development

The BLM onshore oil and gas leasing and development process for federally owned oil and gas is comprised of five steps or stages. These include land-use planning, leasing, exploration, full field development, and filing an application for permit to drill (APD).[34]

1. Land-Use Planning

Step one is land-use planning, the development of BLM Resource Management Plans (RMPs). BLM land-use planning is required under the Federal Land Policy and Management Act (FLPMA).[35] At this stage, lands that will be available for oil and gas leasing are identified, and limitations that will be applied to leasing, including applicable stipulations, are specified.[36] In Wyoming, there are ten BLM field offices and each has an RMP in place.[37] Other western states also have a number of field offices and most operate under the guidance of an RMP.[38] Under many of the RMPs in Wyoming, much of the land under the direction of the field office is available for oil and gas leasing, and this is generally true elsewhere in the West.[39] The development of an RMP requires compliance with the National Environmental Policy Act (NEPA)[40] and is therefore accompanied by preparation of an environmental impact statement (EIS).[41]

2. Leasing

The next stage in the oil and gas leasing and development process on BLM lands and mineral estates is the leasing stage. At this stage leases are first offered for sale at competitive auctions and then are available noncompetitively if a qualified bid is not received at the competitive sale.[42] After an acceptable offer is received, and assuming there are no protests that delay the leasing process, a lease is issued.[43] As has been recognized in numerous court and administrative decisions, the leasing stage is crucial because it represents an “‘irreversible and irretrievable commitment[] of resources’” due to the developed rights granted by a federal onshore oil and gas lease, and thus compliance with NEPA is required prior to issuing a lease, at least when the lease does not contain a stipulation specifying there will be no surface occupancy of the leasehold.[44] This issue will be discussed in more detail in Part VII.D.

3. Exploration

Once an oil and gas lease is issued, the next step is often exploration to determine if there are likely to be valuable oil and gas deposits on a lease. BLM has developed regulations that govern exploration, and exploration projects are also subject to NEPA.[45] In general, at least in Wyoming, exploration projects are approved by preparation of a NEPA environmental assessment (EA), not a more detailed EIS.[46] Sometimes a leaseholder does not engage in exploration and proceeds directly to drilling a “wildcat” well, so called because the well is drilled in an area where the potential for production in paying quantities is uncertain.[47]

4. Full-Field Development

If it becomes apparent that oil and gas may be present in an area and that a number of wells are likely to be drilled, the process enters what is called the project level stage. This stage is also sometimes called the
“full-field development” stage.[48] NEPA applies to this level of activity because of the BLM approvals required before development can occur, and often an EIS is prepared (sometimes an EA is prepared for smaller fields or drilling projects).[49] There have been a number of full-field development EISs prepared in Wyoming in recent years, including, but by no means limited to, analyses of the Jonah Infill project, the Pinedale Anticline project, the Atlantic Rim project, and coal bed methane development in the Powder River Basin; these EISs can be reviewed on BLM field office websites.[50] Approval of these projects through the “record of decision” that accompanies an EIS can allow for the drilling of thousands of wells.[51] Similar full field development EISs in environmentally significant areas have been developed in several of the other western states in recent years, such as the Roan Plateau project in western Colorado.[52]

5. Application for Permit to Drill

Finally, the last stage in the oil and gas development process on BLM lands and mineral estates is called the APD stage. Under BLM’s regulations, no well can be drilled until an APD has been approved.[53] Up until now, no actual surface disturbance has occurred (other than the relatively limited disturbance associated with exploration), but after the APD stage, drills can begin to dig into the ground.[54] The APD stage also implicates NEPA, and in many cases an EA is prepared as part of the APD approval to ensure environmental concerns are considered and mitigated on a site-specific basis.[55] However, since passage of the Energy Policy Act of 2005,[56] “categorical exclusions” from NEPA compliance at the APD stage have been available in many cases, and NEPA compliance at the APD stage has been made less rigorous.[57] In addition to complying with NEPA, the Mineral Leasing Act provides that when an APD is filed, BLM must provide notice to the public of the proposed action.[58]

The outcome of this multistage oil and gas leasing and development process can be substantial environmental disturbance, such as the thousands of wells that have been planned and drilled in Wyoming’s Pinedale Anticline and Jonah fields, and in the Powder River Basin.[59] Similar levels of activity are apparent in other parts of the West, such as in the Farmington area in New Mexico, the Piceance Basin in Colorado, the Uinta Basin in Utah, and in Montana’s portion of the Powder River Basin.[60] It is this Article’s premise that to prevent substantial environmental harm in these and many other environmentally significant areas, it is crucial that BLM recognize the retained rights it still enjoys despite having issued an oil and gas lease and regulate this development accordingly.

B. The BLM Onshore Oil and Gas Leasing Process

Numerous provisions that govern oil and gas leasing can be found in the Mineral Leasing Act and in BLM’s oil and gas leasing regulations.[61]
For purposes of this Article it is not necessary to provide a detailed discussion of the leasing process, but some relevant provisions will be mentioned in this section. A user-friendly description of the leasing process can be found on the BLM website.[62] Information on particular lease sales can be found on BLM state office web pages.[63]

As mentioned, there are two means by which BLM can offer onshore oil and gas leases. Leases must first be made available for sale at a competitive oil and gas auction, which are held at least quarterly.[64] If no legally sufficient bids are received at the competitive sale, BLM can then make the leases available on a noncompetitive basis.[65] Leases not sold at a competitive oil and gas lease sale remain available for noncompetitive leasing for a period of two years after the competitive lease sale.[66]

The maximum size of a competitive lease parcel is 2560 acres (different limits apply in Alaska) and the maximum size of a noncompetitive parcel is 10,240 acres.[67] The primary term of a lease is for ten years and the lease will automatically continue in force so long as there is at least one well on the lease capable of producing oil and gas in paying quantities, or the lease has been committed to a “unitized” group of leases that have at least one well capable of producing in paying quantities.[68] A lease term can be extended for two years if actual drilling is being diligently prosecuted prior to the end of the primary term.[69]

The annual rental on a lease is $1.50 per acre, or fraction thereof, for the first five years of the lease and $2.00 per acre thereafter.[70] Royalties on production must be paid at a rate of 12.5% of the value of production removed.[71] Royalties and other monies received are paid to the United States Department of the Treasury, with fifty percent of that returned to the state where the oil or gas was produced.[72] In addition to rent and royalties, bonding is required prior to conducting surface disturbing activities to ensure compliance with lease terms and reclamation and restoration of impacted lands.[73] Bonding must be in an amount not less than $10,000 per lease or, in lieu of that, statewide bonds of $25,000 or nationwide bonds of $150,000 can be posted.[74]

Generally, BLM will issue a lease to a successful bidder after it receives the bid form and all money due.[75] A lease is effective the first day of the month following the month in which BLM signs the lease, although there are provisions allowing for the lease to be effective sooner.[76] However, the public can protest the sale of leases.[77] If this is done—and BLM often receives protests of lease parcels offered for sale at auction—the lease will not be issued until the protest is resolved, which often takes several months.[78] If the protest is rejected, BLM can issue the lease.[79] If a protest is upheld, the lease parcel will be withdrawn and fees, rentals, and bonus bids will be returned to the bidder.[80] However, a BLM decision to reject a protest is subject to appeal to the Interior Board of Land Appeals (IBLA).[81]

A BLM oil and gas lease issued as a result of this leasing process is made subject to a number of provisions and it also contains a number of terms. The next Part of this Article will discuss these terms and how they create an array of retained rights for BLM, allowing it to regulate oil and gas development in order to protect the natural environment.

IV. The Terms and Conditions of BLM Onshore Oil and Gas Leases

The place to start in determining what rights BLM retains when it issues an onshore oil and gas lease is with the lease itself, the contractual agreement the government enters into when it issues a lease to a private party. BLM’s current regulations provide that “[a] lease shall be issued only on the standard form approved by the Director [of BLM].”[82]

A. Versions of the BLM Oil and Gas Lease Form

Over the years since the Mineral Leasing Act was enacted in 1920, BLM has used several lease forms to issue leases under the pre-FOOGLRA and post-FOOGLRA leasing frameworks. Currently, BLM leases are presented on Form 3100-11, the “Offer to Lease and Lease for Oil and Gas.”[83] Based on information received from BLM’s Forms Manager in Denver, five versions of Form 3100-11 were used between 1984 and 2006.[84] There were no earlier versions of the form on file. The earliest version of Form 3100-11 is dated March 1984.[85] Later versions dated June 1988, October 1992, February 2003, and July 2006 were also on file.[86] In October 2008, BLM adopted a further revision to Form 3100-11, and this is now the most recent version of the standard lease form.[87] Thus, six versions of Form 3100-11 may apply to leases in existence today.

Despite the lack of earlier versions of the lease form that are on file in the BLM archives, upon request I received three examples of earlier leases from the BLM Wyoming state office.[88] These leases were issued in 1954, 1965, and 1971.[89] This sampling of older lease forms coupled with the six archived versions of Form 3100-11 likely constitute a reasonably complete picture of lease forms that have been used over the years, allowing an analysis of what rights have been retained by BLM when it issues an oil and gas lease.
The nine lease forms considered in this Article are on file with the author and are available upon request. In addition, the version of Form 3100-11 currently in use—the October 2008 form—is available via the hyperlink referenced in footnote 83.

 

Table 1: Number of Currently Active Federal Oil and Gas Leases in the Eleven Western States Issued During the Indicated Time Period when Various BLM Oil and Gas Lease Forms Were in Effect or
Presumed to Have Been in Effect
[90]

 

Date Lease Form Was Made Effective

Period of Time Lease Form Was in Effect or
Is Presumed to
Have Been in Effect

Number of Still-Active Leases in the Eleven Western States Issued During This Time Period

September 1953

1920–1954[91]

4383

August 1961

1955–1965[92]

1948

May 1968

1966–February 1984[93]

6755

March 1984

March 1984–May 1988[94]

889

June 1988

June 1988–September 1992

1113

October 1992

October 1992–January 2003

11,442

February 2003

February 2003–June 2006

13,819

July 2006

July 2006–September 2008

6469

October 2008

October 2008–Present

1524

TOTAL

48,342

 

Working from these lease forms, I have assessed the number of leases that are currently active in the eleven western states that were issued in the time periods when the various versions of the leases were in effect or when it is presumed the lease forms were in effect—i.e., the 1954, 1965, and 1971 lease examples have presumed periods of effectiveness; the period when a lease form was in effect is certain with respect to the six 3100-11 forms that have been archived since 1984. Table 1 presents the results of this analysis.[95]

Knowing how many still-active leases were issued during the time periods when each version of the lease was in effect or is presumed to have been in effect allows an analysis of what terms and conditions of a lease were effective at various times and thus allows consideration of what rights have been retained by BLM. While the varying periods when different lease forms were in effect or presumed to have been in effect makes it impossible to discern if there were periods of time when greater rates of leasing were occurring, it is apparent the majority of currently active leases were issued since 1984 when the best records of operative lease forms are available.

B. The Terms of Federal Onshore Oil and Gas Leases

The nine lease forms all start from the proposition that the federal government is granting the lessee the exclusive right to fully develop any oil and gas that may be found on the leasehold and that any necessary facilities that are required to extract the oil and gas can be constructed.[96] The 1954 lease states,

The lessee is granted the exclusive right and privilege to drill for, mine, extract, remove, and dispose of all the oil and gas deposits, except helium gas, in the lands leased, together with the right to construct and maintain thereupon, all . . . structures necessary to the full enjoyment thereof.[97]

The 1965 and 1971 leases make the same provision.[98] Beginning with the March 1984 lease form it is stated that “[t]his lease is issued granting the exclusive right to drill for, mine, extract, remove and dispose of all the oil and gas (except helium) in the lands described . . . together with the right to build and maintain necessary improvements thereupon.”[99] This same language is contained in the June 1988, October 1992, February 2003,
July 2006, and October 2008 lease forms.[100]

But in all of these lease forms the government also retains a number of rights allowing it to condition development so as to protect the environment. In the 1954 lease form, the lease is made “subject to” the provisions of the Mineral Leasing Act and reasonable regulations not inconsistent with the terms of the lease and the provisions in the lease.[101] The lessee agrees to a number of terms and the lessor reserves several rights. The lessee agrees “[t]o take such reasonable steps as may be needed to prevent operations from unnecessarily” causing or contributing to soil erosion or damaging forage or timber growth, polluting waters, damaging crops, or damaging range improvements.[102] It is also agreed that upon conclusion of operations the lessee will restore the surface to its former condition, and the lessor is permitted to prescribe the steps and restoration to be made.[103] The lessee further agrees that rental and royalty suspension may occur if the Secretary of the Interior finds such is necessary “for the purpose of encouraging the greatest ultimate recovery of oil or gas and in the interest of conservation of natural resources.”[104] Moreover, the lessee agrees to “plug properly and effectively all wells . . . before abandoning the same.”[105] Perhaps most significantly, it is agreed in section 4 of the 1954 lease

that the rate of prospecting and developing and the quantity and rate of production from the lands covered by this lease shall be subject to control in the public interest by the Secretary of the Interior, and in the exercise of his judgment the Secretary may take into consideration, among other things, Federal laws, State laws, and regulations issued thereunder.[106]

The lessor also reserved the right to dispose of the surface of the leased lands if not necessary for the extraction of the oil and gas and the right “to dispose of any resource in such lands” if it would not “unreasonably interfere” with lease operations.[107]

The 1965 lease provides that the lease is subject to the same conditions, that the lessee agrees to the same provisions, and that lessor has the same reserved rights.[108] The 1971 lease, too, makes these provisions, but the agreement to not unnecessarily damage enumerated natural resources is expanded to include agreeing not to pollute the air as well as water, and to protecting fossil, historic, or prehistoric resources and other antiquities that are found.[109]

Beginning with the March 1984 lease form, the form takes on what might be called its modern form, and it will be referred to as such henceforth.[110] Many of the provisions in the 1954, 1965, and 1971 leases are continued, but often in somewhat modified form. In this modern form, following the statement of what the lease grants—the exclusive right to extract all of the oil and gas on a leasehold—there immediately follows a statement of what the lease is made “subject to.” The lease states,

Rights granted are subject to applicable laws, the terms, conditions, and attached stipulations of this lease, the Secretary of the Interior’s regulations and formal orders in effect as of lease issuance, and to regulations and formal orders hereafter promulgated when not inconsistent with lease rights granted or specific provisions of this lease.[111]

This same statement is made in the June 1988, October 1992,
February 2003, July 2006, and October 2008 lease forms.[112]

There are several relevant lease terms in the modern lease form that the rights granted to the lessee are made subject to. In section 2 the provision allowing suspension of royalties is maintained. But now, rather than being available “for the purpose of encouraging the greatest ultimate recovery of oil or gas and in the interest of conservation of natural resources,”[113] this action can be taken when necessary “to encourage the greatest ultimate recovery of the leased resources, or [as] is otherwise justified.”[114]
The agreement to allow the Secretary of the Interior to specify the rate of development is maintained but is slightly modified in section 4 of the modern lease forms: “Lessor reserves right to specify rates of development and production in the public interest . . . if deemed necessary for proper development and operation of area, field, or pool embracing these leased lands.”[115] In section 7 of the modern lease forms it is stated that if the impacts from mining “would be substantially different or greater” than normal, “lessor reserves the right to deny approval of such operations.”[116] And in section 12 it is provided that when the leased lands are returned to the lessor, the lessee will reclaim the land as specified by the lessor and remove equipment and improvements not deemed necessary by the lessor for the preservation of producible wells.[117] These same provisions are made in all of the modern lease forms.

But the most significant term in the modern lease forms relative to retained rights allowing protection of the natural environment is section 6 of the lease form. In the March 1984, June 1988, October 1992, and February 2003 forms, this term provides the following:

Lessee shall conduct operations in a manner that minimizes adverse impacts to the land, air, and water, to cultural, biological, visual, and other resources, and to other land uses or users. Lessee shall take reasonable measures deemed necessary by lessor to accomplish the intent of this section. To the extent consistent with lease rights granted, such measures may include, but are not limited to, modification to siting or design of facilities, timing of operations, and specification of interim and final reclamation measures. Lessor reserves the right to continue existing uses and to authorize future uses upon or in the leased lands, including the approval of easements or rights-of-way. Such uses shall be conditioned so as to prevent unnecessary or unreasonable interference with rights of lessee.[118]

Section 6 goes on to provide that prior to any surface disturbance, “lessee shall contact lessor to be apprised of procedures to be followed
and modifications or reclamation measures that may be necessary.”[119]
This section allows for inventories and studies “to determine the extent of impacts to other resources,” although these apparently are limited to “minor inventories” or “short term special studies.”[120] Section 6 concludes by requiring that if during the conduct of operations “threatened or endangered species, objects of historic or scientific interest, or substantial unanticipated environmental effects are observed, lessee shall immediately contact the lessor” and “shall cease any operations that would result in the destruction of such species or objects.”[121] As indicated, these provisions appeared in the March 1984 through February 2003 lease forms; however, the July 2006 and October 2008 lease forms changed the language in Section 6.[122]

In the July 2006 and October 2008 versions of the lease, where previously the word “shall” had been used in section 6 it was replaced with the word “must.”[123] So, for example, the prior requirement that lessee “shall” conduct operations so as to minimize adverse impacts was changed to a requirement that lessee “must” conduct operations to minimize such impacts.[124] And the former requirement that lessee “shall” take reasonable measures deemed necessary by lessor to accomplish this intent was replaced with a statement that lessee “must” take reasonable measures so as to accomplish the intent of minimizing adverse impacts.[125]

The significance of this wording change may be debatable but is probably minimal. In construing the word shall, the United States Supreme Court offered that “[t]hough ‘shall’ generally means ‘must,’” the use, or misuse, of the word “shall” was apparent in the usage of some legal writers because they posited less-than-mandatory definitions of “shall.”[126] “Must” means to “be obliged or required by morality, law, or custom,”[127] and “shall” means something that will take place or exist in the future or an order, promise, requirement, or obligation.[128] Black’s Law Dictionary states that “must,” “like the word ‘shall,’ is primarily of mandatory effect,”[129] and that shall “is generally imperative or mandatory.”[130] It goes on to state that “shall” “in ordinary usage means ‘must’ and is inconsistent with a concept of discretion.”[131] Standard works presenting the meaning of words as construed by the courts also indicate that “shall” and “must” are generally construed in a mandatory light.[132]

It is apparent from the nine versions of the lease reviewed that BLM has retained substantial rights allowing it to protect the natural environment despite having granted lessees a right to develop the oil and gas that might be found on a lease. The leases issued prior to 1984 appear to retain somewhat fewer or lesser rights than those issued after 1984, but even in these earlier leases the lessee agreed “[t]o take such reasonable steps” as are needed to prevent certain categories of resource damage.[133] And probably most significantly it was agreed by BLM and the lessee

that the rate of prospecting and developing and the quantity and rate of production . . . shall be subject to control in the public interest by the Secretary of the Interior, and in the exercise of his judgment the Secretary may take into consideration, among other things, Federal laws, State laws, and regulations issued thereunder.[134]

After March 1984, section 6 of the lease form required that in the conduct of operations, the lessee was required to minimize adverse impacts to a number of resources and specified that reasonable measures deemed necessary by lessor could be specified to ensure this was accomplished, so long as consistent with the lease rights granted.[135] These reasonable measures could include, but were not limited to, modifications to the siting or design of facilities, timing of operations, and the specification of interim and final reclamation measures.[136] The modern lease forms continued to specify that the “[l]essor reserves the right to specify rates of development and production in the public interest.”[137] In the modern leases, the entire lease is made “subject to” applicable laws; the terms, conditions, and stipulations of the lease; the regulations and formal orders that are in place when the lease is issued; and later-adopted regulations and formal orders, if not inconsistent with the lease rights granted.[138] So again, all lease forms have retained a number of rights to the government that allow it to substantially protect the natural environment despite having issued a lease that grants the “exclusive right” to remove all of the oil and gas that might be found on a leasehold.

C. BLM’s 43 C.F.R. § 3101.1-2 Regulation

Another important determinant of what rights and limitations have been created under a BLM onshore oil and gas lease besides the terms and conditions in the standard lease form are the provisions in the BLM leasing regulation found at 43 C.F.R. § 3101.1-2.[139] In this Part I will first present the language of the § 3101.1-2 regulation, then discuss its “reasonable measures” provision which mirrors that in section 6 of the modern lease form, and follow that with a consideration of further BLM guidance interpreting the § 3101.1-2 regulation.

1. The Provisions of the § 3101.1-2 Regulation

This regulation in its current form was promulgated on May 16, 1988.[140] Consequently, this regulation would not specifically or necessarily have been made applicable to leases issued prior to May 1988. But, as Table 1 shows, only twenty-nine percent of the leases that are currently in effect in the eleven western states were issued before this regulation was promulgated and seventy-one percent were issued after its adoption. The regulation provides in full that

[a] lessee shall have the right to use so much of the leased lands as is necessary to explore for, drill for, mine, extract, remove and dispose of all the leased resource in a leasehold subject to: Stipulations attached to the lease; restrictions deriving from specific, nondiscretionary statutes; and such reasonable measures as may be required by the authorized officer to minimize adverse impacts to other resource values, land uses or users not addressed in the lease stipulations at the time operations are proposed. To the extent consistent with lease rights granted, such reasonable measures may include, but are not limited to, modification to siting or design of facilities, timing of operations, and specification of interim and final reclamation measures.
At a minimum, measures shall be deemed consistent with lease rights granted provided that they do not: require relocation of proposed operations by more than 200 meters; require that operations be sited off the leasehold; or
prohibit new surface disturbing operations for a period in excess of 60 days in
any lease year.[141]

In addition, BLM’s regulations define the term “operating right,” which is “the interest created out of a lease authorizing the holder of that right to enter upon the leased lands to conduct drilling and related operations, including production of oil or gas from such lands in accordance with the terms of the lease.”[142]

2. Reasonable Measures

In addition to making a lease subject to stipulations and specific, nondiscretionary statutes, issues that will be addressed below,[143] the § 3101.1-2 regulation provides that “reasonable measures” may be required so as to minimize adverse impacts to the environment and other resources.[144] So long as consistent with the lease rights granted, these reasonable measures may include, “but are not limited to,” modification to siting and design of facilities, timing of operations, and specification of reclamation measures.[145] Given that modern versions of the lease form make these same provisions in section 6, it seems unlikely that “reasonable measures” that might be demanded would be inconsistent with the lease rights granted, so long as any oil and gas can still be extracted. And the term in older leases specifying that the rate of prospecting and development is subject to control “in the public interest” does not indicate that reasonable measures could not be required of operations on these older leases as well.

The provisions in the § 3101.1-2 regulation and section 6 of the modern lease appear to be complimentary and should be read together. However, the § 3101.1-2 regulation may attempt to shrink the potential scope of reasonable measures by providing that

[a]t a minimum, [reasonable] measures shall be deemed consistent with lease rights granted provided that they do not: require relocation of proposed operations by more than 200 meters; require that operations be sited off the leasehold; or prohibit new surface disturbing operations for a period in excess of 60 days in any lease year.[146]

This provision, often called the “200-meter 60-day rule,” is sometimes cited as a limit to BLM’s ability to condition development. BLM or lessees sometimes claim that, in the absence of a stipulation or specific, nondiscretionary statute, the only “reasonable measures” that can be imposed are those in compliance with the 200-meter 60-day “rule.”[147]
This restricted view of the regulation is unwarranted.

For one thing, the regulation is specific that these limited measures, which have been defined as consistent with the lease rights granted and thus are “reasonable,” are “a minimum” of what is consistent with lease rights.[148] Moreover, the final rulemaking, which addressed comments in response to the proposed rule about the definition of “reasonable measures,” clarifies the meaning of “reasonable” in the context of the § 3101.1-2 regulation.[149]
BLM stated, “The final rulemaking provides that the Bureau, at a minimum, can require relocation of proposed operations by 200 meters and can prohibit new surface disturbance for a period of 60 days, and that such requirements are consistent with the lease rights granted.”[150] BLM then stated that “the authority of the Bureau to prescribe ‘reasonable,’ but more stringent, protection measures is not affected by the final rulemaking.”[151]

Quite simply, the 200-meter 60-day rule establishes a floor, not a ceiling, as to the reasonable measures BLM may require. The specific terms in section 6 of the standard lease form certainly do not limit BLM’s authority to just require reasonable measures that comply with the 200-meter 60-day rule, which the lease contract does not even mention. It may be worth noting that the modern version of the lease form—specifically the March 1984 version—predated the § 3101.1-2 regulation by at least four years, so BLM certainly developed the May 1988 § 3101.1-2 regulation in recognition of the existing provisions in its lease form that were in use at the time, namely those in section 6, which do not limit reasonable measures to just those stated in the 200-meter 60-day rule.[152]

In considering supplemental mitigation measures required by BLM to protect the greater sage-grouse (Centrocercus urophasianus), the Interior Board of Land Appeals (IBLA) rejected an interpretation of the § 3101.1-2 regulation that would not allow reasonable measures beyond those mentioned in the 200-meter 60-day rule.[153] It stated, “[This] constrained interpretation of a ‘reasonable measure’ is at odds with the plain language of the regulation, which describes what measures ‘at a minimum’ are deemed consistent with lease rights, and does not purport to prohibit as unreasonable per se measures that are more stringent.”[154] What is reasonable should be determined by what is needed to minimize adverse impacts while still allowing access to any oil and gas, not the predetermined minimum limits mentioned in the 200-meter 60-day rule.

3. Further BLM Guidance on the § 3101.1-2 Regulation

After issuing the § 3101.1-2 regulation, BLM determined there was potential for confusion and disagreement about how the § 3101.1-2 regulation should be interpreted. In an Instruction Memorandum (IM) issued on December 3, 1991, BLM attempted to clarify the requirements of the § 3101.1-2 regulation.[155] Using the term “reserved authority,” BLM stated that “[w]ithin this . . . authority, the BLM may impose additional mitigation measures [beyond stipulations] to ensure that proposed operations minimize adverse impacts to other resources” so long as consistent with lease rights granted.[156] More specifically, BLM determined that the requirement in the Federal Land Policy and Management Act of 1976 for BLM to “take any action necessary to prevent unnecessary or undue degradation of the [public] lands”[157] served as a basis to require reasonable measures in excess of the 200-meter 60-day rule.[158] Approaching imposition of reasonable measures through use of this FLPMA standard was seen as placing
“the resolution of this issue clearly within the concept of striking the best multiple use balance.”[159] However, BLM then went on to narrow the application of this FLPMA statutory standard by imposing a requirement that the need for any reasonable measures required to comply with the unnecessary or undue degradation clause must be “clearly and convincingly documented” based on a site-specific analysis.[160]

Under the terms of IM 92-67, its provisions were to be incorporated into BLM Manual MS-3101, and BLM has done this.[161] The manual generally restates the language from the IM, providing that, among other things, “[t]he clear evidence and convincing need” for conditions of approval must be demonstrated on a site-specific basis.[162] And, as was true in the IM, this requirement was focused on providing for compliance with FLPMA unnecessary or undue degradation clause, not any other statutory requirements.

The requirement for clear and convincing evidence made in the IM and the BLM manual creates an unwarranted hurdle for BLM’s exercise of its authority to require reasonable measures. The § 3101.1-2 regulation states that the basis for imposing reasonable measures is “to minimize adverse impacts to other resource values.”[163] This language is directly comparable to the language in section 6 of the standard lease form, which provides that the lessee shall (or must) conduct operations so as to minimize adverse impacts.[164] Moreover, the § 3101.1-2 regulation and section 6 of the lease form recognize modifications to facility siting and design and timing of operations are means to accomplish these reasonable measures, but options “are not limited to” these measures.[165] The § 3101.1-2 regulation also explicitly states that the enumerated 200-meter 60-day rule provisions are “[a]t a minimum” of what is consistent with the lease rights. In the final rule adopting the § 3101.1-2 regulation, BLM stated, “[T]he authority of the Bureau to prescribe ‘reasonable,’ but more stringent, protection measures is not affected by the final rulemaking.”[166] Nowhere, other than in the IM and manual, is it indicated that the basis for imposing a reasonable measure that exceeds the 200-meter 60-day rule is found only in assuring compliance with the unnecessary or undue degradation clause of the FLPMA, and more importantly there is no indication the standard of proof should be the heightened clear and convincing evidence test specified in the IM and manual.

IBLA recently recognized BLM’s rights to condition postlease development pursuant to the § 3101.1-2 regulation and the unnecessary or undue degradation clause, holding that BLM could require post-lease conditions of approval that were not addressed in lease stipulations to protect sage-grouse.[167] IBLA determined that a claim that conditions of approval were limited to no more than the limits in the 200-meter 60-day rule was unsupported by the § 3101.1-2 regulation and that more stringent limitations were not inconsistent with lease rights.[168] In reaching this conclusion, IBLA did not mention any need for clear and convincing evidence to support BLM’s decision to require more stringent mitigation to protect the sage-grouse.[169] Accordingly, there is no underlying basis for requiring clear and convincing evidence before a reasonable measure can be required.[170]

D. Summary of Rights Granted and Rights Retained Under the Modern Lease Form and the § 3101.1-2 Regulation

The § 3101.1-2 regulation expands on or elaborates on the rights that have been granted pursuant to a BLM oil and gas lease and provides further definition of what rights have been retained by BLM. If read with the provisions in the modern version of the standard lease form, it is apparent that three rights are granted pursuant to a BLM onshore oil and gas lease: 1) an “exclusive right” to remove all of the oil and gas on the leasehold;[171] 2) the right to “use” as much of the leasehold as is “necessary” to recover all of the leased resource;[172] and 3) the right to build and maintain “necessary” improvements to extract the leased resource.[173] Thus, the lessee has a right to exclude others from developing the lease during his removal of all of the oil and gas that might be found on the lease, a right to use no more of the lease than is “necessary” to retrieve all of the leased oil and gas, and a right to build only “necessary” improvements. Lessees have not been granted a right to develop the oil and gas in exactly the place they desire, the manner they desire, or on the exact timeline they may desire.

Conversely, when the § 3101.1-2 regulation is considered with the terms and conditions in the standard lease form operative since 1984, it is apparent BLM has retained a number of rights allowing it to limit or condition development. Under the modern versions of the standard lease form in effect since 1984 and the § 3101.1-2 regulation in effect since 1988, BLM has made development of the lease and removal of any oil and gas “subject to” a number of provisions that allow BLM to condition development, including the following:

  • Applicable laws;[174]
  • Terms, conditions, and stipulations in the lease;[175]
  • Regulations and formal orders in effect when the lease is issued;[176]
  • Regulations and formal orders issued afterward, if not inconsistent with lease rights granted and specific provisions in the lease;[177]
  • Specific, nondiscretionary statutes;[178] and
  • Reasonable measures.[179]

This constellation of rights granted and rights retained that are stated in the lease contract and in the regulatory provision largely define the scope and nature of BLM’s retained rights. As will be discussed next, these rights allow BLM to substantially protect the natural environment when oil and gas development is proposed on an onshore oil and gas lease.

V. BLM’s Retained Rights Under a Federal Onshore Oil and Gas Lease

Under the terms of the modern lease form and the 43 C.F.R. § 3101.1-2 regulation, BLM retains several rights because the lease is made “subject to” these reservations of authority. The lease rights granted are subject to: applicable laws; terms, conditions, and stipulations of the lease; regulations and formal orders in effect when the lease is issued; regulations and formal orders issued afterward, if not inconsistent with lease rights granted or provisions in the lease; stipulations attached to the lease; specific, nondiscretionary statutes; and reasonable measures that BLM might require.[180] While older leases may not as clearly have been made subject to these conditions, the rights granted in those leases are also conditioned to a significant degree.

In this Part, after a brief review of the Supreme Court’s view of the rights retained under a federal onshore oil and gas lease, I will review each of the conditions on the right to develop oil and gas. Based on this review, it will be clear BLM has very substantial retained rights that allow it to regulate oil and gas development so as to protect the natural environment.

A. The Supreme Court’s View of the Rights Granted and Rights Retained Under a Federal Onshore Oil and Gas Lease

The scope of retained rights under a federal onshore oil and gas lease was outlined many years ago by the Supreme Court in Boesche v. Udall,[181] where the Court stated:

Unlike a land patent, which divests the Government of title, Congress under the Mineral Leasing Act has not only reserved to the United States the fee interest in the leased land, but has also subjected the lease to exacting restrictions and continuing supervision by the Secretary. . . . [The Secretary] may prescribe, as he has, rules and regulations governing in minute detail all facets of the working of the land. In short, a mineral lease does not give the lessee anything approaching the full ownership of a fee patentee, nor does it convey an unencumbered estate in the minerals.[182]

Accordingly, it is clear BLM has very expansive retained rights under a federal onshore oil and gas lease that allow it to condition development so as to protect natural resources and values. The recognition by the Supreme Court of these expansive rights retained by the government occurred long before the modern lease form was put in place in 1984 with its explicit list of authorities a lease is made “subject to.”

B. Applicable Laws and Specific, Nondiscretionary Statutes

Modern leases issued since March 1984 are made subject to “applicable laws” under the terms of the lease form.[183] In addition, leases issued since May 1988 are made subject to “restrictions deriving from specific, nondiscretionary statutes” under the terms of the § 3101.1-2 regulation.[184] “Applicable laws” would seem to be a category of statutes the lease has been made subject to that is broader than “specific, nondiscretionary statutes.”
I believe that both of these provisions guide what retained rights BLM enjoys, not one to the exclusion of the other, at least with regard to the 34,367 currently active leases in the eleven western states issued since June 1988, when both reservations were in place (see Table 1).

BLM’s commentary when it adopted the § 3101.1-2 regulation indicates it was not the intent of this regulation to replace or supplant the “applicable laws” language in the lease form.[185] While the commentary focuses on the “reasonable measures” language in the regulation, the overall thrust of this regulation was to “establish the measures over which the Bureau has clear authority” and to “establish minimum parameters” for purposes of specifying site-specific mitigation measures.[186] Consequently, the “specific, nondiscretionary statute” language in the regulation is probably best interpreted as setting a baseline from which BLM has “clear authority,” and not an attempt to exclude other applicable laws that are perhaps less mandatory. Furthermore, BLM’s leasing regulations provide that “[a] lease shall be issued only on the standard form approved by the Director” of BLM.[187] This regulation was also adopted on May 16, 1988, when the current version of the § 3101.1-2 regulation was adopted,[188] so it seems unlikely BLM was attempting to nullify the “applicable laws” language that was already in its existing lease forms through use of the “specific, nondiscretionary statutes” language in the § 3101.1-2 regulation. The “applicable laws” language was present in leases from March 1984 onward, so if BLM intended to modify or limit this language in the § 3101.1-2 regulation adopted in
May 1988 it would have done so explicitly.

Because I view most currently active leases as being subject to both applicable laws and specific, nondiscretionary statutes, I will review both of these kinds of laws. Myriad laws are applicable to environmental protection on a leasehold, and there are several statutes that are specific and nondiscretionary. Some of these laws have been in place for many years—one was enacted prior to the Mineral Leasing Act—and thus would apply to all or most active leases.[189] Many were enacted in the 1960s and 1970s, and thus would have been laws in place when both the “applicable laws” language was introduced in March 1984 and when the “specific, nondiscretionary statutes” language was introduced in May 1988.[190] Thus, many of the laws that will be discussed below at a minimum help define BLM’s retained rights on the 35,256 out of 48,342 currently active leases in the eleven western states that have been issued since March 1984 (see Table 1).[191]

1. The Mineral Leasing Act

As discussed, the Mineral Leasing Act provides for the “disposition” of oil and gas through a leasing system.[192] The Mineral Leasing Act also contains several other provisions that are applicable to oil and gas development that implicate environmental protection, and one provision appears to be specific and nondiscretionary.

First, “[e]ach lease shall contain provisions for the purpose of insuring the exercise of reasonable diligence, skill, and care in the operation of said property.”[193] The courts do not appear to have interpreted the meaning of the word “care” in this passage, but it could allow for protection of the natural environment in the operation of a lease.[194] Second, “[t]he Secretary of the Interior is authorized to prescribe necessary and proper rules and regulations and to do any and all things necessary to carry out and accomplish the purposes of this [Act], also to fix and determine the boundary lines of any structure, or oil or gas field.”[195] The courts have recognized this provision grants broad authority to the Secretary of the Interior to regulate oil and gas development.[196] It obviously allows great discretion in rulemaking, and the regulations applicable to oil and gas leasing and lease operations will be discussed below.[197] But the additional authority to “determine the boundary lines of any structure, or oil or gas field”[198] could directly allow for environmental protection by authorizing BLM to specify the locations of structures and oil and gas fields. A third reservation of authority provided by the Mineral Leasing Act is that “[t]he Secretary of the Interior, for the purpose of encouraging the greatest ultimate recovery of [leasable minerals], and in the interest of conservation of natural resources, is authorized to waive, suspend, or reduce the rental, or minimum royalty, or reduce the royalty on an entire leasehold.”[199] In Copper Valley Machine Works, Inc. v. Andrus[200] and Getty Oil Co. v. Clark,[201] the courts recognized and approved the government’s authority to suspend leases so as to conserve environmental resources based on this statutory provision.[202]

And in what is likely a specific, nondiscretionary provision, the Mineral Leasing Act requires that “[t]he Secretary of the Interior . . . shall regulate all surface-disturbing activities conducted pursuant to any lease issued under this chapter, and shall determine reclamation and other actions as required in the interest of conservation of surface resources.”[203] This addition to the Mineral Leasing Act was adopted in 1987 in the Federal Onshore Oil and Gas Leasing Reform Act (FOOGLRA).[204] Accordingly, this provision may only create retained rights on leases issued after 1987. But even if this is true, approximately 34,367 of the 48,342 currently active leases in the eleven western states are subject to this provision (see Table 1).

2. The National Environmental Policy Act

Although it is well settled that NEPA does not mandate particular results to protect the environment but rather prescribes the necessary process for environmental review, NEPA is also referred to as our nation’s basic environmental charter.[205] NEPA provides that “to the fullest extent possible” the laws and policies of this country are to be interpreted and administered in accordance with the policies set forth in NEPA, which include environmental protection goals.[206] In carrying out the policy of NEPA, agencies must “use all practicable means” consistent with other considerations of national policy to achieve six specified ends aimed at environmental protection.[207] The Council on Environmental Quality regulations implementing NEPA reinforce the obligation to pursue protection of the natural environment that NEPA mandates.[208]

While NEPA may not be specific and nondiscretionary, there is no doubt it is applicable to oil and gas development decision making on BLM lands. The prominent role NEPA plays at the leasing stage will be discussed infra in Part VII.D. However, the courts also recognize that the purposes and goals of NEPA control BLM’s oil and gas development decisions.
In Getty Oil Co., the court determined that “[t]he Secretary [of the Interior] is not only permitted, but is required, to take environmental values into account in carrying out his regulatory functions [related to oil and gas development], unless there is a clear and unavoidable statutory authority prohibiting the Secretary from complying with NEPA’s mandate.”[209]

In a case originating in an important natural area in Michigan that included brown trout (Salmo trutta) waters described as perhaps
“the best east of the Rockies,” the court considered BLM’s and the
Forest Service’s obligations under NEPA when lease development activities are pursued, in this case approval of exploratory drilling.[210] The Forest Service’s no significant impact determination allowing it to avoid preparation of an EIS was arbitrary and capricious because it failed to adequately consider four of the “intensity” factors for determining environmental significance that the Council on Environmental Quality NEPA regulations say should be considered.[211]

The range of alternatives considered in the EA underlying the approval of this project was also deficient. First, the no action alternative of not permitting drilling was improperly rejected from full consideration because the Forest Service felt it was obligated to approve drilling.[212] But the court held that “none of the cited authorities [mandate] approval of proposed mineral extraction, forecloses a decision of No Action, or places the Forest Service’s objectives at odds with environmental preservation.”[213] Moreover, in considering BLM’s regulation at 43 C.F.R. § 3161.2, which directs the authorized officer to require that operations protect environmental quality and which will be discussed in more detail below,[214] the court held that “[t]he plain language of the regulation makes [it] clear that approval is not appropriate in all cases, particularly cases where the project poses a threat to environmental quality.”[215] Second, the court held that the range of alternatives considered was deficient “because it impermissibly limited the range of alternatives to only those that would meet [the project proponent’s] project objectives, rather than alternatives that might better serve Forest Service goals.”[216]

However, the court rejected a claim that the regulation at 43 C.F.R. § 3161.2, which again will be discussed in more detail below, was violated by the Forest Service’s approval of the project.[217] The basis for this holding was the court’s conclusion that violating NEPA did not demonstrate a violation of BLM’s substantive environmental protection regulation.[218] Compliance with BLM’s oil and gas operations regulations relating to environmental protection obligations was also considered in a case that originated in
New Mexico; this case will be considered infra in Part V.D.1.b.

Given this precedent, it is clear that when operations are proposed on a lease, BLM must interpret and implement its obligations in light of the policies established by NEPA, particularly if the lease was issued after 1969 when NEPA was enacted.[219] NEPA is an “applicable law” that a lease is “subject to.”[220]

But as explained above, the role of NEPA at the APD stage of oil and gas development has recently been reduced due to the availability of “categorical exclusions” from NEPA compliance that were created by the Energy Policy Act of 2005.[221] Twenty-eight percent of the APDs that
BLM approved between 2006 and 2008 were relieved of further NEPA compliance through the use of these categorical exclusions.[222] But categorical exclusions should not be viewed as completely eliminating application of NEPA in the oil and gas development process. These exclusions are available under five specified circumstances, and two of the conditions require that there has been prior NEPA compliance before an exclusion can be invoked.[223] And in the majority of field offices, any oil and gas development will occur pursuant to an RMP that was developed in compliance with NEPA.[224] Consequently, NEPA remains an “applicable law” that leases are made “subject to.”

3. The Federal Land Policy and Management Act

FLPMA, BLM’s organic act, establishes policy and requirements to protect the natural environment, including the policy that

the public lands be managed in a manner that will protect the quality of scientific, scenic, historical, ecological, environmental, air and atmospheric, water resource, and archeological values; that, where appropriate, will preserve and protect certain public lands in their natural condition; that will provide food and habitat for fish and wildlife and domestic animals; and that will provide for outdoor recreation and human occupancy and use.[225]

There is no doubt FLPMA is an applicable law that leases have been made subject to, at least if the lease was issued after 1976, which includes the majority of currently active leases in the eleven western states (see Table 1).

While FLPMA also establishes a policy that “recognizes the Nation’s need for domestic sources of minerals . . . including implementation of the Mining and Minerals Policy Act of 1970 as it pertains to the public lands,”[226] it seems clear the commodity development and environmental protection policies must be viewed as companion goals. Under FLPMA, BLM is required to manage the public lands under a multiple use and sustained yield mandate,[227] which requires, among other things, the

harmonious and coordinated management of the various resources without permanent impairment of the productivity of the land and the quality of the environment with consideration being given to the relative values of the resources and not necessarily to the combination of uses that will give the greatest economic return or the greatest unit output.[228]

And most importantly, FLPMA requires that “[i]n managing the public lands the Secretary [of the Interior] shall, by regulation or otherwise, take any action necessary to prevent unnecessary or undue degradation of the lands.”[229] There is little doubt that BLM views this provision as a specific, nondiscretionary statute.[230]

FLPMA’s mandate to prevent unnecessary or undue degradation imposes dual action requirements on BLM. It must take any action needed to prevent both unnecessary degradation as well as undue degradation of the public lands. This dual obligation was confirmed in Mineral Policy Center v. Norton.[231] Addressing this requirement, the court held that “Congress’s intent was clear: Interior is to prevent, not only unnecessary degradation, but also degradation that, while necessary to mining, is undue or excessive.”[232]
While the unnecessary degradation prong may only prevent activities that are not generally recognized or used to pursue mining operations, the undue degradation prohibition establishes a further requirement to prevent activities that would unduly harm or degrade the public land. As stated by the court, “FLPMA, by its plain terms, vests the Secretary of the Interior with the authority—and indeed the obligation—to disapprove of an otherwise permissible mining operation because the operation, though necessary for mining, would unduly harm or degrade the public land.”[233]

BLM has adopted regulations that define unnecessary or undue degradation (UUD) for purposes of hardrock mining pursuant to the General Mining Law,[234] but has no regulations that define UUD relative to oil and gas development. But one court agreed that “[a] reasonable interpretation of the word ‘unnecessary’ is that which is not necessary for mining. ‘Undue’ is that which is excessive, improper, immoderate or unwarranted.”[235] And IBLA determined that “Congress . . . recognized that the mere act of approving oil and gas development does not constitute unnecessary or undue degradation under [the] FLPMA, and that something more than the usual effects anticipated from such development, subject to appropriate mitigation, must occur for degradation to be ‘unnecessary or undue.’”[236] Despite these limited interpretations of the UUD clause, there is no doubt that this provision is specific and nondiscretionary and thus its requirements must be complied with when lease development is proposed.[237]

4. The Endangered Species Act

The Endangered Species Act of 1973 (ESA),[238] which of course seeks to protect threatened or endangered species listed under the Act, calls for special mention. BLM may recognize this law more than any other as being a “specific, nondiscretionary statute,” which thus guides (or limits) its management of oil and gas leases to a degree perhaps not reflected in its decision making for other resources.[239] The ESA was enacted in 1973, and thus, at a minimum, is applicable to the roughly 38,000 currently active leases in the eleven western states issued since 1973 (see Table 1). There is no doubt the ESA’s section 7 “jeopardy standard” and its section 9 prohibition on taking endangered species are specific and nondiscretionary provisions.[240] In addition, the Act requires the Secretary of the Interior to further the purposes of the ESA, including conserving the ecosystems upon which listed species depend and providing for their conservation.[241] Given these mandatory provisions, there is no doubt BLM has the authority, and in fact the obligation, to ensure compliance with the ESA when it makes development decisions related to federal oil and gas leases that could affect listed species.

The ESA establishes a number of requirements intended to foster the conservation of listed species, particularly regarding the prohibition under section 7 on federal actions that cause jeopardy to the continued existence of listed species.[242] Under these provisions, an agency can be required to prepare a biological assessment that considers the effects of an agency action on a listed species and engage in consultation with the United States Fish and Wildlife Service (FWS) regarding the effects of the action.[243] Consultation can result in an FWS biological opinion specifying mandatory terms and conditions for any incidental take of a listed species, recommended conservation measures intended to further protection and recovery of the species, and even a “jeopardy opinion,” which can effectively preclude the action.[244]

The courts have considered the requirements of the ESA in the context of the leasing decision in areas where listed species such as grizzly bears (Ursus arctos horribilis) and spectacled eiders (Somateria fischeri) exist.[245] Consultation with FWS must occur at the leasing stage, and the consultation must consider not only the effects of leasing on listed species, but also
“all phases of the agency action, which includes post-leasing activities.”[246]
In a challenge to the sale of sixteen lease parcels in an area of Colorado where the threatened hookless cactus (Sclerocactus glaucus) occurred, the court held BLM’s consultation with FWS was inadequate because the consultation failed to consider the full “action area” encompassed by all sixteen parcels, having considered only the nine parcels where the cactus occurred, and thus not recognizing potential indirect effects to the species.[247] But other courts have held that ESA challenges to leasing were not ripe for judicial resolution, and thus denied motions for summary judgment.[248] In Wyoming Outdoor Council v. Bosworth, however, the court recognized the ESA is a specific, nondiscretionary statute.[249]

5. Other Laws Applicable to Protection of the Public Lands

Besides these four overarching statutes, there are other laws that are at least applicable to federal oil and gas leases, and some are in all likelihood specific and nondiscretionary. In the interest of space I will not discuss these laws in detail but will note some of them:

  • Under section 106 of the National Historic Preservation Act of 1966,[250] BLM must take into account the effect of its undertakings on sites that are eligible for or included in the National Register of Historic Places.[251] And prior to approval of a federal undertaking that may affect a National Historic Landmark, the agency must minimize harm to the landmark “to the maximum extent possible.”[252]
  • The Archeological Resources Protection Act of 1979[253] provides that “[n]o person may excavate, remove, damage, or otherwise alter or deface . . . any archeological resource located on public lands . . . unless such activity is pursuant to a permit” and also prohibits attempting to do so.[254]
  • The Migratory Bird Treaty Act[255] has been in place since 1918 and makes it unlawful to take, kill, or otherwise possess or interfere with a number of migratory bird species subject to treaties between the United States and several countries unless done under the governing regulations of the Secretary of the Interior.[256] Similarly, the Bald and Golden Eagle Protection Act of 1940[257] makes it illegal to take or otherwise possess or interfere with bald eagles (Haliaeetus leucocephalus) and golden eagles (Aquila chrysaetos) unless done under permit.[258]
  • The National Trails System Act of 1968[259] established recreation, scenic, and historic trails.[260] Section 7(i) allows regulation of the use and protection of the trails,[261] and particularly with respect to historic trails such as the Oregon Trail, the provisions of the National Historic Preservation Act may also apply. Provisions of the National Wild and Scenic Rivers Act of 1968[262] might be applicable to some federal oil and gas leases.[263]
  • The Clean Air Act[264] declared a national purpose to protect and enhance air quality so as to promote the public health and welfare and a national goal of protection of visibility in highly scenic Class I areas, which include many wilderness areas and national parks.[265]
    It establishes a massive regulatory and permitting regime to ensure compliance with National Ambient Air Quality Standards for several “criteria” pollutants and provides for a number of other pollution control requirements.[266] These requirements are primarily implemented by the states, but the Clean Air Act also provides that all federal agencies having jurisdiction over a property or facility that may result in the discharge of air pollutants shall be subject to, and comply with, all requirements “respecting the control and abatement of air pollution in the same manner, and to the same extent as any nongovernmental entity.”[267]
  • The Clean Water Act[268] has as its objective attempting “to restore and maintain the chemical, physical, and biological integrity of the Nation’s waters,” and to achieve this objective it establishes goals that the discharge of water pollutants be eliminated, that fish and wildlife be protected, and that recreation be provided for in and on the water.[269] Like the Clean Air Act, a massive regulatory and permitting regime primarily administered by the states was created.[270] Under this regime several kinds of water quality standards or programs are created and enforced.[271] And using language that is the same as that found in the Clean Air Act, the Clean Water Act also makes its provisions for abatement of water pollution applicable to federal agencies “in the same manner, and to the same extent as any nongovernmental entity.”[272]
  • Several federal statutes respecting the management, control, cleanup, and reporting of chemicals and hazardous wastes or substances have been enacted. These include the Resource Conservation and Recovery Act of 1976 (RCRA);[273] the Comprehensive Environmental Response, Compensation, and Liability Act of 1980 (CERCLA),[274]
    also known as the Superfund; the Toxic Substances Control Act;[275] and the Emergency Planning and Community Right-To-Know Act of 1986.[276] Many of these statutes contain explicit exemptions for the oil and gas industry, and thus they may not be applicable laws relative to BLM oil and gas leases.[277] Nevertheless, chemicals and hazardous waste are subject to controls by BLM; some of the authorities establishing these rights will be discussed.[278] While these federal statutes may not be applicable laws in some cases, it is also apparent there are provisions dealing with hazardous wastes that are applicable.
  • Even noise pollution has come to the attention of Congress. Congress has found that inadequately controlled noise presents a danger to public health and welfare and has declared a policy “to promote an environment for all Americans free from noise that jeopardizes their health or welfare.”[279] And thus, “Congress authorizes and directs that Federal agencies shall, to the fullest extent consistent with their authority under Federal laws administered by them, carry out the programs within their control in such a manner as to further [this] policy.”[280]

It is apparent there is a wide range of environmental protection laws that are applicable to development of federally owned oil and gas resources, and a number of these are “specific, nondiscretionary statutes.”[281]

6. Energy Policy Statutes

In addition to the numerous environmental protection statutes that are “applicable” to federal oil and gas leases, provisions of federal energy policy are also applicable and evidence a goal of pursuing energy development on federal lands. Despite this goal, however, these laws have not repealed or amended the environmental protection statutes that have been discussed. Congress has declared a policy of support for energy development but also stated this would advance the goals of “protecting[] and enhancing environmental quality,” and assuring public health.[282] In the Mining and Minerals Policy Act of 1970,[283] Congress provided that it is the continuing policy of the federal government to “foster and encourage private enterprise” in the pursuit of minerals development.[284] Congress has sought to increase the recoverability of energy resources.[285] Section 604 of the Energy Policy and Conservation Act Amendments of 2000 (EPCA)[286] required an inventory of onshore federal lands to identify oil and gas resources underlying those lands, including an assessment of “the extent and nature of any restrictions or impediments to the development of the resources.”[287]

Probably most significantly, in the Energy Policy Act of 2005 Congress established several policies related to oil and gas development on the public lands. To ensure timely action on leases and APDs, the Secretary of the Interior is to “ensure expeditious compliance” with NEPA and take several other actions.[288] Best management practices (BMPs) are to be developed and implemented in order to improve the leasing program and ensure timely action on APDs.[289] Using these BMPs as guidance, regulations setting forth timeframes for processing leases and APDs are to be developed, and deadlines are to be established for approving or disapproving resource management plans, lease applications, APDs, surface use plans, and related administrative appeals.[290] And in section 390 of the Energy Policy Act of 2005, rebuttable presumptions allowing the use of categorical exclusions to meet NEPA obligations under five enumerated circumstances were established for oil and gas exploration or development activities.[291] Nevertheless, while Congress sought to speed up oil and gas development on the public lands through enactment of the Energy Policy Act of 2005, it did not require accomplishment of this goal by repealing the numerous applicable environmental protection laws that a lease might be subject to.

Based on this review of potentially “applicable laws” oil and gas leases have been made “subject to,” as well as a number of “specific, nondiscretionary statutes” that leases have also been made “subject to,” it is apparent BLM has many retained rights allowing it to protect the natural environment despite having granted a right to develop the oil and gas that might be found on a lease.[292] The federal government has retained significant rights allowing it to protect threatened or endangered species, prevent air and water pollution, control hazardous substances, regulate noise, ensure “care” is exercised in operations on a leasehold, regulate operations in order to conserve surface resources, protect historic trails and other cultural and archeological resources, prevent unnecessary or undue degradation of the public lands, and ensure the policies of NEPA are adhered to, among other things.[293] When coupled with the substantial rights retained under the “terms, conditions, and stipulations in the lease” and “regulations and formal orders” in effect when the lease was issued and even afterward if not inconsistent with the lease rights granted, it is apparent BLM has significant retained rights allowing it to specify to a significant degree the time, place, and manner of oil and gas development on a lease.[294] Retained rights stemming from lease terms, conditions, and stipulations will be considered next.

C. Terms, Conditions, and Attached Stipulations of BLM Oil and Gas Leases

As discussed in detail above, BLM’s leases, whether of the modern form or what is apparent in the examples of older leases, retain many rights to the federal government to protect the natural environment.[295] The terms and conditions in the leases provide that the rate of development and production can be specified; especially in the modern leases there are requirements to minimize adverse impacts to the environment, lease suspensions can be required, reclamation measures can be specified, and in some instances operations can be denied.[296] It is apparent that the contractual relationship established between BLM and its oil and gas lessees allows BLM to regulate the time, place, and manner of oil and gas development to a substantial degree under the terms and conditions of the lease.

But in addition to making the rights granted under a lease subject to the terms and conditions in the lease, the modern versions of the lease form operable since March 1984 state that the rights granted are subject to “attached stipulations of this lease.”[297] The § 3101.1-2 regulation in place since 1988 also makes leases “subject to” stipulations attached to the lease.[298] Stipulations have not been discussed previously.

BLM regulations provide that “[s]tipulations shall become part of the lease and shall supersede inconsistent provisions of the standard lease form.”[299] The lessee is deemed to agree to the terms of a stipulation.[300]
There are three types of stipulations BLM requires: 1) no surface occupancy (NSO) stipulations, 2) timing limitation stipulations (TLS), and 3) controlled surface use (CSU) stipulations.[301] NSO stipulations prohibit drilling on the surface of a lease or a described portion of it and are reserved for the most sensitive landscapes.[302] A TLS limits the time periods when drilling—but not operations and maintenance of production facilities—can occur, such as prohibiting drilling on big game crucial winter ranges between November 15th and April 30th.[303] A CSU stipulation prohibits surface occupancy unless certain operating constraints are met, such as limiting surface occupancy or use within 500 feet of riparian areas unless an acceptable mitigation plan is arrived at first.[304] There are many stipulations currently in use, protecting such things as historic trails and resources, threatened, endangered or special status species, high quality visual environments, raptors, and special management areas, among others.[305] In Wyoming, it is not unusual for a current lease to have between four to seven stipulations attached to it.[306] Examples of these stipulations can be seen in any BLM Notice of Competitive Oil and Gas Lease Sale.[307] BLM’s manual governing issuance of leases contains a number of provisions regarding stipulations.[308]

In addition to stipulations, current leases also often have “information notices” attached to them.[309] There are currently three lease notices in use in Wyoming: one applicable to protections for steep slopes and certain other resources, one applicable to historic trails, and one applicable to the greater sage-grouse.[310] While these notices express an intent to protect these resources, they probably have little or no legal consequence:

An information notice has no legal consequences, except to give notice of existing requirements, and . . . [only] convey[s] certain operational, procedural or administrative requirements relative to lease management within the terms and conditions of the standard lease form. Information notices shall not be a basis for denial of lease operations.[311]

“The issuance of the Information Notices therefore establishe[s] no binding policy or practice . . . .”[312] So while these notices certainly express a goal of BLM’s to protect resources like the sage-grouse, the legal authority for any resulting actions must be found in the lease itself, in the § 3101.1-2 regulation, or in other law, not in the lease notice.

D. Regulations and Formal Orders

With respect to modern versions of the lease form issued since 1984, the rights granted under the lease are made subject to two conditions related to compliance with regulations and formal orders, one applicable to regulations and formal orders in place when the lease is issued, and the other to later-adopted regulations and formal orders. In the modern lease forms, the rights granted are subject to “the Secretary of the Interior’s regulations and formal orders in effect as of lease issuance” and are additionally subject to “regulations and formal orders hereafter promulgated when not inconsistent with lease rights granted or specific provisions of this lease.”[313] The older versions of the lease from 1954, 1965, and 1971 provide that the offer to lease is pursuant and subject to the rules and regulations of the Secretary of the Interior “now or hereafter in effect” when not inconsistent with the lease rights granted.[314] These conditions on the exercise of lease rights will be considered next.

1. Regulations

a. The Regulations at 43 C.F.R. Part 3100

BLM’s current leasing regulations are found at 43 C.F.R. part 3100.
The § 3101.1-2 regulation that elaborates on the rights granted to the lessee and BLM’s retained rights when an oil and gas lease is issued was discussed in some detail above,[315] as was the § 3101.1-1 regulation that provides that leases shall be issued only on standard forms.[316] In addition, the regulations applicable to stipulations were just discussed.[317] An additional regulation in this part provides that “[a] suspension of all operations and production may be directed or consented to by the authorized officer only in the interest of conservation of natural resources.”[318] Suspension of lease operations is a significant means by which BLM can exercise its retained rights to protect the natural environment.[319] When a suspension occurs, the term of the lease is extended by the period of time of the suspension, and rental and minimum royalty payments are also suspended.[320] Few other regulations in part 3100 likely implicate BLM’s retained rights with respect to environmental protection after issuing an oil and gas lease.[321]

The current version of BLM’s oil and gas leasing regulations was promulgated in 1988.[322] Thus, the current version of the part 3100 regulations would clearly apply to the 34,367 currently active leases in the eleven western states issued since that date (see Table 1). Most significantly, the § 3101.1-2 regulation applies to these leases, which represent seventy-one percent of the currently active leases in the eleven western states (see Table 1).

Prior to adoption of the 1988 version of the leasing regulations, which were promulgated to comply with FOOGLRA,[323] several iterations of the leasing regulations had been in place. Regulations governing oil and gas leases were in place in 1938, and notices of modifications to the regulations were published in the Federal Register in 1946, 1954, 1964, 1970, and 1983.[324] The 1983 regulations contained a provision in § 3101.1-2, but it was amended when the 1988 version that has been discussed extensively was adopted.
The 1983 version provided that stipulations could be attached to a lease only if either “the stipulations did not absolutely bar exploration” or the lease as stipulated remained acceptable to the offeror.[325] With respect to provisions allowing BLM to ensure protection of the environment, many of the older versions of the leasing regulations provided for suspensions and stipulations.[326]

Whether leases issued prior to 1988 are subject to the current leasing regulations, particularly the § 3101.1-2 regulation, is debatable, but the broad reservations contained in the 1954, 1965, and 1971 leases, such as the term allowing the rate of prospecting and development and the quantity and rate of production to be subject to BLM control in the public interest, [327] suggest that these leases could be subject to the later-adopted regulations. The older leases provide that reasonable regulations “hereafter in force” apply to the lease if not inconsistent with the provisions in the lease.[328] Section 6 of the 1984 version of the lease form already allowed for reasonable measures to be required, even before the § 3101.1-2 regulation was promulgated in 1988.[329] Accordingly, the current version of the leasing regulations could well apply to leases issued prior to 1988. However, as will be discussed below, in some circumstances the courts have not been receptive to allowing later-enacted statutes to govern a lease.[330]

b. The Regulations at 43 C.F.R. Part 3160 and Other BLM Regulations

In addition to its leasing regulations, BLM also has an extensive body of regulations governing onshore lease operations. These regulations are found at 43 C.F.R. part 3160.[331] BLM’s current operating regulations are replete with provisions allowing BLM to protect the natural environment when operations are proposed, including the following:

  • “The authorized officer is authorized and directed to . . . require compliance with lease terms, with the regulations in this title and all other applicable regulations promulgated under the cited laws; and to require that all operations be conducted in a manner which protects other natural resources and the environmental quality . . . .”[332]
  • “Before approving operations on [a] leasehold, the authorized officer shall determine . . . that the proposed plan of operations is sound both from a technical and environmental standpoint.”[333]
  • Operators are to comply with applicable laws, regulations, lease terms, onshore oil and gas orders, notices to lessees, and other orders and instructions from BLM, including but not limited to conducting all operations in a manner that “protects other natural resources and environmental quality.”[334]
  • The regulations make extensive provisions regarding submission of APDs, including requiring submission of a surface use plan of operations which must contain information regarding roads and drill pads, methods for containment and disposal of waste materials, and reclamation plans.[335]
  • “The operator shall conduct operations in a manner which protects the mineral resources, other natural resources, and environmental quality,” which obligates the operator to comply with all pertinent orders, applicable laws, regulations, lease terms and conditions, and the approved drilling plan.[336] BLM is to prepare an environmental review to ensure compliance with NEPA, and this environmental review can be used to determine terms and conditions of approval of the proposed drilling plan.[337]
  • “The operator shall exercise due care and diligence to assure that leasehold operations do not result in undue damage to surface or subsurface resources or surface improvements.”[338]
  • Operators may be subject to penalties for noncompliance with these regulations, including shut down or shut-in of operations where significant environmental impacts are occurring.[339]

While these regulations clearly create mandatory obligations to protect the environment, that is not their sole purpose. The regulations at 43 C.F.R. §§ 3161.2 and 3162.1(a) require actions to protect the environment, but they also specifically provide that an objective of operations is to maximize oil and gas recovery.[340]

Moreover, one court, in Blancett v. U.S. Bureau of Land Management,[341] determined many of these regulations do not provide a basis for a “failure to act” claim pursuant to the Administrative Procedure Act.[342] This case concerned claims that BLM had failed to protect the environment from oil and gas operations that affected a ranch in New Mexico.[343] The court ruled that while the regulations at 43 C.F.R. §§ 3161.2, 3162.1(a), and 3162.5-1(a)–(b) established broad objectives, “none of the regulations in Part 3160 imposes a mandatory duty on BLM to protect the environment with the specificity required to support a claim under § 706(1) of the [Administrative Procedure Act].”[344] It found the regulations did not specify discrete agency action and did not define actions that were legally required.[345] Thus, the plaintiffs’ lawsuit failed the two-part test under the Supreme Court’s precedent in Norton v. Southern Utah Wilderness Alliance[346] that is required to support a § 706(1) claim.[347] Consequently, the court granted BLM’s motion to dismiss the lawsuit based on the pleadings and found that it did not have subject matter jurisdiction. However, because the dismissal without prejudice did not constitute a decision on the merits,[348] the precedential value of this unpublished decision is limited. BLM’s obligations to protect the environment will be considered further in Part IX.[349]

Despite the decision in Blancett, it seems clear that even if BLM’s operations regulations do not mandate particular actions by BLM that can be enforced in court, the regulations nevertheless provide that BLM is obligated to require environmental protection when it permits oil and gas development. As the court recognized in Blancett, defendant BLM “acknowledge[s] that the regulations charge BLM with requiring operator compliance with lease terms and regulations and with requiring that operations be conducted in a manner that protects environmental quality.”[350]

A form of the part 3160 regulations that closely approximates the current version of the regulations with respect to environmental protection obligations has been in place since 1982 when the Minerals Management Service (MMS) amended the predecessor regulations.[351] The 1982 regulations were intended to be codified at 30 C.F.R. part 221, and at that time onshore operations were under the direction of MMS, not BLM.[352] However, the 1982 regulations were amended again in August 1983. In the 1983 revision the regulations were transferred from 30 C.F.R. part 221 and redesignated as
43 C.F.R. part 3160, and the management authority was transferred to BLM.[353] In 1988, as part of the regulatory revisions needed to conform to FOOGLRA, the operating regulation governing APDs was modified to its current form by adding requirements related to surface use plans of operation, as well as other provisions.[354] Thus, with respect to environmental protection provisions, the current version of the operations regulations has been fully in place since 1988,[355] but regulations quite similar to, and often identical to, the current regulations have been in place since 1982.[356] Consequently, the vast majority of currently active leases in the eleven western states are subject to the current operating regulations or a version very similar to them (see Table 1).

Prior to the 1982 revision of the regulations, MMS managed oil and gas operations under regulations adopted in 1942.[357] The 1942 regulations, which were in place for forty years,[358] provided for less in the way of environmental protection than the current regulations, but they did provide that “[t]he lessee shall not pollute streams or damage the surface or pollute the underground water of the leased or other land.”[359] More generally, the old operations regulations required compliance with lease terms, regulations, and applicable law.[360]

In addition to the part 3160 regulations, BLM also promulgated regulations governing approval of land use authorizations. With respect to provisions that are relevant here, these regulations have been in place since 1981.[361] These regulations provide that the United States reserves the right to use the public lands or authorize the use of the public lands by the general public in ways that are compatible or consistent with the land-use authorization.[362] They also provide that each land-use authorization shall contain terms and conditions that shall minimize damage to scenic, cultural, and aesthetic values and wildlife habitat and that “otherwise protect the environment”;[363] require compliance with air and water quality standards;[364] and require compliance with state environmental protection standards that are more stringent than federal standards.[365] Land-use authorizations shall also contain provisions that “[r]equire the use to be located in an area which shall cause least damage to the environment, taking into consideration feasibility”[366] and to “[o]therwise protect the public interest.”[367] Other provisions provide for inspection and monitoring during construction, operation, and maintenance of the land-use authorization so as to protect
the environment.[368]

In sum, BLM’s oil and gas leasing regulations, its oil and gas operations regulations, and the land-use authorization regulations provide an additional and substantial basis for BLM to assert retained rights so as to protect the natural environment. The leasing regulations have existed in their present form since 1988, the operations regulations have been in essentially their current form since 1982, and the relevant land-use authorization regulations have been in place since 1981. Consequently the majority of currently active leases in the eleven western states are subject to these provisions without need to consider the question of whether later-adopted regulations were incorporated into a lease or were consistent with lease rights previously granted (see Table 1).

2. Formal Orders

Beyond these regulatory provisions are a number of authorities that could be “formal orders,” which many leases are also subject to—particularly leases issued since 1984 when this condition on the granted lease rights was introduced.[369] These formal orders could include BLM Resource Management Plans (RMPs) developed pursuant to FLPMA, onshore oil and gas orders, notices to lessees, provisions in the BLM manual and handbook, BLM instruction memoranda, BLM’s “Gold Book,”
Executive Orders, and Department of the Interior Solicitor opinions and Secretarial orders. These sources of authority will be considered next.

a. Resource Management Plans

BLM RMPs are required by FLPMA,[370] and their role in the oil and gas leasing and development process was discussed above.[371] Once an RMP is developed, the Secretary of the Interior shall manage the public lands governed by the plan in accordance with the plan.[372] There seems to be little doubt that an RMP constitutes a formal order that an oil and gas lease issued since 1984 is subject to.

The first RMPs were adopted in the early to mid-1980s.[373] Accordingly, oil and gas leases have been made subject to these formal orders since approximately the mid-1980s. As indicated several times above, it seems likely that older leases are also subject to the provisions in a later-adopted RMP because the expansive language in older leases—“not inconsistent with any express and specific provisions herein”[374]—arguably makes the older leases subject to the later-adopted RMP provisions. For RMPs adopted after 1984, the RMP provisions could well be “not inconsistent with lease rights granted or specific provisions of this lease,” as provided for in the modern lease form in place since 1984.[375]

RMPs provide general guidance for oil and gas development that might occur pursuant to them.[376] Under the BLM handbook governing land-use planning, an RMP should identify areas open to leasing subject to various constraint levels—for example, an area may be open to leasing with “moderate constraints” such as seasonal and controlled surface-use restrictions; identify areas closed to leasing; identify lease stipulations, conditions of approval, and best management practices that will be employed; identify “[w]hether constraints identified in the land use plan for new leases also apply to areas currently under lease”; and define “resource condition objectives for areas under development to guide reclamation activities in these areas.”[377] Thus, RMPs contain considerable guidance that oil and gas leases are subjec to.

b. Onshore Oil and Gas Orders

BLM is authorized to issue Onshore Oil and Gas Orders when necessary to implement or supplement the oil and gas operations regulations.[378]
Seven onshore orders are currently in effect.[379] They deal with drilling and disposal of produced water, site security, and other issues. An onshore order is “binding on operating rights owners and operators.”[380]

The most significant onshore order for purposes of this discussion is Onshore Oil and Gas Order Number 1.[381] This order was first adopted on October 21, 1983,[382] and it was most recently revised on March 7, 2007.[383]
It governs approval of oil and gas exploratory, development, and service wells and most subsequent well operations on essentially all federal onshore oil and gas leases.[384] The order governs APDs including their accompanying drilling plans and surface use plan of operations.[385] Among other things, the order describes a number of requirements for the surface-use plan of operations.[386] These include provisions for revegetation of disturbed areas and the safe containment and disposal of waste material (including chemicals).[387] The processing of APDs is discussed and prescribed in detail, including requirements for on-site inspections.[388] BLM can approve, defer, or deny an APD depending on whether certain requirements have been met; this includes a provision that “BLM cannot approve an APD or Master Development Plan until the requirements of certain other laws and regulations including NEPA, the National Historic Preservation Act, and the Endangered Species Act have been met.”[389] Onshore Order Number 1 then makes this provision:

The approved APD will contain Conditions of Approval that reflect necessary mitigation measures. In accordance with 43 CFR 3101.1-2 . . . , the BLM . . . may require reasonable mitigation measures to ensure that the proposed operations minimize adverse impacts to other resources, uses, and users, consistent with granted lease rights. The BLM will incorporate any mitigation requirements, including Best Management Practices, identified through the APD review and appropriate NEPA and related analyses, as Conditions of Approval to the APD.[390]

It is noteworthy that the “reasonable mitigation measures” referred to here are not confined to the “200-meter 60-day rule” limitations mentioned in the § 3101.1-2 regulation, and thus these reasonable mitigation measures are arguably not limited accordingly; this is consistent with both the language in the § 3101.1-2 regulation and section 6 of the standard lease form in use since 1984.[391] Moreover, there is no indication in Onshore Order Number 1 that the heightened clear and convincing evidence standard presented in IM 92-67 and BLM Manual MS-3101 is applicable for determining reasonable measures.[392]

Onshore Order Number 1 also specifies several general operating requirements. It provides that “[t]he operator must conduct operations to minimize adverse effects to surface and subsurface resources, prevent unnecessary surface disturbance, and conform with currently available technology and practice.”[393] Furthermore, “[t]he operator must comply with the provisions of the approved APD and applicable laws, regulations, Orders, and Notices to Lessees, including but not limited to [several specified provisions, including provisions related to cultural and historic resources, ESA compliance, and surface protection].”[394]

While the current version of Onshore Order Number 1 has only been in place since March 2007, as noted, it has been in place in some form since October 1983.[395] Thus, the roughly 36,000 leases issued since 1983 are subject to this formal order in one of its previous versions (see Table 1). As claimed elsewhere, it is not clear that the newest version of Onshore Order Number 1 would necessarily be inconsistent with lease rights granted in older leases since those older leases contain at least somewhat expansive reservations of authority allowing actions to be taken to protect the environment and other resources.[396]

c. Notices to Lessees

Another kind of formal order that is recognized is the notice to lessee (NTL). The BLM authorized officer may issue an NTL “when necessary to implement the onshore oil and gas orders and the regulations in this part.”[397] NTLs “implement the regulations in [part 3160] and operating orders, and serve as instructions on specific item(s) of importance within a State, District, or Area.”[398]

There are three operable NTLs in Wyoming, which are posted on BLM’s website.[399] One of these addresses flow meters,[400] another deals with reporting “undesirable events,”[401] and the last deals with royalties from lost oil and gas.[402] The flow meter NTL is applicable in Wyoming and the other two NTLs apply nationwide.[403] According to BLM personnel, there is a trend to convert NTLs to onshore oil and gas orders and many are only applicable in a particular state.[404]

d. The BLM Manual and Handbook

BLM also has an agency manual and handbook.[405] The BLM manual “provides policy, procedures, and instructions to manage programs.”[406]
The BLM handbook is a “source of detailed instructions for performing specialized procedures to carry out policy and direction described in the Manual Section.”[407] According to the BLM handbook, “[H]andbooks are considered part of the Manual.”[408] It is debatable whether the provisions in the manual and handbook constitute formal orders since they are not developed pursuant to the formal notice-and-comment rulemaking procedures specified by the Administrative Procedure Act,[409] however there is no doubt these internal sources of guidance play a major role in BLM’s day-to-day decision making.[410]

Potentially relevant manual sections that could constitute formal orders that a lease has been made subject to include but are not limited to the following: MS-1601 (land-use planning); MS-1703 (hazardous materials management and resource restoration); MS-3150 (onshore oil and gas geophysical exploration surface management requirements); MS-6840 (special status species management); and MS-8110, -8130, -8140, and -8150 (relating to various aspects of cultural resources management).[411] Potentially relevant handbook sections include but are not limited to H-1601-1 (land-use planning), H-1740-2 (integrated vegetation management), H-1790-1 (NEPA), H-3070-2 (economic evaluation of oil and gas properties), H-3101-1 (issuance of leases), H-3110-1 (noncompetitive leases), H-3150-1 (onshore oil and gas geophysical exploration surface management requirements), and H-3203-1 (leasing terms).[412]

In the interest of space, I will make no effort to review all of the provisions in this guidance. This would be a daunting task, and it might well be virtually impossible to determine what versions of these documents were in place at various times in the past. However, there are potentially a number of relevant provisions that could constitute formal orders, perhaps most significantly those found in the handbook section entitled “Planning for Fluid Minerals Resources.”[413] The provisions in BLM Manual MS-3101, relating to issuance of leases, are also relevant and some have been discussed.[414]

e. BLM Instruction Memoranda

In addition to manual and handbook provisions, BLM also has an extensive library of “Instruction Memoranda” (IMs), which may also be formal orders that a lease is subject to, at least if the lease was issued since 1984 when the “formal orders” language was adopted in the standard lease form. IMs “are temporary directives that supplement the Bureau Manual Sections.”[415] The BLM website presents IMs that have been issued since 1999.[416] Generally they are directives from the BLM Director to BLM state directors and field office officials, although state offices may also issue IMs.[417] Most, if not all, IMs have associated expiration dates,[418] so it is debatable whether they have continuing force after they expire, even if the IM was in force when a lease was issued. But BLM sometimes continues to treat IMs as effective after they have nominally expired.[419] At this time,
IMs 2009-225, 2009-078, 2009-044, and 2009-011 are operational at a minimum (all expire on September 30, 2010).[420] These IMs address a range of topics including oil and gas inspection and enforcement strategies,[421] processing APDs that employ directional drilling from well pads on nonfederal lands,[422] the use of categorical exclusions from NEPA compliance for geophysical exploration,[423] and assessment and mitigation of impacts to paleontological resources.[424] Many other nominally expired IMs relate to oil and gas development.[425]

f. The BLM “Gold Book”

An additional BLM document that could constitute a formal order is The Gold Book (actually entitled Surface Operating Standards and Guidelines for Oil and Gas Exploration and Development: The Gold Book).[426] While this document also has not been adopted through formal notice-and-comment rulemaking, it is an important source of information and guidance for BLM decision making regarding operations on an oil and gas lease.[427] It is essentially a user-friendly companion to Onshore Oil and Gas Order Number 1.

The Gold Book provides a wide array of guidance (and requirements) relative to all phases of oil and gas development operations. It was “developed to assist operators by providing information on the requirements for obtaining permit approval and conducting environmentally responsible oil and gas operations on Federal lands.”[428] It defines “Best Management Practices” as measures that “minimiz[e] undesirable impacts to the environment” and promotes the use of best management practices to achieve this end.[429] The Gold Book states that “[c]onstraints . . . may be imposed on the location of access roads, well sites, and facility sites or the timing of geophysical exploration, well drilling, or other operations” and “may result from lease stipulations, the surface management agency’s review and environmental analysis of the proposed operations, Notices to Lessees, Onshore Orders, or regulations.”[430] The Gold Book specifies that environmental concerns might be addressed through conditions of approval or best management practices that result from a site-specific analysis.[431] Thus, design and construction techniques for well sites should “minimize surface disturbance and the associated effects of proposed operations and maintain the reclamation potential of the site.”[432] There are a number of specific considerations related to construction of well sites, reserve pits, roads and access ways, and drainage and drainage structures.[433] Guidance for drilling and production operations is also specified, as “[o]nshore oil and gas lease operations are subject to applicable laws, regulations, lease terms, the [APD], APD conditions of approval, Onshore Oil and Gas Orders, Notices to Lessees, and orders and instructions of the authorized officer.”[434]
These obligations aim to ensure that the conduct of operations protects “natural resources, environmental quality, life, and property.”[435] Maximizing oil and gas recovery with minimum adverse effect on the environment is “[t]he primary objective.”[436] To achieve these objectives, The Gold Book details measures for disposal of produced water, pollution control and hazardous waste management, noise control, protection of visual and scenic resources, and even how facilities should be painted.[437] The Gold Book also specifies reclamation measures.[438]

g. Presidential Executive Orders

Executive Orders (EOs) issued by the President of the United States are official documents by which the President manages the operations of the executive branch. A number of these relate to obligations of the federal government to protect the natural environment. There is no doubt they are formal orders that many leases are subject to.

A few of the active EOs indicate the extent to which BLM retains rights in areas that have been leased for oil and gas development. President Carter issued EOs 11,990 and 11,988 in 1977 to guide and establish requirements for federal protection of floodplains and wetlands.[439] EO 12,088, issued by President Carter in 1978, provides that “[t]he head of each Executive agency is responsible for ensuring that all necessary actions are taken for the prevention, control, and abatement of environmental pollution with respect to Federal facilities and activities under the control of the agency.”[440] President Nixon issued EO 11,593 in 1971 to guide and establish obligations for the protection of cultural and historical resources.[441] EO 13,186, issued by President Clinton in 2001, provides for the conservation of migratory birds.[442]

In addition to EOs aimed at protecting the natural environment, there are EOs that address energy development. President George W. Bush issued EO 13,211 in 2001 to require the preparation of a Statement of Energy Effects for federal regulatory actions that can have significant adverse effects on the supply, distribution, or use of energy.[443] EO 13,212, also issued by President Bush in 2001, requires federal agencies to expedite permitting of energy projects.[444] It states, “For energy-related projects, agencies shall expedite their review of permits or take other actions as necessary to accelerate the completion of such projects, while maintaining safety, public health, and environmental protections.”[445] These directives to further energy production have not eliminated requirements to protect the natural environment when federal oil and gas leases are developed.

h. Solicitor Opinions and Secretarial Orders

Finally, two additional types of formal orders that a lease may be subject to are opinions of the Solicitor of the U.S. Department of the Interior and orders issued by the Secretary of the Interior. A list of, and access to, many of these opinions and orders can be found online.[446] On January 6, 2010, Secretary of the Interior Ken Salazar issued Secretarial Order 3294, which established an Energy Reform Team in the Department of the Interior that will oversee evaluation and reform of Department energy policies.[447] Part and parcel of this reform effort was the establishment of new policies regarding onshore oil and gas leasing under the management of BLM. This includes a requirement for “Master Leasing and Development Plans” prior to leasing in areas where intensive new oil and gas development is anticipated, and increased environmental review of lease parcels leading to identification of mitigation measures.[448] This new policy direction could lead to substantial changes in BLM’s oil and gas program and to issues related to BLM’s assertion of its retained rights. This new direction will be discussed further in Part VIII.B.

E. Reasonable Measures

“Reasonable measures” is the last of the several conditions that a BLM oil and gas lease is subject to. This option for ensuring environmental protection when operations are proposed on a lease, which is provided for by both the § 3101.1-2 regulation and section 6 of the modern lease form, has been discussed in some detail above.[449] BLM can require reasonable measures to minimize adverse effects to the environment that include, but are not limited to, modifying the siting and design of facilities, timing of operations, and specifying interim and final reclamation measures, so long as the reasonable measures are consistent with the lease rights granted.[450]

As is apparent from this lengthy discussion of legal authorities,
BLM has substantial retained rights under the lease contract that allow it to protect the natural environment when lease development is proposed.
But furthermore, in addition to what is apparent from this analysis, basic principles of contract law may also help define or illuminate BLM’s retained rights. These principles will be considered next.

VI. General Principles of Contract Law Will Help Define BLM’s
Retained Rights

  1. Court Decisions Related to Federal Oil and Gas Leases Have Relied on General Principles of Contract Law

Courts evaluating the federal government’s rights and duties under federal oil and gas leases have considered basic principles of contract law. Consequently, it is appropriate to not only consider the provisions and legal authorities lease contracts are specifically subject to when determining BLM’s retained rights in leased land, but to also consider more general contract law principles. There is, of course, a large body of law that has been developed around contracts.

In Mobil Oil Exploration and Producing Southeast, Inc. v. United States (Mobil Oil),[451] the United States Supreme Court considered oil and gas leases off the North Carolina coast that were issued pursuant to the Outer Continental Shelf Leasing Act (OCSLA) and held that repudiation of the leases occurred when the federal government refused to take a required action (approval of an exploration plan) within a specified timeline.[452]
The Court noted, “[W]hen the United States enters into contract relations, its rights and duties therein are governed generally by the law applicable to contracts between private individuals.”[453] Based on this, the Court looked to the Restatement (Second) of Contracts for a definition of when repudiation and breach of contract occurs, and also stated that “[t]he Restatement of Contracts reflects many of the principles of contract law that are applicable to this action.”[454] Mobil Oil will be considered further in Part VII.B.

Similarly, in another offshore leasing case that dealt with OCSLA leases off the California coast, Amber Resources Co. v. United States,[455] the United States Court of Appeals for the Federal Circuit ruled that the government had breached the lease contracts when it altered the terms of suspensions.[456] Again, the court looked to the Restatement (Second) of Contracts for guidance on when repudiation and breach occurs. The court relied on the Supreme Court’s analysis in Mobil Oil to reach its conclusion.[457]

In considering state law claims related to assignments of leases and royalty interests based on BLM onshore oil and gas leases, the District Court in Wyoming determined that reservation language should be examined
“in accordance with the general principles of contract interpretation.”[458] Relying on Wyoming Supreme Court precedent, the court determined the prime focus should be on the intent of the parties and where the language of a contract is unambiguous, intent should be gathered from the contract itself, although the context within which the document was written can be considered.[459] If contract language is ambiguous, extrinsic evidence can
be considered.[460]

Another case originating in Wyoming stemmed from BLM decisions to suspend oil and gas leases in an area with rich trona deposits so that trona mining could occur prior to oil and gas development.[461] The United States Court of Federal Claims observed that when determining whether the suit was timely filed, repudiation of a contract occurs when the government announces it will not perform contractual obligations and a breach of contract occurs when the government actually fails to honor its obligations or when the promisee brings suit in the face of a repudiation.[462]

Given this precedent it is appropriate to consider underlying principles of contract law that might help define the scope and nature of obligations under a federal onshore oil and gas lease, and thus BLM’s retained rights and duties pursuant to a lease. This will be done next by briefly considering some of the relevant guidance in the Restatement (Second) of Contracts and American Jurisprudence 2d Contracts.

B. Contract Principles Presented in the Restatement of Contracts and American Jurisprudence

The initial question in construction of a contract is a determination of whether the contract is ambiguous.[463] Contract language is unambiguous when it has a “definite and precise meaning,” and if the contract is unambiguous “the rules governing the interpretation of ambiguous contracts do not come into play.”[464] The meaning of an unambiguous contract is determined without reference to extrinsic facts or aids and “it must be enforced as written.”[465] Ambiguity is determined objectively through the eyes of a reasonably intelligent person, considering the entire written agreement.[466] Ambiguity is not created just because a contract will work hardship on one party, or the parties disagree over the meaning of a contract, or urge varying interpretations.[467] Ambiguity must emanate from the language used in the contract, “rather than from one party’s subjective perception of its terms.”[468]

Where there is ambiguity, the intention of the parties to the contract will be sought; “the fundamental and cardinal rule in the construction or interpretation of contracts is that the intention of the parties is to be ascertained.”[469] If the contract is not ambiguous, intent is determined from the language used in the contract.[470] The intention or meaning of a contract can be conveyed by implication if such is plainly required by the language in the contract.[471]

Other principles of contract law can also affect construction and interpretation. Ambiguous language is interpreted most strongly against the drafting party, which is certainly BLM when it comes to onshore oil and gas leases.[472] However, in contracts where the government enters into the contract on behalf of the public, the contract is liberally construed in favor of the government.[473] There is an implied covenant of good faith and fair dealing in every contract, but this duty does not alter a contract’s express provisions.[474] Parties to a contract are presumed to contract with reference to existing law.[475] Existing law is made part of the contract, but subsequent law is not made part of a contract unless there is clear expression in the contract to do so.[476]

A federal onshore oil and gas lease is, undoubtedly, a written, integrated agreement between the government and the lessee.[477] Thus, the language used in the lease will likely determine which rights to condition development are retained by BLM, an issue which has been discussed at length elsewhere. The language in a federal onshore oil and gas lease is arguably unambiguous, so interpretation of what rights BLM retains will likely be based on consideration of that language and not extrinsic evidence. But that of course could be subject to debate; a claim might be made in a particular circumstance that ambiguity exists and extrinsic evidence needs to be considered to interpret the contract.

The intent of the parties to a BLM oil and gas lease is to allow for, and even promote, oil and gas development on public lands.[478] Modern versions of the lease form state, “This lease is issued granting the exclusive right to drill for, mine, extract, remove and dispose of all the oil and gas (except helium) in the lands described . . . together with the right to build and maintain necessary improvements thereupon.”[479] The three older versions of the lease form make a nearly equivalent grant.[480] Yet, in the next sentence following this grant, modern versions of the lease state “[r]ights granted are subject to” the authorities discussed above at length—applicable laws;
lease terms, conditions, and stipulations; regulations and formal orders in place when the lease is issued; and regulations and formal orders issued afterward if not inconsistent with the lease rights granted.[481] The § 3101.1-2 regulation adds to this list.[482] And while older versions of the lease form may be less explicit, they nevertheless provide that “lessee agrees” to take reasonable steps to prevent certain specified types of environmental damage, “lessor reserves” certain rights, and that “it is agreed” that the rate of prospecting and development and the quantity and rate of production are subject to control in the public interest by the Secretary of the Interior.[483]

Parties to an onshore federal oil and gas lease intend to allow for oil and gas resource development; however, they also understand that, or should understand that, any such development is conditional.[484] Consequently, when general principles of contract law are considered, it is apparent that BLM has significant retained rights under a lease allowing it to condition development to protect the natural environment. The provision in section 6 of the modern version of the standard lease form, stating that BLM can specify reasonable measures to minimize adverse impacts to resources, is perhaps the provision that is most likely to be challenged as ambiguous. However, the language that appears in section 6 of the October 2008 standard lease form states that the “[l]essee must take reasonable measures deemed necessary by lessor to accomplish the intent of this section.”[485]
The intent specified is to “conduct operations in a manner that minimizes adverse impacts” to various resources, and it is stated that reasonable measures “include, but are not limited to, modification to siting or design of facilities, timing of operations, and specification of interim and final reclamation measures” so long as consistent with the lease rights granted.[486] Therefore, it would appear that reasonable measures could include any measures that BLM might require so long as they did not take away the exclusive right to remove all of the oil and gas on a leasehold or prohibit the construction of necessary improvements. Any condition short of this appears to be within BLM’s discretion and within the meaning of the term reasonable measures as used in the standard lease form. In Yates Petroleum Corp.,[487] the Interior Board of Land Appeals (IBLA) rejected an attempt to limit BLM’s imposition of reasonable measures to nothing more stringent than those mentioned in the 200-meter 60-day rule and recognized BLM could restrict the siting or timing of lease activities.[488] Thus, a highly constrained interpretation of what constitutes reasonable measures likely will not succeed, especially in light of the general contract principle that when the government enters into a contract on behalf of the public, then the contract is construed in favor of the public.[489]

VII. Potential Limitations on BLM’s Ability to Exercise Its
Retained Rights

I have discussed in detail the authorities that support BLM’s assertion of considerable retained rights in areas it has leased for oil and gas development, allowing it to protect the natural environment through the exercise or implementation of those retained rights. But of course, this is not a one-way street, and consideration must be given to contrary authority that could limit the exercise of any asserted retained rights. Some of these possible contrary authorities will be considered in this section.

A. The Lessee Has Been Granted the Right to Use as Much of the Leased Lands as Is Necessary to Remove All of the Oil and Gas and the Right to Build Necessary Improvements

Modern versions of the lease form in use since 1984 grant the exclusive right to remove all of the oil and gas on a leasehold and the right to build and maintain necessary improvements thereupon.[490] The § 3101.1-2 regulation supplements this grant by providing that “[a] lessee shall have the right to use so much of the leased lands as is necessary to [remove] all the leased resource in a leasehold.”[491] As discussed, under the modern lease forms and the § 3101.1-2 regulation three rights have been granted: 1) the exclusive right to use the leasehold for the removal of all oil and gas; 2) the right to “use” as much of the leasehold as is “necessary” to remove “all” of the oil and gas; and 3) a right to build “necessary” improvements.[492] The three older versions of the lease grant similar rights, but these lease forms were in use prior to promulgation of the § 3101.1-2 regulation in 1988. The 1954, 1965, and 1971 versions of the lease form all provide that the lessee is granted the “exclusive right and privilege to [remove] all the oil and gas . . . in the lands leased, together with the right to construct and maintain [structures] necessary to the full enjoyment thereof.”[493]

In considering whether these granted rights might limit BLM’s ability to assert retained rights to limit or guide development, it seems unlikely there will often be dispute that a particular lessee has the exclusive right to access the oil and gas on a leasehold. Thus, the more critical questions likely relate to what actions might be “necessary” for the use of the leasehold for the removal of all the oil and gas, and what might constitute “necessary” improvements.

The right to do what is necessary to access all of the oil and gas that may be found on a lease and the right to build and maintain necessary improvements should not be viewed as granting an unfettered right to do anything the lessee may desire to extract the oil and gas. The word “necessary” gathers meaning from the connection in which it is used.[494] It can mean absolute physical necessity or inevitability, or it can mean only that which is “convenient, useful, appropriate, suitable, proper, or conducive to the end sought.”[495] This latter construction probably defines the word “necessary” in the context of BLM’s standard lease form and the § 3101.1-2 regulation given the significant conditions the lease is subject to.

The connection in which the word “necessary” is used includes the provision in the next sentence of the modern lease forms that makes the rights granted subject to applicable laws; the terms, conditions, and stipulations found in the lease; regulations and formal orders in place when the lease is issued; and regulations and formal orders issued afterward if not inconsistent with the lease rights granted.[496] The § 3101.1-2 regulation adds to or elaborates on this list by providing that the rights granted are subject to stipulations attached to the lease; specific, nondiscretionary statutes; and “such reasonable measures as may be required by the authorized officer to minimize adverse impacts.”[497] Therefore, the context of any rights granted is that they have been made conditional on compliance with an array of external authorities, and what is “necessary” should be interpreted in this context. As discussed in detail above, many of these external sources of authority that have been incorporated into the lease include mandatory obligations to protect the environment that are imposed on BLM, the lessee, or both.[498]

Accordingly, the term “necessary” should not be viewed as strongly limiting BLM’s retained rights. Lessees can take actions to access the oil and gas and to build related improvements only to the extent these activities can be conducted in a manner that is in compliance with the substantial reservations of authority found in the lease. What is necessary is better viewed as being defined by actions that are “appropriate” or “proper” in light of what the rights granted are subject to rather than an absolute right to pursue any activity that is desired by the lessee.[499]

B. Breach and Repudiation of Contract Claims

Perhaps the ultimate limit on efforts by BLM to exert its retained rights would be a successful claim by a lessee asserting BLM had repudiated the lease contract or breached it through the actions it took, with attendant monetary damages awarded. A repudiation of a contract occurs when there is a “statement by the obligor to the obligee indicating that the obligor will commit a breach that would of itself give the obligee a claim for damages for total breach” or “a voluntary affirmative act which renders the obligor unable or apparently unable to perform without such a breach.”[500] A total breach is defined as a breach that “so substantially impairs the value of the contract to the injured party at the time of the breach that it is just in the circumstances to allow him to recover damages based on all his remaining rights to performance.”[501]

Probably the most significant case that has considered the issue of repudiation and breach of contract in the context of federal oil and gas leases was Mobil Oil, although it considered offshore leases issued pursuant to the OCSLA, not onshore Mineral Leasing Act leases. In Mobil Oil the government entered into lease contracts with the petitioners for oil exploration and development off the coast of North Carolina.[502] Due to provisions in the later-enacted Outer Banks Protection Act (OBPA)[503] that prohibited approval of required exploration, development, and production plans until specified new requirements were met, the government refused to approve an exploration plan within a specified timeline and placed the leases in suspension.[504] On these facts the Supreme Court ruled a repudiation of contract had occurred and awarded the petitioners compensation.[505]
The Court’s analysis provides guidance as to when repudiation or breach of a federal oil and gas lease contract might be deemed to occur.

The contracts at issue in Mobil Oil provided the leases were “subject to” several statutory and regulatory provisions, and the Court recognized that these provisions “in effect were incorporated into the contracts.”[506] However, the Court refused to allow the later-enacted OBPA to control these leases, because it determined the OBPA was not a statute the leases were made subject to.[507] Besides the fact that the OBPA was not a statute referenced in the lease contracts, the Court also determined that the “catchall provision” specifying the leases were subject to applicable statutes and regulations did not extend to the later-enacted OBPA and the leases were not subject to the later-enacted OBPA.[508] The Court found that without a contractual limitation on the government’s ability to impose “new and different requirements,” such as those in the newly-enacted OBPA, the companies would have received “next to nothing” when they entered into the leases.[509]

Mobil Oil teaches that care must be exercised in attempting to incorporate later-adopted regulations and statutes into a lease. The provision in modern leases that the lease is made subject to applicable laws likely includes only laws in existence when the lease is issued. The only regulations that a lease may be subject to, whether in existence at lease formation or adopted afterward, are “the Secretary of the Interior’s regulations and formal orders” as specifically provided for in the modern lease forms.[510] Nevertheless, Mobil Oil does not teach that BLM will be greatly limited in exercising its retained rights.

The Court in Mobil Oil recognized that the statutes and regulations referenced in the leases contained terms “which in effect were incorporated into the contracts” and that these “made clear that obtaining the necessary permissions [to conduct postlease activities] might not be an easy matter.”[511] Furthermore, the Court did not hold that later-adopted statutes or regulations could never be made part of a lease contract; it only held the leases created a promise not to impose new approval procedures and standards beyond those in the underlying statues and regulations in effect when the leases were executed and which had been specifically incorporated into the leases.[512] While acknowledging that the lease contracts “gave the companies rights to explore for, and to develop oil,” the Court also pointed out that

the need to obtain Government approvals so qualified the likely future enjoyment of the exploration and development rights that the contract,
in practice, amounted primarily to an opportunity to try to obtain exploration and development rights in accordance with the procedures and under the standards specified in the cross-referenced statutes and regulations.[513]

Under the facts in Mobil Oil, the Court determined this “gateway” had been significantly narrowed by the government’s actions and thus determined that a repudiation had occurred.[514] But if the government does not deviate significantly from the procedures and standards stated in the contract or incorporated into it when it is initially formed, a breach is unlikely to be found.

Given that 35,256 of the 48,342 currently active leases in the eleven western states have been issued since 1984 when the “applicable laws” language was introduced (see Table 1), that many of the “applicable laws” were adopted prior to 1980, and that BLM’s oil and gas operating regulations have been in place in nearly their present form since 1982 (and the relevant land use authorization regulations since 1981), it seems likely that most BLM oil and gas leases will survive claims that BLM actions pursuant to these authorities are a repudiation. More generally, so long as BLM takes care not to make leases worth “next to nothing,” its actions are unlikely to constitute a breach of contract. It must ensure that the gateway for seeking approval of activities on the lease is not so substantially narrowed that the legal regime that served as the basis for the bargained for right to explore for and extract oil and gas is lost or significantly altered. But given the significant number of conditions that an onshore lease is subject to, as in Mobil Oil, BLM oil and gas leases represent an opportunity to seek approval for development, not an unqualified right. As long as that opportunity is not entirely foreclosed BLM should be within its rights to demand protection of the environment, and no breach or repudiation of the contract would occur.

C. Reasonable Measures

The import of the term “reasonable measures,” which appears in section 6 of the modern lease forms as well as in the § 3101.1-2 regulation, was discussed above.[515] If a narrow view—such as that indicated in the
200-meter 60-day rule—were adopted, it could limit BLM’s ability to effectively assert its retained rights under an onshore oil and gas lease. But, as discussed,[516] a narrow interpretation seems unfounded. Section 6 of the modern lease form provides that reasonable measures are those “deemed necessary by lessor” and the regulation provides these measures are “as may be required by the authorized officer.”[517] Both the modern lease form and the § 3101.1-2 regulation state that reasonable measures within BLM’s discretion may include, but are not limited to, modification of the siting or design of facilities and timing of operations so long as they are consistent with the lease rights granted.[518] Moreover, the § 3101.1-2 regulation provides that the limits stated in the 200-meter 60-day rule are “[a]t a minimum” of what is consistent with lease rights.[519] Consequently, it seems unlikely that the discretion to impose reasonable measures on lease operations would be construed in such a narrow manner as to greatly limit BLM’s retained rights to condition development. This view is supported by recent IBLA precedent.[520]

D. Courts Have Found BLM Cannot Completely Prohibit Development
When It Issues a Non-No Surface Occupancy Lease, Which Represents
an Irreversible and Irretrievable Commitment of Resources That
Requires Compliance with NEPA

The federal courts have held that when BLM and the Forest Service engage in oil and gas leasing activities that do not preclude surface disturbance, they make an irreversible and irretrievable commitment of resources that triggers NEPA requirements because the government has committed itself to allowing some level of disturbance.[521] The leases at issue have not provided for “no surface occupancy;” the leases have been “non‑NSO” leases.[522] This view of the nature of an oil and gas lease could limit BLM’s ability to exercise its retained rights because the vast majority of federal onshore leases are non-NSO.

In Sierra Club v. Peterson, concerning a BLM and Forest Service leasing action on roadless lands in the Targhee and Bridger-Teton National Forests in Idaho and Wyoming, the D.C. Circuit determined that, with respect to the non-NSO leases that were challenged, “[e]ven assuming, arguendo, that all lease stipulations are fully enforceable, once the land is leased the Department no longer has the authority to preclude surface disturbing activities even if the environmental impact of such activity is significant.”[523] Consequently, preparation of an EIS was necessary to support the leasing decision.[524] In Conner v. Burford, involving leasing on Forest Service lands with important wildlife and natural values in Montana, the Ninth Circuit determined that the sale of non-NSO leases “constitutes the point of commitment; after the lease is sold the government no longer has the ability to prohibit potentially significant inroads on the environment.”[525] So, again, preparation of an EIS was necessary prior to leasing.[526] In Bob Marshall Alliance v. Hodel, the Ninth Circuit reached the same conclusion with respect to leasing on “wild, mountainous terrain” in the Lewis and Clark National Forest in Montana.[527]

More recently, in Northern Alaska Environmental Center v. Kempthorne (Northern Alaska),[528] involving the National Petroleum Reserve in Alaska, the Ninth Circuit again ruled that leasing represented an irretrievable commitment of resources and thus required preparation of an EIS.[529] But in this case, the court held that a parcel-by-parcel NEPA analysis was not required because impacts were unidentifiable at the leasing stage on a parcel-by-parcel basis.[530] The United States Court of Appeals for the
Tenth Circuit, in New Mexico ex rel. Richardson v. BLM,[531] also concluded that issuing an oil and gas lease without an NSO stipulation in a biologically diverse Chihuahuan Desert grassland can constitute an irretrievable commitment of resources and thus require site-specific NEPA analysis prior to lease issuance. The court recognized that “[b]ecause BLM could not prevent the impacts resulting from surface use after a lease issued, it was required to analyze any foreseeable impacts of such use before committing the resources.”[532] The IBLA has reached the same conclusions.[533]

While these cases have clearly determined that when BLM issues leases that do not include an NSO stipulation it has committed itself to allowing some level of development, these rulings probably will not greatly limit BLM’s ability to exercise its retained rights to protect the natural environment. In the majority of these cases, the leasing decisions implicated many lease parcels and thousand of acreas of public land were at issue.[534] The question before these courts was whether an EIS was needed before this far-reaching action could be taken when the leases did not preclude surface occupancy.[535] The courts concluded that an EIS was required if the leases being issued were non-NSO because the courts did not believe any reservation of authority was sufficient to assure impacts would be insignificant for purposes of NEPA over the the numerous lease parcels and large areas at issue.[536] But this determination of the need for NEPA compliance when a Federal leasing action affects public land does not necessarily stand for the proposition that BLM cannot limit development as needed on specific lease parcels. In fact, in most of these cases the courts recognized that BLM still retained rights to protect the environment, even if development could not be entirely precluded on all leases.[537]

In Sierra Club the court recognized that mitigation measures could be required, but because surface disturbance could not be absolutely precluded, it determined BLM needed to prepare an EIS.[538] In Conner, the court recognized that reasonable regulation of surface-disturbing activities was allowed but again determined this did not assure impacts would be reduced to insignificance for purposes of NEPA, and it therefore required an EIS to be prepared at the leasing stage.[539] In Northern Alaska the court concluded that, although surface disturbance could not be precluded,
“[t]he government can condition permits for drilling on implementation of environmentally protective measures, and we assume it can deny a specific application altogether if a particularly sensitive area is sought to be developed and mitigation measures are not available.”[540]

The extent of BLM’s retained rights in the context of non-NSO leases garnered discussion in a challenge to BLM and Forest Service compliance with the ESA at the leasing stage in Wyoming Outdoor Council v. Bosworth.[541] In Wyoming Outdoor Council the district court found that when the reservations of authority in the § 3101.1-2 regulation as well as the requirements related to APDs and the need for NEPA compliance at the APD stage were considered, “these reservations and procedural hurdles demonstrate that while the lessee clearly has a legal right to apply for permission to conduct oil and gas operations, his right to development of the lease parcel is far from certain.”[542] Thus, while there may be a need to prepare an EIS at the leasing stage so as to comply with NEPA, especially when numerous parcels or large areas are approved for lease sales and development cannot be absolutely precluded on all the leases, BLM still retains substantial rights to condition development on particular parcels, up to and including the prohibition of development in some circumstances.

E. Takings Claims

I have interacted with a number of BLM field personnel throughout Wyoming on a number of oil and gas projects. In response to a suggestion to assert BLM’s retained rights, BLM field personnel have sometimes commented that such action could be challenged as an illegal “taking” and BLM is limited in its rights due to this perceived barrier. The U.S. Constitution provides that “no private property be taken for public use, without
just compensation.”[543] This prohibition on the federal government “taking” property without just compensation is, however, unlikely to be a basis for successfully asserting legal claims against the government if it asserts its retained rights under an oil and gas lease.

Generally speaking, if claims were made against the government if it asserted its retained rights, those claims would likely have to be based on breach of contract claims, not constitutional takings claims. In a case challenging BLM actions related to onshore oil and gas leases issued in Wyoming, the Federal Court of Claims observed that “the concept of a taking as a compensable claim theory has limited application to the relative rights of party litigants when those rights have been voluntarily created by contract.”[544] “Ordinarily, the government’s interference with contractual rights arising under a contract with the government will give rise to a breach of contract action rather than a taking claim.”[545] And, as discussed, when the Supreme Court considered challenges to the government’s actions affecting offshore leases in Mobil Oil, the Court addressed the matter as a question of contract law, not constitutional law.[546]

Despite this general principal, concurrent takings claims can be pursued if the property right that is asserted is not governed by the terms of the contract.[547] Thus, while it is unlikely that takings claims will generally have viability because the standard lease contract has reduced the parties’ agreement to writing, it is possible a takings claim might be viable if the lessee can identify a property interest that has been interfered with that is not governed by the contract. But such claims would seem to have a remote chance of widespread success given the apparent comprehensive nature of BLM oil and gas leases.[548] To the extent a regulatory taking claim was successfully advanced, the Supreme Court has developed an extensive body of law specifying what is required to establish that a Fifth Amendment regulatory taking has occurred.[549]

F. Lessees Must Exercise Diligence to Develop Leases

Under section 4 of the modern lease forms, the lessee “must exercise reasonable diligence in developing and producing.”[550] Under section 2(j) of the 1954, 1965, and 1971 lease forms, the lessee agrees “[t]o exercise reasonable diligence in drilling and producing the wells herein provided for.”[551] The Mineral Leasing Act also requires reasonable diligence in the operation of leased property.[552] Moreover, a lessee can be required to develop wells “in accordance with good economic operating practices” and must ensure that drainage of oil and gas from a lease is not occurring due to development on adjacent leases.[553]

It is conceivable that these obligations to pursue production could limit or at least get in the way of BLM’s asserting retained rights to protect the natural environment. Nevertheless, these provisions do not specifically limit BLM’s retained rights or modify other obligations BLM operates under, so in all likelihood these requirements will have little impact on BLM’s exercise of its retained rights. And if development is essentially mandated or if BLM perceives a need to require development, it is more likely that BLM will be forced to assert its retained rights because development might occur in areas where there was otherwise less interest in pursuing development.

G. Split Estate Issues

BLM manages approximately 58 million acres of land where the surface is privately owned but the federal government owns the rights to the minerals underlying the land.[554] These lands are called split estates.[555]
While BLM operates under many of the same legal requirements on split estate lands as it does on lands wholly owned by the federal government (the oil and gas lease forms used on split estates do not differ from those used in other situations), and enjoys many of the same legal rights, the simple fact that the surface is privately owned—often by a rancher or farmer whose family has lived on the land for several generations—could affect how BLM asserts its retained rights.[556]

BLM guidance provides that it must fulfill the requirements of NEPA, the National Historic Preservation Act, the ESA, the Clean Water Act, and “other applicable laws” when it engages in permitting on split estates.[557]
The guidance states that during permit review, BLM “offers the surface owner the same level of resource protection provided on federally owned surface.”[558] Additionally, BLM will also invite the surface owner to on-site inspections, seek the owner’s input on development and reclamation issues, carefully consider the surface owner’s views and the effects on the surface owner’s use of the land “before determining mitigation requirements and approving operations,” and carefully consider the surface owner’s views on reclamation requirements and seek concurrence that final reclamation is satisfactory.[559] Consequently, while BLM enjoys the same retained rights on split estates that it enjoys elsewhere and may well exercise those rights, it is equally clear that the private surface owner will exert a strong influence over the measures that BLM prescribes. Overall, it is probably unlikely that BLM will require lesser environmental protections on split estate lands than on wholly federally owned lands, but it is possible that its approach to exerting its retained rights will differ on split estate lands.

VIII. Means by Which BLM Can Exercise Its Retained Rights

In this Part, I will briefly describe some of the means by which BLM could exercise its retained rights on federal onshore oil and gas leases. This will not be an exhaustive review; the goal is only to give the reader a sense of the options that are available to BLM to protect the natural environment. Undoubtedly more options exist than those that will be discussed. I will also present several policy changes BLM might consider that would make it better able to exercise its retained rights.

A. Options Available for Regulating Oil and Gas Development on the Public Lands That Would Help Protect the Natural Environment

BLM has substantial authority to regulate the time, place, and manner of oil and gas development.[560] It can regulate the siting of development, the design of facilities, and the timing of operations.[561] It can specify the rates of oil and gas development and production.[562] There is no doubt BLM can specify the conditions of oil and gas development on a federal onshore lease to a considerable degree.

One of the most important means by which environmental values can be protected is by requiring phased or paced development in environmentally sensitive areas. This is an “obvious” way to manage oil and gas development, according to the IBLA.[563] In Montana, the federal district court found that an EIS that had not considered phased development for coal bed methane development in Montana’s portion of the Powder River Basin failed to meet the requirements of NEPA.[564] Using this approach BLM can ensure that development activities are staggered over time, or take place in prescribed areas, until reclamation and other measures of environmental recovery indicate development can proceed in other areas.

Another important means to achieve environmental protection is to require clustered development and the related measure of directional drilling. Directional drilling, also called horizontal, deviated, or slant drilling, allows for hydrocarbon deposits that are not directly under a well pad to be accessed.[565] Using this technology, it is possible to concentrate wells on a more limited number of well pads yet still reach the oil and gas, which reduces the environmental impacts of drilling.[566] The technology and practicality of directional drilling is improving and at this point hydrocarbon deposits several thousand feet, and even more, from a well pad can be reached.[567] On the Pinedale Anticline natural gas field in western Wyoming, directional drilling will allow for thirty-two wells to be drilled from a single, consolidated well pad.[568]

Lease suspension is another means at BLM’s disposal to ensure environmental protection is achieved in leased areas. As has been discussed, both the Mineral Leasing Act and BLM’s supporting regulations allow BLM to suspend lease operations “in the interest of conservation,” as do terms in BLM’s leases.[569] One court has held that “suspending operations to avoid environmental harm is definitely a suspension in the interest of conservation in the ordinary sense of the word.”[570] Suspending leases so as to protect the natural environment is a recognized means to protect the natural environment, having been employed by BLM in the Jack Morrow Hills and Pinedale Anticline areas in Wyoming, for example.[571]

Another mechanism that could be utilized to protect environmentally sensitive areas is unitization of leases. When a group of leases are “unitized,” the leases can be maintained in force through the drilling and operation of a few, or even one, well which reduces pressure on lessees to drill or produce on their individual leases so as to maintain them in effect.[572] More efficient management is possible when a group of leases are managed collectively (unitized) rather than individually. Unitization can allow for lease holders to enjoy the benefits of a lease while achieving protection of sensitive areas. Pursuing unitization allows for orderly development with less infrastructure and disturbance, while helping to eliminate concerns such as those related to drainage of oil and gas from a lease, which sometimes creates pressure to develop a lease. BLM has authority to require unitization pursuant to section 4 of the modern leases.[573] The 1954, 1965, and 1971 leases also allow for unitization to be required.[574]

BLM can exert its retained rights by other means, including the imposition of reasonable measures,[575] conditions of approval,[576] best management practices (BMPs),[577] and the retention and enforcement of lease stipulations.[578] These conditions could affect an array of practices related to the time, place, or manner of oil and gas development. Examples include limiting the size of well pads, requiring “closed-loop” drilling fluid systems to control hazardous chemicals, using remote (computerized) means to monitor well conditions, requiring carpooling and other traffic reduction measures, requiring “liquids gathering systems” (piping hydrocarbons and perhaps produced water from scattered well locations to a centralized gathering facility so as to reduce activity at individual wells),[579] and requiring netting to be placed over “reserve” (waste) pits so as to protect birds, bats, and other wildlife. A number of additional measures could be added to this list, including, but not limited to, requiring “green completions” to reduce air pollution when wells are brought into production following drilling, dust control measures, the use of protective mats to reduce surface disturbance when drilling is occurring, using existing roads and minimizing the level of road construction used to access well pads, and reinjecting produced water rather than disposing of it on the surface. Assuring effective reclamation with native plant species (especially shrubs such as sagebrush (Artemesia)) is also important. BLM has developed a website devoted to BMPs, and these measures should be vigorously employed.[580] The University of Colorado Law School has also developed a website devoted to BMPs applicable to oil and gas development and these too can be employed.[581]

One of the most important means by which BLM can protect the natural environment is to ensure that stipulations oriented toward the protection of wildlife and other resources are not abandoned and are, in fact, vigorously enforced. In Wyoming, BLM has shown an increasing tendency to eliminate these important protections, to grant exceptions and waivers to them,
or both.[582] This is an unfortunate trend that should not be perpetuated if protection of other resources is desired.[583]

Other options that could be considered by BLM when operations are proposed in sensitive areas include pursuing lease buyout and trade. Lease buyout likely would require the approval of Congress, not to mention congressional authorization of funding, but lease trades could be pursued administratively by BLM if a company was willing to exchange its leases.

B. Policy Changes

BLM could make several policy changes which would enable it to better exert its retained rights so as to ensure protection of the natural environment. While, as argued above, the 200-meter 60-day rule establishes a floor to the reasonable measures BLM can require, not a ceiling,[584] this provision in the § 3101.1-2 regulation is nevertheless sometimes treated by BLM as imposing limits on its discretion.[585] The § 3101.1-2 regulation should therefore be rewritten to eliminate the 200-meter 60-day rule. The provision stating that reasonable measures deemed consistent with the lease rights granted “[a]t a minimum” include limitations that do not “require relocation of proposed operations by more than 200 meters; require that operations be sited off the leasehold; or prohibit new surface disturbing operations for a period in excess of 60 days in any lease year”[586] creates tension with the prior two sentences in the regulation. The first sentence provides that reasonable measures to minimize adverse impacts can be imposed “as may be required by the authorized officer,” and then the next sentence states, “Such reasonable measures may include, but are not limited to, modification to siting or design of facilities, timing of operations, and specification of interim and final reclamation measures.”[587] This tension should be eliminated from the regulation, and BLM should simply provide for taking reasonable measures as it deems necessary to minimize adverse impacts, consistent with the lease rights granted.[588]

BLM should also take action to ensure IM 92-67 and similar provisions in BLM Manual MS-3101 have no continuing force.[589] While the IM nominally expired in 1992, it seems to have some continuing influence over BLM oil and gas development decision making.[590] And the manual section has no stated expiration date.[591] In particular, the requirement that the need for stipulations or conditions of approval “must be clearly and convincingly documented” or that there be “clear evidence and convincing need” for a condition of approval should be eliminated.[592] This elevated burden of proof is not justified.[593] BLM decision making regarding what measures are needed to minimize adverse impacts when it approves oil and gas development should be subject to the arbitrary and capricious standard that applies to all agency actions, not a heightened clear and convincing evidence standard.[594]

It would also be useful if BLM developed regulations defining what constitutes “unnecessary or undue degradation” (UUD) in the context of oil and gas development, as it has done for hardrock minerals.[595] Given the importance of this “specific, nondiscretionary statute” under FLPMA[596] it would be helpful to have a formal definition of what constitutes UUD in the context of oil and gas development. As recognized in Mineral Policy Center, any such regulation should recognize that both unnecessary degradation of the public lands and undue degradation of the lands must be prevented.[597] Provisions related to unnecessary degradation could prevent activities that are not necessary for mining while the undue degradation prong of any regulation should prevent excessive or unwarranted harm to the public lands.[598] The numerous environmental protection laws applicable to oil and gas development on the public lands could help define what impacts are excessive or unwarranted.

More generally, BLM should consider issuing IMs that fully explain BLM’s retained rights and its authority to exercise its retained rights so as to protect the natural environment. Likewise, the Secretary of the Interior or the Interior Department Solicitor should consider issuing similar orders or opinions. The extent of BLM’s retained rights should be fully explained and apparent in agency policy.

In October 2009, BLM issued a report regarding seventy-seven lease parcels in Utah that had been offered for sale at the December 2008 lease sale but were withdrawn due to court action and other controversy.[599]
In this report the agency made a number of recommendations for improvement of its leasing program with regard to the Utah lease parcels.[600] One recommendation made by the reviewing team of BLM and other agency personnel was this: “BLM and others would benefit by guidance from the Solicitor’s Office on the nature of the right created by issuance of a lease.”[601] The team noted that it had heard varying opinions expressed by personnel in the BLM Utah state office regarding what rights were granted by a lease, ranging from views that a lease was a “compensable property right” that could only be extinguished by paying just compensation, to views that a lease is a “contingent right” that could be extinguished.[602] There were also various opinions expressed regarding what level of development constituted enjoyment of lease rights.[603] The review team concluded that “[t]he nature of a lease right is a fundamental issue that underlies the Bureau’s oil and gas leasing program.”[604] The findings and differences of opinion in the report emphasize the need for formal statements from BLM via IMs, or from the Department of Interior via Solicitor’s opinions or Secretarial orders, regarding the nature of the rights granted under a federal onshore oil and gas lease, and, just as importantly, the rights that BLM retains and will exert despite having issued a lease.

Any BLM IMs and Department of the Interior Solicitor opinions or Secretarial orders related to BLM’s retained rights could be made part of the oil and gas reform effort the Department of the Interior is now pursuing.[605]
In particular, they could support or be a component of the Master Leasing and Development Plans that will now be required.[606]

IX. BLM Has an Obligation to Fully Assert Its Retained Rights

In this Article I have largely expressed the degree of BLM’s retained rights under an oil and gas lease and its ability to exercise them in somewhat conditional terms. BLM “has” retained rights; it “can” or even “should” exercise them, but I generally have not said BLM must exert those retained rights. In this Part, however, I will argue BLM must fully exert its retained rights and I will explain the basis for this view.

Fundamentally, it is my view that not only does BLM have retained rights allowing it to protect the natural environment in areas where it has issued an oil and gas lease that grants the right to develop those minerals, it in fact has an obligation to fully assert those rights. The reason I take this view is because many of the authorities that the right to develop has been made subject to are stated in mandatory terms or establish specific, nondiscretionary obligations.

Under the Mineral Leasing Act, BLM “shall” regulate surface disturbing activities in the interest of conservation of surface resources.[607]
Under FLPMA, BLM “shall” take any action necessary to prevent unnecessary or undue degradation of the public lands.[608] Under the ESA, BLM “shall” further the purposes of the ESA, “shall” ensure its actions do not jeopardize the continued existence of listed species or destroy or adversely modify their critical habitat, and it is unlawful for BLM to take a listed species.[609] The National Historic Preservation Act, Migratory Bird Treaty Act, and the Bald and Golden Eagle Protection Act contain various mandatory requirements or prohibitions.[610] The Clean Air Act and Clean Water Act provide that federal agencies “shall” be subject to laws for the control and abatement of air and water pollution.[611] A number of other applicable laws discussed in Part V.B are also framed in mandatory terms.

Many of BLM’s oil and gas operating regulations related to protection of the natural environment are also mandatory.[612] For example, in approving oil and gas operations, BLM is directed to protect natural resources and environmental quality and operators are subject to a number of other obligations (which BLM is charged with enforcing). BLM’s land-use authorization regulations require mandatory terms and conditions for the protection of a number of environmental attributes and benefits.[613] Some of the terms and conditions in the lease forms are stated in mandatory terms, especially in modern versions of the lease. Section 6 of the modern leases in use since March 1984 provides that lessees “shall” (or “must”) take reasonable measures to minimize adverse impacts to the environment, with the determination of what is reasonable being as “deemed necessary by lessor to accomplish the intent of this section.”[614] Provisions in Onshore Oil and Gas Order Number 1 include mandatory obligations for BLM.[615]

Modern versions of the lease form make any rights granted under the lease subject to these various mandatory conditions.[616] The § 3101.1-2 regulation contains a similar provision making the lease rights granted subject to stipulations attached to the lease; specific, nondiscretionary statutes; and reasonable measures required by the authorized officer to minimize adverse impacts.[617] It seems clear that BLM is obliged to meet a number of mandatory requirements for environmental protection under the terms of a federal onshore oil and gas lease and the authorities that have been incorporated into it.

This is not to say these mandatory obligations eliminate or override BLM’s obligation to manage the public lands for multiple use and sustained yield[618] or to meet the energy development goals expressed in several statutes and BLM’s regulations.[619] Assertion of its retained rights relative to environmental protection will have to be done in recognition of these obligations. But it is equally clear that the mineral policies of this country have been formulated in recognition of a need for substantial environmental protection. Accordingly, when BLM issues an oil and gas lease it does not grant an unqualified right to development. It has retained many rights to condition development so as to protect the natural environment. And many of these retained rights are grounded in mandatory environmental protection obligations.

It is not my contention that a successful “failure to act” lawsuit charging violation of § 706(1) of the Administrative Procedure Act could necessarily be launched against BLM in order to force it to assert particular retained rights.[620] One court rejected this proposition with respect to BLM’s operations regulations.[621] Rather, my contention is that BLM has substantial retained rights allowing it to protect the environment when oil and gas operations are proposed on an onshore lease, and given the mandatory nature of many of the underlying authorities that have been incorporated into the lease, it must fully exert those retained rights, even if the agency retains discretion to determine exactly what those measures might be.[622]

Given the wide array of mandatory provisions requiring strong measures to protect the environment, which attach to a lease and govern lease operations, it is clear that not only does BLM have discretion to condition lease development and operations pursuant to its retained rights in order to protect the natural environment, it in fact has an obligation to
do so, even if the details of what those actions might be remain within
BLM’s discretion.

X. Conclusion

There are approximately 39,000,000 acres of federal mineral estate in the eleven western states subject to onshore oil and gas leases issued by the Bureau of Land Management. The leases grant the lessee the right to extract any oil or natural gas that may be found on the leased land. However, the leases also make the grant of rights subject to a number of reservations of authority to the federal government. The rights that BLM retains stem from laws, regulations, terms in the lease contract, and other authorities. A review of the provisions in these authorities shows that BLM retains substantial rights to regulate the time, place, and manner of oil and gas development, despite having granted rights allowing oil and gas development. Development can be conditioned through regulation of the siting and design of facilities and the timing of operations, as well as specification of the rates of oil and gas development and production so as to minimize adverse impacts to the environment, other resource values, land uses, and land users. If BLM fully exercises this array of retained rights it can considerably reduce environmental disturbance caused by oil and gas development on the public lands. Given the mandatory, nondiscretionary nature of many of the authorities that a federal onshore oil and gas lease is subject to, BLM has an obligation to fully exert its retained rights.



* The author is program director and a staff attorney with the Wyoming Outdoor Council. He has a B.S. degree in wildlife biology, an M.S. degree in range science, and received his J.D. from the University of Utah College of Law. He would like to thank Rebekah Smith for her assistance with research supporting this Article during her tenure as an intern with the Wyoming Outdoor Council during the summer of 2008. He would also like to thank Sara Waterson for her assistance in generating the data that appear in the table in this Article and other background data. Thanks is also due to the BLM personnel who are mentioned in the Article and who kindly offered helpful (and in some cases critical) information and materials. And finally, the author would like to thank Lisa Dardy McGee, a staff attorney with the Wyoming Outdoor Council, and Timothy J. Preso, a staff attorney with Earthjustice, who reviewed a draft of this Article and made helpful suggestions that improved it greatly. The author can be reached at bruce@wyomingoutdoorcouncil.org.

[1] SeeBureau of Land Mgmt., U.S. Dep’t of the Interior, Public Land Statistics 2008 tbl.1-3 (2008), available at http://www.blm.gov/public_land_statistics/pls08/pls1-3_08.pdf [hereinafter Bureau of Land Mgmt., Public Land Statistics 2008]; Bureau of Land Mgmt., U.S. Dep’t of the Interior, Total Number of Acres Leased, http://www.blm.gov/pgdata/etc/
medialib/blm/wo/MINERALS__REALTY__AND_RESOURCE_PROTECTION_/energy/oil___gas_statistics.Par.16715.File.dat/chart_2009_02.pdf. These data do not reflect oil and gas leasing on tribal lands. See Bureau of Land Mgmt., U.S. Dep’t of the Interior, Facts About Federal Energy Leasing and Development, http://www.blm.gov/wo/st/en/info/newsroom/Energy_Facts_07.html (last visited Apr. 18, 2010) (pointing out that nationwide the Bureau of Land Management manages nearly 700 million acres of federal mineral estate).

[2] See 43 C.F.R. pts. 3100, 3160 (2008) (presenting BLM’s onshore oil and gas leasing and oil and gas operations regulations).

[3] See Bureau of Land Mgmt., Public Land Statistics 2008, supra note 1, tbl.1-3.

[4] See Bureau of Land Mgmt., U.S. Dep’t of the Interior, BLM-Alaska Energy Program, http://www.blm.gov/ak/st/en/prog/energy.html (last visited Apr. 18, 2010) (presenting information on BLM oil and gas leasing in Alaska).

[5] The Forest Service must consent to leasing on its lands, although BLM conducts the actual leasing. See Mineral Leasing Act, 30 U.S.C. § 226(h) (2006) (providing that leasing by the Secretary of the Interior on Forest Service lands cannot occur over the objection of the Secretary of Agriculture); 43 C.F.R. § 3101.7-1(c) (2008) (same); 36 C.F.R. §§ 228.100–.116 (2009) (presenting the Forest Service’s oil and gas resource regulations).

[6] 43 U.S.C. §§ 1331–1356 (2006). For a description of the Minerals Management Service’s offshore leasing program, see Minerals Mgmt. Serv., U.S. Dep’t of the Interior, Offshore Energy & Minerals Management, http://www.mms.gov/offshore (last visited Apr. 18, 2010).

[7] 30 U.S.C. §§ 181–287 (2006).

[8] Id.

[9] 30 U.S.C. §§ 22–24, 26–30, 33–35, 37, 39–43, 47 (2006).

[10] Id. § 29.

[11] Id. § 23.

[12] 30 U.S.C. § 181 (2006).

[13] Id. §§ 181, 184(d), 188–189, 191, 226(b)–(c).

[14] Id. § 226(a) (emphasis added). In a line of cases, numerous courts have held that the decision to issue a lease in the first instance is a decision within the Secretary of the Interior’s discretion. See, e.g., Udall v. Tallman, 380 U.S. 1, 4 (1965); United States ex rel. McLennan v. Wilbur, 283 U.S. 414, 417 (1931); McDonald v. Clark, 771 F.2d 460, 463 (10th Cir. 1985); McTiernan v. Franklin, 508 F.2d 885, 887 (10th Cir. 1975); Duesing v. Udall, 350 F.2d 748, 750 (D.C. Cir. 1965); Cont’l Land Res., 162 I.B.L.A. 1, 7 (2004). But see Mountain States Legal Found. v. Hodel, 668 F. Supp. 1466, 1474 (D. Wyo. 1987) (finding that delay in processing leasing proposals can constitute an impermissible withdrawal of public lands); Mountain States Legal Found. v. Andrus, 499 F. Supp. 383, 391 (D. Wyo. 1980) (same). In Bob Marshall Alliance v. Hodel, 852 F.2d 1223 (9th Cir. 1988), the United States Court of Appeals for the Ninth Circuit declined to follow the holding in Andrus relative to withdrawals. Id. at 1229–30.

[15] 30 U.S.C. § 226(b)(1)(A) (2006).

[16] Id.

[17] Id. § 226(c)(1).

[18] Id. § 226(f)–(h).

[19] Federal Onshore Oil and Gas Leasing Reform Act of 1987, Pub. L. No. 100-203, 101 Stat. 1330-256 (codified as amended at 30 U.S.C. §§ 195, 226-3 (2006)).

[20] 30 U.S.C. § 226(b)–(h) (2006).

[21] Act of Feb. 25, 1920, ch. 85, § 17, 41 Stat. 437, 443 (1920) (current version at 30 U.S.C. § 181(b) (2006)).

[22] Act of Aug. 8, 1946, ch. 916, § 3, 60 Stat. 950, 951 (1946) (current version at 30 U.S.C. § 181(c) (2006)).

[23] 4 George Cameron Coggins & Robert L. Glicksman, Public Natural Resources Law § 39:2, at 39-6 (2d ed. 2010).

[24] Id. at 39-6 to -7. “SIMO” stands for “simultaneous lease drawing,” but according to BLM officials the abbreviation is really a shortened reference to “simultaneous.” Telephone Interview with William Gewecke, Petroleum Eng’r, Minerals & Realty Mgmt., Bureau of Land Mgmt.
(Nov. 12, 2009).

[25] Patricia J. Beneke, The Federal Onshore Oil and Gas Leasing Reform Act of 1987:
A Legislative History and Analysis
, 4 J. Min. L. & Pol’y 11, 15 (1988).

[26] Id.

[27] Id. at 17–25.

[28] Id. at 35–37.

[29] See generally id. at 11; Thomas L. Sansonetti & William R. Murray, A Primer on the Federal Onshore Oil and Gas Leasing Reform Act of 1987 and Its Regulations, 25 Land & Water L. Rev. 375 (1990); Abraham E. Haspel, Drilling for Dollars: The New and Improved Federal Oil Lease Program, Reg., Fall 1990, at 62.

[30] 734 F.2d 347 (8th Cir. 1984) (determining that KGS determinations on the Fort Chaffee Military Reservation in Arkansas were arbitrarily constrained, allowing lands to be inappropriately leased on a noncompetitive basis in an area with strong competition for productive oil and gas properties).

[31] Telephone Interview with Julie Weaver, Chief, Branch of Fluid Minerals Adjudication, Wyo. State Office, Bureau of Land Mgmt. (Oct. 15, 2009).

[32] Id.

[33] Id. According to Ms. Weaver, in older leases there can be some differences in rental provisions when a lease was in a KGS or in a unitized field, and sometimes different royalty provisions can apply. Id. But there are no differences in the environmental protection provisions in competitive versus noncompetitive leases or in pre- versus post-FOOGLRA leases. Id.

[34] In New Mexico ex rel. Richardson v. Bureau of Land Mgmt. (Richardson), 565 F.3d 683 (10th Cir. 2009), the United States Court of Appeals for the Tenth Circuit construed the BLM oil and gas development process as being comprised of three stages: land use planning, leasing, and filing an APD. Id. at 689 n.1, 716. However, I believe the five-step process I describe captures the nuances of the oil and gas leasing and development process; moreover, the court did note that “exploring” needed to occur. Id. at 689 n.1.

[35] 43 U.S.C. §§ 1701–1785 (2006); see id. § 1712 (presenting FLPMA’s planning requirements); 43 C.F.R. pt. 1600 (2008) (presenting BLM’s regulations implementing FLPMA’s planning requirements).

[36] Richardson, 565 F.3d at 689 n.1.

[37] The RMP for a BLM field office can be found on that field office’s website. For example, the RMP for the Pinedale, Wyoming field office can be found on that field office’s website. Pinedale Field Office, Bureau of Land Mgmt., Record of Decision/Approved RMP, http://www.blm.gov/wy/st/en/programs/Planning/rmps/pinedale/rod_armp.html (last visited
Apr. 18, 2010).

[38] See, e.g., Bureau of Land Mgmt., U.S. Dep’t of the Interior, Arizona Resource Management Plans, http://www.blm.gov/az/st/en/info/nepa/environmental_library/arizona_resource_
management.html (last visited Apr. 18, 2010) (providing draft and final RMPs for the Arizona state office).

[39] See, e.g., Pinedale Field Office, Bureau of Land Mgmt., U.S. Dep’t of the Interior, Record of Decision and Approved Pinedale Resource Management Plan 2-1 tbl.1-1 (2008), available at http://www.blm.gov/pgdata/etc/medialib/blm/wy/programs/planning/rmps/ pinedale/rod.Par.45058.File.dat/05_Record_of_Decision_and_Approved_Pinedale_RMP.pdf; id. map 1-3, available at http://www.blm.gov/pgdata/etc/medialib/blm/wy/programs/planning/
rmps/pinedale/rod/maps.Par.50090.File.dat/03_Map1-03.pdf. Areas available for lease can be examined using the GeoCommunicator tool at Bureau of Land Mgmt. & U.S. Forest Serv.,
U.S. Dep’t of the Interior & U.S. Dep’t of Agric., GeoCommunicator Home, http://www.geocommunicator.gov (last visited Apr. 18, 2010).

[40] National Environmental Policy Act of 1969, 42 U.S.C. §§ 4321–4347 (2006).

[41] See id. § 4332(2)(C) (2006) (requiring preparation of an EIS when a federal action may significantly affect the quality of the human environment); 43 C.F.R. § 1601.0-6 (2008) (“Approval of a resource management plan is considered a major Federal action significantly affecting the quality of the human environment.”).

[42] Beneke, supra note 25, at 43.

[43] See infra notes 75–81 and accompanying text (discussing lease protests).

[44] See, e.g., Sierra Club v. Peterson, 717 F.2d 1409, 1414 (D.C. Cir. 1983) (quoting Mobil Oil Corp. v. Fed. Trade Comm’n, 562 F.2d 170, 173 (2d Cir. 1977)) (holding that issuing an oil and gas lease without a no surface occupancy stipulation represents an irreversible and irretrievable commitment of resources, which requires compliance with NEPA); Richardson, 565 F.3d 683, 718 (10th Cir. 2009) (same); Conner v. Burford, 848 F.2d 1441, 1449–50 (9th Cir. 1988) (same); Ctr. for Native Ecosystems, 170 I.B.L.A. 331, 344–45 (2006). These and other cases will be discussed in Part VII.D, infra.

[45] 43 C.F.R. pt. 3150 (2008).

[46] See 40 C.F.R. §§ 1501.3–.4, 1508.9 (2009) (presenting Council on Environmental Quality regulations governing when to prepare an EA versus an EIS and requirements for these two types of documents); id. pt. 1502 (2009) (same).

[47] See Gates Rubber Co. v. Comm’r, 74 T.C. 1456, 1460 (1980).

[48] Rocky Mountain Oil & Gas Ass’n v. Watt, 696 F.2d 734, 742 (10th Cir. 1982).

[49] See National Environmental Policy Act of 1969, 42 U.S.C. § 4332(2) (2006) (making NEPA applicable to all federal agencies, of which BLM is one); id. § 4332(2)(C) (requiring an EIS for all federal agency actions significantly affecting the quality of the human environment).

[50] See, e.g., Bureau of Land Mgmt., U.S. Dep’t of the Interior, Record of Decision for the Jonah Infill Drilling Project: Environmental Impact Statement 1 (2006), available at http://www.blm.gov/pgdata/etc/medialib/blm/wy/information/NEPA/pfodocs/jonah.Par.5187.File.dat/00rod2.pdf [hereinafter Bureau of Land Mgmt., Jonah Infill ROD] (approving 3100 wells); Bureau of Land Mgmt., U.S. Dep’t of the Interior, Record of Decision: Final Supplemental Environmental Impact Statement for the Pinedale Anticline Oil and Gas Exploration and Development Project 4 (2008), available at http://www.blm.gov/pgdata/etc/medialib/blm/wy/
information/NEPA/pfodocs/anticline/rod.Par.50775.File.dat/00ROD.pdf [hereinafter Bureau of Land Mgmt., Pinedale Anticline ROD] (approving 4399 wells); Bureau of Land Mgmt., U.S. Dep’t of the Interior, Record of Decision: Environmental Impact Statement for
the Atlantic Rim Natural Gas Field Development Project 1 (2006), available at http://www.blm.gov/pgdata/etc/medialib/blm/wy/information/NEPA/rfodocs/atlantic_rim/rod.Par.46558.File.dat/ROD.pdf [hereinafter Bureau of Land Mgmt., Atlantic Rim EIS] (approving approximately 2000 wells); see also Theodore Roosevelt Conservation P’ship v. Salazar, 605 F. Supp. 2d 263, 269 (D.D.C. 2009) (deciding in a challenge to the Atlantic Rim project that BLM did not violate NEPA or FLPMA).

[51] See supra note 50.

[52] See Bureau of Land Mgmt., U.S. Dep’t of the Interior, Record of Decision for the Designation of Areas of Critical Environmental Concern for the Roan Plateau: Resource Management Plan Amendment and Environmental Impact Statement 1 (2008), available at http://www.blm.gov/pgdata/etc/medialib/blm/co/programs/land_use_planning/rmp/roan_plateau/documents.Par.3928.File.dat/FinalRoanRODII_3_13_08.pdf.

[53] 43 C.F.R. § 3162.3-1(c) (2008).

[54] Id.

[55] See S. Utah Wilderness Alliance, 159 I.B.L.A. 220, 224 (2003).

[56] Pub. L. No. 109-58, 119 Stat. 604 (codified primarily in scattered sections of 42 U.S.C.)

[57] See 42 U.S.C. § 15942(a), (b)(1)–(4) (2006) (presenting the Energy Policy Act of 2005’s categorical exclusions). In September 2009, the United States Government Accountability Office (GAO) released a report entitled Energy Policy Act of 2005: Greater Clarity Needed to Address Concerns with Categorical Exclusions for Oil and Gas Development Under Section 390 of the Act. U.S. Gov’t Accountability Office, Energy Policy Act of 2005: Greater Clarity Needed to Address Concerns with Categorical Exclusions for Oil and Gas Development Under Section 390 of the Act (2009), available at http://www.gao.gov/new.items/d09872.pdf. The GAO found that 6100 out of 22,000 APDs, or 28%, that had been filed between 2006 and 2008 were approved via categorical exclusion from NEPA. Id. at 12. Categorical exclusions were also used in another 1150 instances. Id. at “Highlights” (unnumbered page). The GAO also found that the use of categorical exclusions often was not in compliance with section 390 of the Energy Policy Act or BLM guidance on the use of categorical exclusions. Id. at 23. The report recommends that Congress take action to amend section 390 so as to clarify certain key terms, and that BLM take interim action to provide better oversight and guidance on the use of categorical exclusions. Id. at 53. BLM indicated to the GAO that it will take immediate steps to ensure the use of section 390 categorical exclusions are consistent with the Energy Policy Act of 2005 and BLM guidance. Id. at 54. The Forest Service has also adopted a categorical exclusion from NEPA for oil and gas development projects. 36 C.F.R. § 220.6(e)(17) (2009). This categorical exclusion is not based on the Energy Policy Act of 2005 categorical exclusions and is a separate Forest Service policy. See National Environmental Policy Act Procedures, 73 Fed. Reg. 43,084, 43,090–91 (July 24, 2008) (codified at 36 C.F.R. pt. 220). Issues related to Energy Policy Act of 2005 categorical exclusions will be considered further infra in the text accompanying notes 221–23.

[58] Mineral Leasing Act, 30 U.S.C. § 226(f) (2006).

[59] See W. Org. of Res. Councils v. Bureau of Land Mgmt., 591 F. Supp. 2d 1206, 1208
(D. Wyo. 2008) (reviewing a BLM decision to allow up to 51,000 coal bed methane wells in the Powder River Basin); Bureau of Land Mgmt., Jonah Infill ROD, supra note 50, at 1; Bureau of Land Mgmt., Pinedale Anticline ROD, supra note 50, at 4.

[60] See S. Utah Wilderness Alliance, 177 I.B.L.A. 284, 284–85 (2009); Gas Gathering Agreement in Powder River Basin: Coal Bed Methane Project Reached Between
Pennaco Energy and TransMontaigne Unit, Bear Paw Energy Inc.
, Bus. Wire, Mar. 24, 1999, http://findarticles.com/p/articles/mi_m0EIN/is_1999_March_24/ai_54191657 (last visited
Apr. 18, 2010); Press Release, Nat’l Trust for Historic Pres., Coalition Applauds
Bureau of Land Management for Withdrawing Eight Parcels of Land Near Chaco Canyon, New Mexico from Oil and Gas Lease Sale (Oct. 9, 2009), http://www.preservationnation.org/about-us/press-center/press-releases/2009/coalition-applauds-bureau-of.html (last visited Apr. 18, 2010); ExxonMobil, Colorado: Piceance Basin, http://www.exxonmobil.com/corporate/energy_project_ piceance.aspx (last visited Apr. 18, 2010).

[61] 30 U.S.C. § 226(a)–(e) (2006); 43 C.F.R. pt. 3100 (2008).

[62] Bureau of Land Mgmt., U.S. Dep’t of the Interior, Oil and Gas, http://www.blm.gov/wo/st/
en/prog/energy/oil_and_gas.html (last visited Apr. 18, 2010); see also Sansonetti & Murray, supra note 29, at 385–403 (discussing, among other things, the leasing process).

[63] See, e.g., Bureau of Land Mgmt., U.S. Dep’t of the Interior, Competitive Lease Sale Notices & Results, http://www.blm.gov/wy/st/en/programs/energy/Oil_and_Gas/Leasing.html (last visited Apr. 18, 2010) (presenting Wyoming oil and gas lease sale information).

[64] 30 U.S.C. § 226(b)(1)(A) (2006); 43 C.F.R. §§ 3110.1(b), 3120.1-1 to -2 (2008).

[65] 30 U.S.C. § 226(b)(1)(A), (c) (2006); 43 C.F.R. §§ 3110.1(b), 3120.6 (2008).

[66] 30 U.S.C. § 226(b)(1)(A) (2006); 43 C.F.R. §§ 3110.1(b), 3120.6 (2008).

[67] 30 U.S.C. § 226(b)(1)(A) (2006); 43 C.F.R. §§ 3110.3-3(b), 3120.2-3 (2008).

[68] 30 U.S.C. § 226(e) (2006); 43 C.F.R. §§ 3107.2-1, 3107.3-1, 3110.3-1, 3120.2-1 (2008).

[69] 30 U.S.C. § 226(e) (2006); 43 C.F.R. § 3107.1 (2008).

[70] 30 U.S.C. § 226(d) (2006); 43 C.F.R. § 3103.2-2(a) (2008).

[71] 30 U.S.C. § 226(b)(1)(A), (c) (2006); 43 C.F.R. § 3103.3-1(a)(1) (2008).

[72] 30 U.S.C. § 191(a) (2006).

[73] 43 C.F.R. § 3104.1(a) (2008).

[74] Id. §§ 3104.2, 3104.3(a)–(b).

[75] Id. §§ 3110.4(a), 3120.5-1(a)–(b), 3120.5-2, 3120.5-3(a).

[76] Id. §§ 3110.3-2, 3120.2-2.

[77] Id. §§ 4.450-2, 3120.1-3; see also Bureau of Land Mgmt., U.S. Dep’t of the Interior, Notice of Competitive Oil and Gas Lease Sale, at i–ii, viii–ix (2009), available at http://www.blm.gov/
pgdata/etc/medialib/blm/wy/programs/energy/og/leasing/2009.Par.62062.File.dat/12list.pdf
(presenting information on BLM’s competitive oil and gas lease sale on December 1, 2009,
in Wyoming and describing protest procedures).

[78] Bureau of Land Mgmt., supra note 77, at vi.

[79] Id. at ix.

[80] Id.

[81] Id.; 43 C.F.R. §§ 4.410(a), 3120.1-3 (2008). However, an appeal to the IBLA is not subject to an automatic stay while the appeal is considered, so lease parcels can be issued after a protest is rejected even if an appeal is filed. See id. § 3120.1-3 (providing that “[n]o action pursuant to the regulations in this subpart shall be suspended under § 4.21(a) of this title due to an appeal from a decision by the authorized officer to hold a lease sale” and also providing that the authorized officer “may” suspend a lease on a parcel while considering a protest or appeal).

[82] 43 C.F.R. § 3101.1-1 (2008).

[83] See Bureau of Land Mgmt., U.S. Dep’t of Interior, Form 3100-11, Offer to Lease and Lease For Oil and Gas 1 (2008), available at http://www.blm.gov/pgdata/etc/medialib/blm/mt/
blm_programs/energy/oil_and_gas/leasing/lease_sales/2009/jan.Par.6548.File.dat/3100-11.pdf.

[84] Mailed Copies of Lease Forms from Karen Wrenn, Forms Manager, Denver Office,
Bureau of Land Mgmt., to Rebekah Smith (Aug. 13, 2008) (on file with author). These forms included versions published in 1984, 1988, 1992, 2003, and 2006. Bureau of Land Mgmt.,
U.S. Dep’t of Interior, Form 3100-11, Offer to Lease and Lease for Oil and Gas (1984) [hereinafter Bureau of Land Mgmt., 1984 Lease Form]; Bureau of Land Mgmt., U.S. Dep’t of Interior, Form 3100-11, Offer to Lease and Lease for Oil and Gas (1988) [hereinafter Bureau of Land Mgmt., 1988 Lease Form]; Bureau of Land Mgmt., U.S. Dep’t of Interior,
Form 3100-11, Offer to Lease and Lease for Oil and Gas (1992) [hereinafter Bureau of Land Mgmt., 1992 Lease Form]; Bureau of Land Mgmt., U.S. Dep’t of Interior, Form 3100-11, Offer to Lease and Lease for Oil and Gas (2003) [hereinafter Bureau of Land Mgmt., 2003 Lease Form]; Bureau of Land Mgmt., U.S. Dep’t of Interior, Form 3100-11, Offer to Lease and Lease for Oil and Gas (2006) [hereinafter Bureau of Land Mgmt., 2006 Lease Form].

[85] Bureau of Land Mgmt., 1984 Lease Form, supra note 84.

[86] See sources cited supra note 84.

[87] See Bureau of Land Mgmt., supra note 83.

[88] Mailed Copies of Lease Forms from Vickie Mistarka, Wyo. State Office, Bureau of Land Mgmt., to author (Feb. 2009) (on file with author). These forms included versions in use in 1954, 1965, and 1971. Bureau of Land Mgmt., U.S. Dep’t of Interior, Form 4-1158, Offer to Lease and Lease for Oil and Gas (1954) [hereinafter Bureau of Land Mgmt., 1954 Lease Form]; Bureau of Land Mgmt., U.S. Dep’t of Interior, Form 4-1158, Offer to Lease and Lease for Oil and Gas (1965) [hereinafter Bureau of Land Mgmt., 1965 Lease Form]; Bureau of Land Mgmt., U.S. Dep’t of Interior, Form 3120-19, Lease for Oil and Gas (1971) [hereinafter Bureau of Land Mgmt., 1971 Lease Form].

[89] See sources cited supra note 88. The 1954 lease was issued on Form 4-1158 (fourth edition), dated September 1953; the 1965 lease was issued on Form 4-1158 (ninth edition), dated August 1961; and the 1971 lease was issued on Form 3120-19, dated May 1968.

[90] Id.

[91] The time period the lease is presumed to have been in effect is based on an example of a lease that was issued on July 9, 1954, provided by the BLM Wyoming state office. This lease form is dated September 1953, but it is assumed similar leases were in effect from the enactment of the Mineral Leasing Act in 1920 through the date of this lease.

[92] The time period the lease is presumed to have been in effect is based on an example of a lease that was issued on January 20, 1965, provided by the BLM Wyoming state office. This lease form is dated August 1961, but it is assumed similar leases were in effect from the date of the 1954 lease through the date of this lease.

[93] The time period the lease is presumed to have been in effect is based on an example of a lease that was issued on March 29, 1971, provided by the BLM Wyoming state office. This lease form is dated May 1968, but it is assumed similar leases were in effect from the date of the 1965 lease through the date of the first lease available in BLM’s archives, which is March 1984.

[94] This and the subsequent lease forms are available in BLM’s archives, so the dates this lease and the subsequent leases were in effect can be determined with assurance and is not presumed.

[95] These data were generated from BLM’s LR2000 database. Bureau of Land Mgmt.,
U.S. Dep’t of the Interior, Bureau of Land Management’s Land & Mineral Legacy Rehost
2000 System–LR 2000, http://www.blm.gov/lr2000/ (last visited Apr. 18, 2010). A search was done for all currently active oil and gas leases within the different time frames by state in the
11 western states.

[96] In addition to granting the right to develop oil and gas, the leases also make provisions for other matters not directly implicating BLM’s retained rights relative to protection of the natural environment. These include provisions for payment of rentals, royalties, and bonds, among other things. See Bureau of Land Mgmt., supra note 83, at 1.

[97] Bureau of Land Mgmt., 1954 Lease Form, supra note 88, at 1.

[98] Bureau of Land Mgmt., 1965 Lease Form, supra note 88, at 1; Bureau of Land Mgmt., 1971 Lease Form, supra note 88, at 1.

[99] Bureau of Land Mgmt., 1984 Lease Form, supra note 84, at 1.

[100] Bureau of Land Mgmt., 1988 Lease Form, supra note 84, at 1; Bureau of Land Mgmt., 1992 Lease Form, supra note 84, at 1; Bureau of Land Mgmt., 2003 Lease Form, supra note 84, at 1; Bureau of Land Mgmt., 2006 Lease Form, supra note 84, at 1; Bureau of Land Mgmt., supra note 83, at 1. The “exclusive right” to develop all of the oil and gas that might be found on a lease should probably be viewed as creating a right for the lessee to ensure no other entity seeks to develop oil and gas on a lease, not as creating rights against the government that could prevent it from exercising its retained rights. An exclusive right is “[o]ne which only the grantee thereof can exercise, and from which all others are prohibited or shut out.” Black’s Law Dictionary 565 (6th ed. 1990).

[101] Bureau of Land Mgmt., 1954 Lease Form, supra note 88, at 2.

[102] Id.

[103] Id.

[104] Id.

[105] Id.

[106] Id.

[107] Id.

[108] Bureau of Land Mgmt., 1965 Lease Form, supra note 88.

[109] Bureau of Land Mgmt., 1971 Lease Form, supra note 88, at 2.

[110] See Bureau of Land Mgmt., supra note 83.

[111] Bureau of Land Mgmt., 1984 Lease form, supra note 84, at 1.

[112] Bureau of Land Mgmt., 1988 Lease form, supra note 84, at 1; Bureau of Land Mgmt., 1992 Lease Form, supra note 84, at 1; Bureau of Land Mgmt., 2003 Lease Form, supra note 84, at 1; Bureau of Land Mgmt., 2006 Lease Form, supra note 84, at 1; Bureau of Land Mgmt., supra note 83, at 1.

[113] See, e.g., Bureau of Land Mgmt., 1971 Lease Form, supra note 88, at 1.

[114] Bureau of Land Mgmt., supra note 83, at 2.

[115] Bureau of Land Mgmt., 1984 Lease Form, supra note 84, at 2; Bureau of Land Mgmt., 1988 Lease Form, supra note 84, at 2; Bureau of Land Mgmt., 1992 Lease Form, supra note 84, at 2; Bureau of Land Mgmt., 2003 Lease Form, supra note 84, at 2; Bureau of Land Mgmt., 2006 Lease Form, supra note 84, at 3; Bureau of Land Mgmt., supra note 83, at 3.

[116] Bureau of Land Mgmt., 1984 Lease Form, supra note 84, at 2; Bureau of Land Mgmt., 1988 Lease Form, supra note 84, at 2; Bureau of Land Mgmt., 1992 Lease Form, supra note 84, at 2; Bureau of Land Mgmt., 2003 Lease Form, supra note 84, at 2; Bureau of Land Mgmt., 2006 Lease Form, supra note 84, at 3; Bureau of Land Mgmt., supra note 83, at 3.

[117] Bureau of Land Mgmt., 1984 Lease Form, supra note 84, at 1.

[118] Bureau of Land Mgmt., 1984 Lease Form, supra note 84, at 1; Bureau of Land Mgmt., 1988 Lease Form, supra note 84, at 1; Bureau of Land Mgmt., 1992 Lease Form, supra note 84, at 1; Bureau of Land Mgmt., 2003 Lease Form, supra note 84, at 1.

[119] Bureau of Land Mgmt., 1984 Lease Form, supra note 84, at 2; Bureau of Land Mgmt., 1988 Lease Form, supra note 84, at 2; Bureau of Land Mgmt., 1992 Lease Form, supra note 84, at 2; Bureau of Land Mgmt., 2003 Lease Form, supra note 84, at 2.

[120] Bureau of Land Mgmt., 1984 Lease Form, supra note 84, at 2; Bureau of Land Mgmt., 1988 Lease Form, supra note 84, at 2; Bureau of Land Mgmt., 1992 Lease Form, supra note 84, at 2; Bureau of Land Mgmt., 2003 Lease Form, supra note 84, at 2.

[121] Bureau of Land Mgmt., 1984 Lease Form, supra note 84, at 2; Bureau of Land Mgmt., 1988 Lease Form, supra note 84, at 2; Bureau of Land Mgmt., 1992 Lease Form, supra note 84, at 2; Bureau of Land Mgmt., 2003 Lease Form, supra note 84, at 2.

[122] Compare Bureau of Land Mgmt., 1984 Lease Form, supra note 84, at 2, Bureau of Land Mgmt., 1988 Lease Form, supra note 84, at 2, Bureau of Land Mgmt., 1992 Lease Form, supra note 84, at 2, and Bureau of Land Mgmt., 2003 Lease Form, supra note 84, at 2, with Bureau of Land Mgmt., 2006 Lease Form, supra note 84, at 3, and Bureau of Land Mgmt., supra note 83.

[123] Compare Bureau of Land Mgmt., 2006 Lease Form, supra note 84, at 3, and Bureau of Land Mgmt., supra note 83, at 3, with Bureau of Land Mgmt., 1984 Lease Form, supra note 84, at 2, Bureau of Land Mgmt., 1988 Lease Form, supra note 84, at 2, Bureau of Land Mgmt., 1992 Lease Form, supra note 84, at 2, and Bureau of Land Mgmt., 2003 Lease Form, supra
note 84, at 2.

[124] Compare Bureau of Land Mgmt., 1984 Lease Form, supra note 84, at 2, Bureau of Land Mgmt., 1988 Lease Form, supra note 84, at 2, Bureau of Land Mgmt., 1992 Lease Form, supra note 84, at 2, and Bureau of Land Mgmt., 2003 Lease Form, supra note 84, at 2, with Bureau of Land Mgmt., 2006 Lease Form, supra note 84, at 3, and Bureau of Land Mgmt., supra note 83.

[125] Compare Bureau of Land Mgmt., 1984 Lease Form, supra note 84, at 2, Bureau of Land Mgmt., 1988 Lease Form, supra note 84, at 2, Bureau of Land Mgmt., 1992 Lease Form, supra note 84, at 2, and Bureau of Land Mgmt., 2003 Lease Form, supra note 84, at 2, with Bureau of Land Mgmt., 2006 Lease Form, supra note 84, at 3, and Bureau of Land Mgmt., supra note 83.

[126] Gutierrez de Martinez v. Lamagno, 515 U.S. 417, 432–33 n.9 (1995).

[127] The American Heritage Dictionary of the English Language 1160 (4th ed. 2000).

[128] Id. at 1598.

[129] Black’s Law Dictionary 1019 (6th ed. 1990).

[130] Id. at 1375.

[131] Id.

[132] See 27A Words and Phrases 663–90 (2007 & Supp. 2009) (presenting constructions of “must”); 39 id. at 173–229 (2006 & Supp. 2009) (presenting constructions of “shall”).

[133] See, e.g., Bureau of Land Mgmt., 1954 Lease Form, supra note 88, at 2; Bureau of Land Mgmt., 1971 Lease Form, supra note 88, at 2.

[134] Bureau of Land Mgmt., 1954 Lease Form, supra note 88, at 2; Bureau of Land Mgmt.,
1965 Lease Form, supra note 88, at 2; Bureau of Land Mgmt., 1971 Lease Form, supra note 88, at 2.

[135] See, e.g., Bureau of Land Mgmt., supra note 83, at 3.

[136] Id.

[137] Id.

[138] Id. at 1.

[139] 43 C.F.R. § 3101.1-2 (2008).

[140] Oil and Gas Leasing, Geothermal Resources Leasing, 53 Fed. Reg. 17,340, 17,352
(May 16, 1988).

[141] 43 C.F.R. § 3101.1-2 (2008) (emphasis added).

[142] Id. § 3100.0-5(d).

[143] See discussion infra Parts V.B–C.

[144] 43 C.F.R. § 3101.1-2 (2008).

[145] Id.

[146] Id.

[147] See, e.g., Bureau of Land Mgmt., U.S. Dep’t of the Interior, BLM Manual Handbook 3110-1, Oil and Gas Adjudication Handbook: Issuance of Leases §§ 3101.06.B, 3101.06.B.1, 3101.12 (1996) (on file with the author) (stating that conditions of approval will impose requirements “by not more than” the limitations in the 200-meter 60-day rule); Pinedale Field Office, Bureau of Land Mgmt., Draft Environmental Impact Statement for the Pinedale Resource Management Plan app. 7, at A7-1 (2007), available at http://www.blm.gov/pgdata/etc/medialib/blm/wy/programs/planning/rmps/pinedale/deis/appendices.Par.48971.File.dat/Appendix07.pdf (“[T]he [standard lease terms] allow the authorized officer to move a well or other facility up to 200 meters or delay operations for up to 60 days in a year.”); Instruction Memorandum No. WY-2010-12 from State Dir., Wyo. State Office,
Bureau of Land Mgmt., to Dist. Managers & Deputy State Dirs. 12 (Dec. 29, 2009), available at http://www.blm.gov/pgdata/etc/medialib/blm/wy/resources/efoia/IMs/2010.Par.61358.File.dat/

wy2010-012.pdf (presenting the BLM Wyoming state office Instruction Memorandum regarding sage-grouse conservationand stating, “BLM may, to some degree, exceed the siting and timing limitations set forth in 43 C.F.R. § 3101.1-2”).

[148] 43 CFR § 3101.1-2 (2008).

[149] Oil and Gas Leasing, Geothermal Resources Leasing, 53 Fed. Reg. 17,340, 17,341
(May 16, 1988).

[150] Id.

[151] Id.

[152] See id.; Bureau of Land Mgmt., 1984 Lease Form, supra note 84, at 2.

[153] Yates Petroleum Corp., 176 I.B.L.A. 144, 156 (2008).

[154] Id.

[155] Instruction Memorandum No. 92-67 from Dir., Bureau of Land Mgmt., to All State Dirs. (Dec. 3, 1991) (on file with the author).

[156] Id. at 1.

[157] Federal Land Policy and Management Act of 1976, 43 U.S.C. § 1732(b) (2006).
The implications of the FLPMA requirement to prevent unnecessary or undue degradation will be considered further infra in Part V.B.3.

[158] Instruction Memorandum No. 92-67 from Dir. to All State Dirs., supra note 155, at 3.

[159] Id. at 2.

[160] Id.

[161] Id. at 4; Bureau of Land Mgmt., supra note 147, § 3101.06.

[162] Bureau of Land Mgmt., supra note 147, § 3101.06.B.2.

[163] 43 C.F.R. § 3101.1-2 (2008).

[164] Bureau of Land Mgmt., supra note 83, at 3.

[165] 43 C.F.R. § 3101.1-2 (2008); Bureau of Land Mgmt., supra note 83, at 3.

[166] Oil and Gas Leasing, Geothermal Resources Leasing, 53 Fed. Reg. 17,340, 17,341
(May 16, 1988).

[167] Yates Petroleum Corp., 176 I.B.L.A. 144, 155 (2008) (citing 43 C.F.R. § 3101.1-2 and Federal Land Policy and Management Act of 1976, 43 U.S.C. § 1732(b) (2006)).

[168] Id. at 156 (“‘[T]he authority of the Bureau to prescribe ‘reasonable,’ but more stringent, protection measures is not affected by the final rulemaking.’” (alteration in original) (quoting
53 Fed. Reg. at 17,340–41)).

[169] See id.

[170] IM 92-67 expired by its own terms on September 30, 1992. Instruction Memorandum No. 92-67 from Dir. to All State Dirs., supra note 155, at 1. That said, IMs can continue to be treated as operative by BLM even after they nominally expire. See, e.g., Yates Petroleum Corp.,
176 I.B.L.A. at 159 n.16 (pointing out that in the request for state director review decision under consideration in that appeal, “IM No. WY-90-231 expired on Sept. 30, 1991, [but] it is BLM practice to continue to use the guidance contained in the memorandum”). BLM has sometimes continued to cite the need for clear and convincing evidence to support its ability to condition development long after IM 92-67 expired. See Bureau of Land Mgmt, U.S. Dep’t of the Interior, Final Environmental Impact Statement for the Jack Morrow Hills Coordinated Activity Plan/Proposed Green River Resource Management Plan app. 4, at A4-1 (2004), available at http://www.blm.gov/pgdata/etc/medialib/blm/wy/field-offices/rock_springs/jmhcap/
2004final/vol2.Par.9991.File.dat/106app04.pdf (stating that conditions of approval not provided for by stipulation must be documented through analysis that “must provide clear and convincing evidence showing that undue and unnecessary degradation would result if the [condition of approval] were not applied”). Consequently, IM 92-67 is of continuing concern; BLM Manual MS-3101 has no stated expiration date.

[171] Bureau of Land Mgmt., supra note 83, at 1.

[172] 43 C.F.R. § 3101.1-2 (2008).

[173] Bureau of Land Mgmt., supra note 83, at 1.

[174] Id.

[175] Id. at 1; see also 43 C.F.R. § 3101.1-2 (2008) (providing that the lease is made subject to “[s]tipulations attached to the lease”).

[176] Bureau of Land Mgmt., supra note 83, at 1.

[177] Id.

[178] 43 C.F.R. § 3101.1-2 (2008).

[179] Id.; see Bureau of Land Mgmt., supra note 83, at 3 (providing in section six that the lessee must take reasonable measures deemed necessary by the lessor to minimize adverse impacts).

[180] 43 C.F.R. § 3101.1-2 (2008); Bureau of Land Mgmt., supra note 83, at 1.

[181] 373 U.S. 472 (1963).

[182] Id. at 477–78 (citation omitted) (holding that the Secretary of the Interior has broad administrative powers allowing him to cancel a lease he determined was improperly issued); accord Udall v. Tallman, 380 U.S. 1, 19 (1965) (“An oil and gas lease does not vest title to the lands in the lessee.” (citing Boesche, 373 U.S. at 477–78)); id. at 22 (stating that an oil and gas lease gives the lessee “no right in the land itself”).

[183] See Bureau of Land Mgmt., supra note 83, at 1.

[184] 43 C.F.R. § 3101.1-2 (2008).

[185] Oil and Gas Leasing, Geothermal Resources Leasing, 53 Fed. Reg. 17,340, 17,341–42
(May 16, 1988).

[186] Id. at 17,341.

[187] 43 C.F.R. § 3101.1-1 (2008).

[188] 53 Fed. Reg. at 17,352.

[189] See infra Part V.B.1–6.

[190] See infra Part V.B.1–6.

[191] But see Bureau of Land Mgmt., supra note 147, § 3101.12.B (stating that with respect to specific, nondiscretionary laws, “the requirements of the law shall be met by all oil and gas leases regardless of when the leases were issued”).

[192] Mineral Leasing Act, 30 U.S.C. §§ 181, 226(a)–(c) (2006); see discussion supra Parts II, III.A–B.

[193] 30 U.S.C. § 187 (2006) (emphasis added).

[194] However, the Supreme Court said in a case involving leases “located in a mouth of the Mississippi River” in Louisiana that the Mineral Leasing Act “controls in some measure the actual use of the leased tract, to promote goals such as conservation and safety,” but did not identify particular language in 30 U.S.C. § 187 supporting this view. Wallis v. Pan Am. Petroleum Corp., 384 U.S. 63, 64, 69 (1966).

[195] 30 U.S.C. § 189 (2006).

[196] See Arch Mineral Corp. v. Lujan, 911 F.2d 408, 415 (10th Cir. 1990) (recognizing in a coal leasing case that § 189 “is a broad grant of authority”); Getty Oil Co. v. Clark, 614 F. Supp.
904, 916 (D. Wyo. 1985) (“This provision grants the Secretary broad powers and authority commensurate with the broad responsibilities imposed upon his office.”), aff’d sub nom.
Texaco Producing, Inc., 84 F.2d 776 (10th Cir. 1988).

[197] See discussion infra Part V.D.1.a–b.

[198] 30 U.S.C. § 189 (2006).

[199] Id. § 209 (emphasis added); see also 43 C.F.R. § 3103.4-4 (2008) (providing a companion regulatory provision authorizing suspension of all operations and production on a lease “in the interest of conservation of natural resources”).

[200] 653 F.2d 595 (D.C. Cir. 1981).

[201] 614 F. Supp. 904 (D. Wyo. 1985).

[202] Copper Valley Machine Works, Inc., 653 F.2d at 600 (determining that the “ordinary meaning” of the term “in the interest of conservation” in § 209 of the Mineral Leasing Act allows suspension of operations so as to avoid environmental harm); Getty Oil Co., 614 F. Supp. at 916–17
(holding § 189 and § 209 of the Mineral Leasing Act provide broad grants of authority allowing conditioning of development to protect the environment, even allowing denial of drilling operations to protect wilderness values when a suspension is requested by the lessee).

[203] 30 U.S.C. § 226(g) (2006) (emphasis added) (requiring further that a “plan of operations” exist before a drilling permit can be issued and that bonding be in place “to ensure the complete and timely reclamation of the lease tract, and the restoration of any lands or surface waters adversely affected by lease operations after the abandonment or cessation of oil and gas operations on the lease”).

[204] Federal Onshore Oil and Gas Leasing Reform Act of 1987, Pub. L. No. 100-203, § 5102(g), 101 Stat. 1330, 1330-257 to -258 (codified as amended at 30 U.S.C. § 226(g) (2006)); see supra notes 19–20 and accompanying text (discussing the enactment of FOOGLRA).

[205] See Robertson v. Methow Valley Citizens Council, 490 U.S. 332, 348, 350 (1989) (stating that “[s]ection 101 of NEPA declares a broad national commitment to protecting and promoting environmental quality,” but holding “it is now well settled that NEPA itself does not mandate particular results, but simply prescribes the necessary process”); 40 C.F.R. § 1500.1 (2009) (providing that NEPA “is our basic national charter for protection of the environment”).

[206] National Environmental Policy Act of 1969, 42 U.S.C. § 4332 (2006). The continuing policy of the federal government is “to use all practicable means and measures” to achieve three stated goals, one of which is “to create and maintain conditions under which man and nature can exist in productive harmony.” Id. § 4331(a).

[207] Id. § 4331(b) (providing that all practicable means are to be used to achieve the ends of fulfilling responsibilities to succeeding generations, assuring pleasing surroundings, attaining the widest range of beneficial uses of the environment without undesirable and unintended consequences, preserving our national heritage, achieving balance that permits high standards of living and sharing of amenities, and enhancing the quality of renewable resources and achieving maximum recycling of depletable resources).

[208] See, e.g., 40 C.F.R. § 1500.2 (2009) (“Federal agencies shall to the fullest extent possible . . . [u]se all practicable means . . . to restore and enhance the quality of the human environment and avoid or minimize any possible adverse effects of their actions upon the quality of the human environment.”).

[209] Getty Oil Co., 614 F. Supp. 904, 920 (D. Wyo. 1985) (citing Flint Ridge Dev. Co. v. Scenic Rivers Ass’n, 426 U.S. 776, 787–88 (1976), aff’d sub nom. Texaco Producing, Inc., 840 F.2d 776
(10th Cir. 1988); Grindstone Butte Project v. Kleppe, 638 F.2d 100, 103 (9th Cir. 1981);
Detroit Edison Co. v. U.S. Nuclear Reg. Comm’n, 630 F.2d 450 (6th Cir. 1980)).

[210] Anglers of the Au Sable v. U.S. Forest Serv. (Au Sable), 565 F. Supp. 2d 812, 815, 818
(D. Mich. 2008).

[211] Id. at 824–33 (identifying issues related to uniqueness, controversy and uncertainty; potential for setting precedent and cumulative impacts; and impacts to endangered species as having been insufficiently considered); see 40 C.F.R. § 1508.27(b)(1)–(10) (2009) (presenting the 10 Council on Environmental Quality intensity factors that guide determination of whether an agency action will significantly affect the environment, and thus whether an EIS needs to be prepared rather than a less rigorous EA).

[212] Au Sable, 565 F. Supp. 2d at 834.

[213] Id.

[214] See discussion infra Part V.D.1.b.

[215] Au Sable, 565 F. Supp. 2d at 835.

[216] Id. at 836.

[217] Id. at 840 (citing 43 C.F.R. § 3161.2 (2008), which provides that the BLM authorized officer is directed to require that operations protect natural resources and environmental quality).

[218] Id.

[219] National Environmental Policy Act of 1969, Pub. L. No. 91-190, 83 Stat. 852 (1970) (codified as amended at 42 U.S.C. §§ 4321–4347 (2006)).

[220] See discussion supra Parts IV.D, V.A.

[221] See supra note 57 and accompanying text.

[222] See supra note 57 and accompanying text.

[223] Energy Policy Act of 2005, 42 U.S.C. § 15942(b) (2006) (making provisions in subdivisions 1 and 3 that require prior NEPA compliance before the enumerated activity can be categorically excluded from further NEPA compliance).

[224] See National Environmental Policy Act of 1969, 42 U.S.C. § 4332 (2006) (requiring compliance with NEPA for major federal actions significantly affecting the quality of the human environment); Federal Land Policy and Management Act of 1976, 43 U.S.C. § 1712 (2006) (requiring BLM to develop land use plans); 43 C.F.R. § 1601.0-6 (2008) (“Approval of a resource management plan is considered a major Federal action significantly affecting the quality of the human environment.”).

[225] 43 U.S.C. § 1701(a)(8) (2006).

[226] Id. § 1701(a)(12) (citation omitted); see infra text accompanying notes 283–84.

[227] 43 U.S.C. § 1732(a) (2006) (“The Secretary shall manage the public lands under principles of multiple use and sustained yield, in accordance with the land use plans . . . .”).

[228] Id. § 1702(c); see also id. § 1702(h) (defining “sustained yield”).

[229] Id. § 1732(b).

[230] See Bureau of Land Mgmt., supra note 147, §§ 3101.06.B.2, 3101.06.B.2.a, 3101.06.B.3, 3101.12.A, 3101.13.A (making references to the unnecessary or undue degradation clause as being a basis for conditioning development, including statements that it “is within the terms of the lease, because all leases are subject to applicable laws and regulations” and “mitigation required to protect the lands from unnecessary and undue degradation is consistent with the lease rights granted”); Instruction Memorandum No. 2003-234 from Dir., Bureau of Land Mgmt., to All Field Officials (July 28, 2003) (on file with author) (stating that conditions of approval are not to exceed the limitations in the lease terms and conditions “unless warranted to prevent unnecessary and undue degradation or meet other regulatory requirements”).

[231] 292 F. Supp. 2d 30, 42 (D.D.C. 2003).

[232] Id. at 43.

[233] Id. at 42.

[234] 43 C.F.R. subpt. 3809 (2008) (presenting BLM’s hardrock mining regulations). “Unnecessary or undue degradation” is defined at id. § 3809.5.

[235] Utah v. Andrus, 486 F. Supp. 995, 1005 n.13 (D. Utah 1979) (quoting Brief for American Mining Congress as Amicus in Opposition to the United States’ Request for Permanent Injunction at 9, Utah v. Andrus, 486 F. Supp. 995 (Nos. C 79-0037, C 79-0307)).

[236] Biodiversity Conservation Alliance, 174 I.B.L.A. 1, 4–8 (2008) (applying a rational basis standard to determine whether BLM’s determination that a project would not cause UUD
was permissible).

[237] See discussion supra Part IV.C.3 (reviewing the guidance in IM 92-67 and BLM Manual MS-3101 as to reasonable measures developed to comply with the UUD clause).

[238] 16 U.S.C. §§ 1531–1544 (2006).

[239] See generally Bureau of Land Mgmt., U.S. Dep’t of the Interior, BLM Manual MS-6840, Special Status Species Management (2008), available at http://www.blm.gov/pgdata/etc/medialib/ blm/wo/Information_Resources_Management/policy/blm_manual.Par.43545.File.dat/6840.pdf(presenting BLM’s special status species manual, MS-6840, including policy regarding the ESA).

[240] See 16 U.S.C. § 1536(a)(2) (2006) (“Each Federal agency shall . . . insure that any action authorized, funded, or carried out by such agency . . . is not likely to jeopardize the continued existence of any endangered species or threatened species or result in the destruction or adverse modification of habitat of such species which is determined by the Secretary . . . to be critical . . . .”); id. § 1538(a)(1)(B) (making it unlawful for any person to “take any [endangered] species within the United States or the territorial sea of the United States”); see also Tenn. Valley Auth. v. Hill, 437 U.S. 153, 173 (1978) (“One would be hard pressed to find a statutory provision whose terms were any plainer than those in § 7 of the Endangered Species Act. Its very words affirmatively command all federal agencies ‘to insure that actions authorized, funded,
or carried out by them do not jeopardize the continued existence’ of an endangered species or ‘result in the destruction or modification of habitat of such species . . . .’ This language admits of no exception.” (alteration in original) (citation omitted) (quoting 16 U.S.C. § 1536 (1976))).

[241] 16 U.S.C. § 1536(a)(1) (2006) (“The Secretary [of the Interior] shall review other programs administered by him and utilize such programs in furtherance of the purposes of this chapter.”); id. § 1531(b) (providing that two purposes of the ESA are to provide a means for the conservation of ecosystems upon which listed species depend, and to provide a program for the conservation of listed species).

[242] Id. § 1536(a)(2).

[243] Id. § 1536(c).

[244] See id. § 1536(a)(3), (b)–(c); see also 50 C.F.R. § 402 (2008) (presenting FWS’s biological assessment, consultation, and biological opinion regulations).

[245] See, e.g., N. Alaska Envtl. Ctr. v. Kempthorne, 457 F.3d 969, 981 (9th Cir. 2006); Conner, 848 F.2d 1441, 1453–54 (9th Cir. 1988).

[246] Conner, 848 F.2d at 1453–54 (holding that failure to prepare a “comprehensive” biological opinion considering all stages of oil and gas development failed to adequately consider the potential for jeopardizing listed species, which violated the ESA); N. Alaska Envtl. Ctr., 457 F.3d at 981 (approving use of a leasing biological opinion based on a reasonable and foreseeable development scenario to meet the requirement to make projections of the impacts of production on protected species); Bob Marshall Alliance v. Hodel, 852 F.2d 1223, 1228
(9th Cir. 1988) (holding a leasing biological opinion must consider postleasing activities, which was absent in this case, so the ESA was violated); see also  Mont. Wilderness Ass’n v. Fry,
310 F. Supp. 2d 1127, 1150 (D. Mont. 2004) (holding the scope of the leasing action for ESA purposes “includes activities from leasing through post-production and abandonment,” but this requirement was not met in this case). In 1992, the Director of BLM issued an Information Bulletin to all BLM State Directors in response to the decision in Conner. Information Bulletin No. 92-198 from Dir., Bureau of Land Mgmt., to All State Dirs. (Jan. 21, 1992) (on file with author). In this Bulletin BLM stated, “The simple rule coming out of the Conner v. Burford case is that we will comply with NEPA and ESA prior to leasing.” Id. at 1. And, “[l]easing in areas where [listed species] are known to exist requires [FWS] Section 7 consultation.” Id. at 2.
Thus, BLM seems to view at least Conner as having application beyond the Ninth Circuit.

[247] Wilderness Soc’y v. Wisely, 524 F. Supp. 2d 1285, 1304–06 (D. Colo. 2007) (holding also that NEPA compliance was insufficient because a no surface occupancy alternative for the leases had been improperly rejected).

[248] Wyo. Outdoor Council v. Bosworth, 284 F. Supp. 2d 81, 90–93 (D.D.C. 2003) (holding in a case where earlier consultation had occurred when identifying areas that would be open for leasing, but which had not occurred when the decision to issue leases was made, that because BLM and the Forest Service retained authority to condition and even prohibit development, ESA challenges were not ripe); Wyo. Outdoor Council v. Dombeck, 148 F. Supp. 2d 1, 10 (D.D.C. 2001) (holding ESA challenges not ripe because leases had been sold but not actually issued).

[249] Bosworth, 284 F. Supp. 2d at 91.

[250] 16 U.S.C. §§ 470–470x-6 (2006). Section 106 is found at id. § 470f.

[251] Id.

[252] Id. § 470h-2(f).

[253] Id. §§ 470aa–470mm.

[254] Id. § 470ee(a).

[255] Id. §§ 703–712.

[256] Id. §§ 703, 704.

[257] Id. §§ 668–668d.

[258] Id. §§ 668(a), 668a.

[259] Id. §§ 1241–1251.

[260] Id. § 1244(a).

[261] Id. § 1246(i).

[262] Id. §§ 1271–1287.

[263] See id. § 1273(b).

[264] 42 U.S.C. §§ 7401–7671q (2006).

[265] Id. §§ 7401(b)(1), 7491(a)(1).

[266] See id. §§ 7408(a), 7409 (establishing the National Ambient Air Quality Standards); id. § 7411 (establishing new source performance standards for stationary sources).

[267] Id. § 7418(a).

[268] Federal Water Pollution Control Act, 33 U.S.C. §§ 1251–1387 (2006).

[269] Id. § 1251(a).

[270] See, e.g., id. § 1311(a) (prohibiting the discharge of any pollutants except when in compliance with the Act); id. § 1342 (establishing the National Pollution Discharge Elimination System and allowing states to administer the permit program).

[271] See, e.g., id. § 1313(d) (requiring states to identify state waters and establish for each the “total maximum daily load” of pollutants); id. § 1342 (establishing the National Pollution Discharge Elimination System, which requires a permit for specified discharges); id. § 1365 (authorizing citizen suits against any person for violations of an effluent standard or limitation).

[272] Id. § 1323(a).

[273] 42 U.S.C. §§ 6901–6992k (2006) (amending Solid Waste Disposal Act, Pub. L. No. 89-272, 79 Stat. 992 (1965)).

[274] 42 U.S.C. §§ 9601–9675 (2006).

[275] 15 U.S.C. §§ 2601–2692 (2006).

[276] 42 U.S.C. §§ 11001–11050 (2006).

[277] See generally Envtl. Prot. Agency, Crude Oil and Natural Gas Waste, http://www.epa.gov/
osw/nonhaz/industrial/special/oil/index.htm (last visited Apr. 18, 2010) (presenting provisions and policies related to exploration, development, and production of oil and gas under RCRA).

[278] See infra Part VIII.D.

[279] Noise Control Act of 1972, 42 U.S.C. § 4901(a)–(b) (2006).

[280] Id. § 4903(a).

[281] 43 C.F.R. § 3101.1-2 (2010).

[282] Energy Reorganization Act of 1974, 42 U.S.C. § 5801(a) (2006).

[283] Mining and Minerals Policy Act of 1970, 30 U.S.C. §§ 21a, 1901–1905 (2006).

[284] Id. § 21a.

[285] See Energy Policy Act of 1992, 42 U.S.C. § 13411(a) (2006) (directing the Secretary of Energy to seek to increase the recoverability of domestic oil resources); id. § 13413(a) (directing the Secretary of Energy to increase the recoverable natural gas resource base).

[286] 42 U.S.C. §§ 6201–6422 (2006). Section 604 of the Energy Policy and Conservation Act Amendments of 2000 is at id. § 6217 (2006).

[287] Id. § 6217(a). In response to this mandate, BLM has issued three reports intended to document the extent that federal onshore oil and gas resources are unavailable for development due to “restrictions or impediments,” having released those reports in three phases. See Bureau of Land Mgmt., U.S. Dep’t of the Interior, EPCA Phase III Inventory, http://www.blm.gov/wo/st/
en/prog/energy/oil_and_gas/EPCA_III.html (last visited Apr. 18, 2010) (presenting a BLM website containing the results of the EPCA inventories). BLM’s analyses have been subject to criticism. See The Wilderness Soc’y, “EPCA III” Fact Sheet 2 (2008), available at http://wilderness.org/files/EPCA_III_fact_sheet.pdf (arguing that 88% of onshore federal gas resources and 68% of onshore federal oil resources are available for development, contrary to BLM’s claims in its “EPCA III” report that only 59% of the gas and 37.8% of the oil is “accessible”).

[288] Energy Policy Act of 2005, 42 U.S.C. § 15921(a)(1) (2006).

[289] Id. § 15921(b)(1).

[290] Id. § 15921(b)(3).

[291] Id. § 15942(a)–(b)(5); see supra notes 57, 221–23 and accompanying text (discussing the Energy Policy Act categorical exclusions).

[292] Bureau of Land Mgmt., supra note 83, at 1.

[293] See supra Part V.B.

[294] Bureau of Land Mgmt., supra note 83, at 1.

[295] See discussion supra Part IV.B; see also Bureau of Land Mgmt., supra note 83, at 3.

[296] Bureau of Land Mgmt., supra note 83, at 3.

[297] Id. at 1.

[298] 43 C.F.R. § 3101.1-2 (2008).

[299] Id. § 3101.1-3.

[300] Id.

[301] Bureau of Land Mgmt., supra note 147, § 3101.13A.

[302] Id. § 3101.13A1(c).

[303] Id. § 3101.13A1(a).

[304] Id. § 3101.13A1(b).

[305] See, e.g., Wyo. State Office, Bureau of Land Mgmt., Notice of Competitive Oil and Gas Lease Sale (2010), available at http://www.blm.gov/pgdata/etc/medialib/blm/wy/programs/
energy/og/leasing/2010.Par.40252.File.dat/02list.pdf (presenting the different types of lease stipulations for BLM lease sales in Wyoming).

[306] See id. at 1–31.

[307] See, e.g., id. (presenting lease stipulations for BLM lease sales in Wyoming).

[308] Bureau of Land Mgmt., supra note 147, § 3101.13A.

[309] Id. § 3101.13B.

[310] Wyo. State Office, supra note 305, at 44–46.

[311] 43 C.F.R. § 3101.1-3 (2008).

[312] Cont’l Land Res., 162 I.B.L.A. 1, 5 (2004).

[313] Bureau of Land Mgmt., supra note 83, at 1.

[314] Bureau of Land Mgmt., supra note 147, § 3101.11B; Bureau of Land Mgmt., 1954 Lease Form, supra note 88, at 1; Bureau of Land Mgmt., 1965 Lease Form, supra note 88, at 1; Bureau of Land Mgmt., 1971 Lease Form, supra note 88, at 1.

[315] See discussion supra Part IV.C.

[316] See supra Part IV.

[317] See supra text accompanying notes 299–308.

[318] 43 C.F.R. § 3103.4-4(a) (2008); see also Mineral Leasing Act, 30 U.S.C. § 209 (2006) (providing that the Secretary of the Interior is authorized to suspend leases “in the interest of conservation of natural resources”).

[319] See supra notes 200–02 and accompanying text (citing Copper Valley Mach. Works, Inc., 653 F.2d 595, 600 (D.C. Cir. 1981), and its approval of the use of suspensions to avoid environmental harm as consistent with the ordinary meaning of the term “in the interest of conservation” of natural resources in 30 U.S.C. § 209).

[320] 43 C.F.R. § 3103.4-4(b), (d) (2008).

[321] However, there are provisions in the regulations that provide for consultation with non-BLM surface managing agencies prior to leasing and even a prohibition on leasing over surface managing agency objection in some cases (including Forest Service objection), and there are also special regulations that apply to leasing on National Wildlife Refuges. 43 C.F.R. §§ 3101.5-1, .5-2, .5-4, .7-1, .7-2 (2008).

[322] Oil and Gas Leasing, Geothermal Resources Leasing, 53 Fed. Reg. 17,340 (May 16, 1988) (codified at 43 C.F.R. pts. 3000–3260); Minerals Management, 53 Fed. Reg. 22,814 (June 17, 1988) (codified at 43 C.F.R. pts. 3000–3280). Limited amendments that do not implicate BLM’s retained rights relative to environmental protection have been made since 1988. See, e.g.,
Oil and Gas Lease Acreage Limitation Exemptions and Reinstatement of Oil and Gas Leases,
71 Fed. Reg. 14,821, 14,821–23 (Mar. 24, 2006) (codified at 43 C.F.R. pt. 3100); Oil and Gas Leasing, 70 Fed. Reg. 58,854, 58,874–75 (Oct. 7, 2005) (codified at 43 C.F.R. pts. 3000–3870);
Oil and Gas Leasing: Onshore Oil and Gas Operations, 66 Fed. Reg. 1883, 1892–94 (Jan. 10, 2001) (codified at 43 C.F.R. pts. 3100–3160); Promotion of Development, Reduction of Royalty on Heavy Oil, 61 Fed. Reg. 4748, 4750–52 (Feb. 8, 1996) (codified at 43 C.F.R. pt. 3100).

[323] See Thomas L. Sansonetti & William R. Murray, A Primer on the Federal Onshore Oil and Gas Leasing Reform Act of 1987 and Its Regulations, 25 Land & Water L. Rev. 375–76, 383 (1990) (discussing the adoption of FOOGLRA and related regulations).

[324] See 43 C.F.R. pt. 192 (1939); Minerals Management and Oil and Gas Leasing, 48 Fed. Reg. 33,648, 33,662–75 (July 22, 1983) (codified at 43 C.F.R. pts. 3100–3150); Reorganization and Revision of Chapter, 35 Fed. Reg. 9503, 9670 (June 13, 1970) (codified at 43 C.F.R. pts. 3100–3109); Revision of Regulations—Continued, 29 Fed. Reg. 4507 (Mar. 31, 1964) (codified at 43 C.F.R. pts. 3000–3129); Editorial Revision of Regulations, 19 Fed. Reg. 8835, 9011–19 (Dec. 23, 1954) (codified at 43 C.F.R. pt. 192); General Regulations Applicable to Mineral Permits, Leases and Licenses, 11 Fed. Reg. 12,952 (Nov. 1, 1946) (codified at 43 C.F.R. pts. 191–192); Oil and Gas Leases, 11 Fed. Reg. 9760 (Sept. 5, 1946) (codified at 43 C.F.R. pt. 192).

[325] 43 C.F.R. § 3101.1-2 (1983).

[326] E.g., 11 Fed. Reg. at 12,953 (requiring special stipulations for lands in national forests and reclamation projects); id. at 12,954 (providing for suspension of operations, production, and rental payments).

[327] See supra notes 106–09, 134 and accompanying text.

[328] See Bureau of Land Mgmt., supra note 147, § 3101.1.11B; see also Bureau of Land Mgmt., 1954 Lease Form, supra note 88, at 2; Bureau of Land Mgmt., 1965 Lease Form, supra note 88, at 2; Bureau of Land Mgmt., 1971 Lease Form, supra note 88, at 2.

[329] Bureau of Land Mgmt., 1984 Lease Form, supra note 84, at 1.

[330] See discussion infra Parts VI, VII.B.

[331] 43 C.F.R. pt. 3160 (2008).

[332] Id. § 3161.2.

[333] Id.

[334] Id. § 3162.1(a).

[335] Id. § 3162.3-1(f); see also Mineral Leasing Act of 1920, 30 U.S.C. § 226(g) (2006) (requiring “a plan of operations covering proposed surface-disturbing activities”).

[336] 43 C.F.R. § 3162.5-1(a) (2008).

[337] Id. “Conditions of approval” is a term of art in BLM and means requirements that BLM can impose based on a site-specific review but which were not necessarily provided for by stipulation. Presumably the “conditions of approval” referenced in 43 C.F.R. § 3162.5-1(a) are one form of a “reasonable measure[]” that can be required pursuant to 43 C.F.R. § 3101.1-2 and section six of the modern lease forms. 43 C.F.R. § 3102.1-2 (2009); Bureau of Land Mgmt., supra note 83. Best Management Practices (BMPs) are another type of protective measure that BLM encourages and can require, and is increasingly emphasizing. See supra text accompanying notes 289–90 (discussing BMP provisions in the Energy Policy Act of 2005); infra text accompanying notes 429–34, 577–81 (discussing BMPs and BMP provisions in The Gold Book).

[338] 43 C.F.R. § 3162.5-1(b) (2008).

[339] Id. § 3163.1(a)(3).

[340] Id. §§ 3161.2, 3162.1(a) (providing in both instances that operations are to result in the maximum ultimate recovery of oil and gas); see also id. § 3160.0-4 (providing that the objective of BLM’s oil and gas operations regulations “is to promote the orderly and efficient exploration, development and production of oil and gas”).

[341] No. Civ.A. 04-2152 (JDB), 2006 WL 696050 (D.D.C. Mar. 20, 2006).

[342] 5 U.S.C. §§ 551–559, 701–706, 1305, 3105, 3344, 4301, 5335, 5362, 7521 (2006); Blancett, 2006 WL 696050, at *6; see 5 U.S.C. § 706(1) (2006) (authorizing a reviewing court to “compel agency action unlawfully withheld or unreasonably delayed”); see also id. § 551(13) (defining “agency action” that is subject to judicial review under the Administrative Procedure Act as including five particular activities, including a “failure to act”).

[343] Blancett, 2006 WL 696050, at *1.

[344] Id. at *11.

[345] Id. at *6, *10.

[346] 542 U.S. 55 (2004).

[347] Blancett, 2006 WL 69050, at *6; see Norton, 542 U.S. at 64 (requiring that a cause of action under 5 U.S.C. § 706(1) “can proceed only where a plaintiff asserts that an agency failed to take discrete agency action that it is required to take” (emphasis added)).

[348] Blancett, 2006 WL 696050, at *11.

[349] See discussion infra Part IX. The court in Au Sable, 565 F. Supp. 2d 812 (E.D. Mich. 2008), also held claims that BLM and Forest Service actions violated 43 C.F.R. § 3161.2 were unsubstantiated. Id. at 840. However, that holding was based on a determination that “plaintiffs have not alleged any facts that would establish a violation of this regulation independent of their [successful] NEPA claim.” Id. Au Sable was not based on a consideration of whether the requirements to sustain a “failure to act” claim were met. Id.; see discussion supra Part V.B.2 (considering the court’s decision in Au Sable).

[350] Blancett, 2006 WL 696050, at *8.

[351] Oil and Gas Operating Regulations, 47 Fed. Reg. 47,758, 47,765–76 (Oct. 27, 1982) (codified at 43 C.F.R. pt. 3160 (1983)) (adopting final rule that, among other things, amended the language of 30 C.F.R. §§ 221.11, 221.12, 221.20, 221.23, and 221.30 with language identical to or similar to that found in the current regulations at 43 C.F.R. §§ 3161.2, 3162.1, 3162.3-1, and 3162.5-1).

[352] See id. at 47,758 (indicating rulemaking was undertaken by the Minerals
Management Service).

[353] Onshore Oil and Gas, General, 48 Fed. Reg. 36,582, 36,583 (Aug. 12, 1983) (codified at
43 C.F.R. pt. 3160 (1983)) (establishing, among other things, a form of the regulation at 43 C.F.R. § 3161.2 that is identical to the current version); see also 43 C.F.R. § 3161.2 (2006).

[354] See, e.g., Minerals Management, 53 Fed. Reg. 22,814, 22,846 (June 17, 1988) (codified at
43 C.F.R. pt. 3160 (1988)).

[355] Compare 43 C.F.R. pt. 3160 (1988), with 43 C.F.R. pt. 3160 (2008).

[356] Compare 43 C.F.R. pt. 3160 (1983), with 43 C.F.R. pt. 3160 (1988), and 43 C.F.R.
pt. 3160 (2008).

[357] Oil and Gas Operating Regulations, 7 Fed. Reg. 4132 (June 2, 1942) (codified at 30 C.F.R. pt. 221 (1944)).

[358] See supra text accompanying note 351.

[359] 30 C.F.R. § 221.32 (1944).

[360] Id. §§ 221.4, .18. An even older version of the operating regulations is found at 30 C.F.R. §§ 221.1–.56 (1939).

[361] Leases, Permits, and Easements, 46 Fed. Reg. 5772, 5777 (Jan. 19, 1981) (codified at
43 C.F.R. pt. 2920 (1981)).

[362] 43 C.F.R. § 2920.7(a) (2008). “Land use authorization” means “any authorization to use the public lands issued under this part” and “lease” means “an authorization to possess and use public lands for a fixed period of time.” Id. § 2920.0-5(c), (l).

[363] Id. § 2920.7(b)(2).

[364] Id. § 2920.7(b)(3).

[365] Id. § 2920.7(b)(4).

[366] Id. § 2920.7(c)(5).

[367] Id. § 2920.7(c)(6).

[368] Id. §§ 2920.9-1(c), -2.

[369] See supra notes 111–12, 176–77 and accompanying text.

[370] Federal Land Policy and Management Act of 1976, 43 U.S.C. § 1712(a) (2006) (stating that the Secretary of the Interior “shall . . . develop, maintain, and, when appropriate, revise land use plans”). See generally id. § 1712 (specifying land-use planning requirements); 43 C.F.R. §§ 1601.1-1 to -8 (2008) (presenting the objectives and policies for BLM’s planning regulations).

[371] See discussion supra Part III.A.1.

[372] 43 U.S.C. § 1732(a) (2006); see also 43 C.F.R. § 1610.5-3(a) (2008) (“All future resource management authorizations and actions . . . shall conform to the approved plan.”).

[373] See 2 Coggins & Glicksman, supra note 23, § 16:18, at 16-31 (noting that by 1987,
BLM had completed only 12 of 162 RMPs).

[374] Bureau of Land Mgmt., 1954 Lease Form, supra note 88, at 1; Bureau of Land Mgmt.,
1965 Lease Form, supra note 88, at 1; Bureau of Land Mgmt., 1971 Lease Form, supra note 88, at 1.

[375] Bureau of Land Mgmt., supra note 83, at 1.

[376] See discussion supra Part III.A.1.

[377] Bureau of Land Mgmt., U.S. Dep’t of the Interior, Land Use Planning Handbook 23–24 (2005), available at http://www.blm.gov/pgdata/etc/medialib/blm/ak/aktest/planning/planning_
general.Par.65225.File.dat/blm_lup_handbook.pdf; see also Bureau of Land Mgmt., U.S. Dep’t of the Interior, BLM Planning for Fluid Mineral Resources (1990) [hereinafter Bureau of Land Mgmt., Fluid Mineral Handbook] (outlining similar provisions). Provisions in this handbook are discussed below. See infra Part V.D.2.d.

[378] 43 C.F.R. § 3164.1(a) (2008).

[379] See Bureau of Land Mgmt., U.S. Dep’t of the Interior, Onshore Operations, http://www.blm.gov/wy/st/en/programs/energy/Oil_and_Gas/Onshore_Operations.html (listing BLM’s active onshore orders) (last visited Apr. 18, 2010).

[380] 43 C.F.R. § 3164.1(b) (2008).

[381] See generally Bureau of Land Mgmt., U.S. Dep’t of the Interior, Onshore Oil and Gas Order No. 1, http://www.blm.gov/wo/st/en/prog/energy/oil_and_gas/Onshore_Order_no1.html (last visited Apr. 18, 2010) (containing links to background information regarding Onshore Oil and Gas Order Number 1).

[382] Onshore Oil and Gas Order No. 1, 48 Fed. Reg. 48,916 (Oct. 21, 1983).

[383] Onshore Oil and Gas Operations, 72 Fed. Reg. 10,308 (Mar. 7, 2007).

[384] Id.

[385] Id.

[386] Id. at 10,331–33.

[387] Id. at 10,332–33 (subsections describing methods for handling waste and plans for
surface reclamation).

[388] Id. at 10,333–34 (subsections describing APD posting and processing and APD approval).

[389] Id. at 10,334.

[390] Id.

[391] See discussion supra Part IV.C.2–3 (arguing reasonable measures are not limited to those specified in the 200-meter 60-day rule).

[392] See Onshore Oil and Gas Operations, 72 Fed. Reg. at 10,335; see also discussion supra Part IV.C.3 (arguing the clear and convincing evidence standard in IM 92-67 and BLM Manual MS-3101 is unwarranted).

[393] Onshore Oil and Gas Operations, 72 Fed. Reg. at 10,335.

[394] Id. Onshore Order Number 1 also makes provisions related to waiver, exemption, or modification of lease stipulations. Id. at 10,337; see also 43 C.F.R. § 3101.1-4 (2008) (establishing similar provisions for modification and waiver of stipulations).

[395] See Onshore Oil and Gas Order No. 1, 48 Fed. Reg. 48,916 (Oct. 21, 1983); supra notes 381–83 and accompanying text.

[396] See supra Part IV.B.

[397] 43 C.F.R. § 3164.2(a) (2008).

[398] Id. § 3160.0-5.

[399] Bureau of Land Mgmt., U.S. Dep’t of the Interior, Oil & Gas Operations, http://www.blm.gov/wy/st/en/programs/energy/Oil_and_Gas/Onshore_Operations.html (last visited Apr. 18, 2010).

[400] See Bureau of Land Mgmt., U.S. Dep’t of the Interior, Notice to Lessee/Operators of Onshore Federal and Indian Oil and Gas Leases Within the Jurisdiction of the Wyoming State Office (NTL 2004-1) (2004), available at http://www.blm.gov/pgdata/etc/medialib/blm/wy/
programs/energy/og/ogdocs.Par.7786.File.dat/04wy-efcntl.pdf.

[401] See U.S. Geological Survey, U.S. Dep’t of the Interior, Notice to Lessees and Operators of Onshore Federal and Indian Oil and Gas Leases (NTL-3A) (1979),
available at http://www.blm.gov/pgdata/etc/medialib/blm/co/programs/oil_and_gas.Par.49503. File.dat/ntl3a.pdf. Undesirable events include spills of toxic liquids of 100 or more barrels, equipment failures or other accidents that result in the venting of certain volumes of gas, fires, blowouts of wells, accidents involving fatal injuries, and “[a]ny spill, venting, or fire, regardless of the volume involved, which occurs in a sensitive area, e.g., areas such as parks, recreation sites, wildlife refuges, lakes, reservoirs, streams, and urban or suburban areas.” Id. at 1–2.

[402] See Bureau of Land Mgmt., U.S. Dep’t of the Interior, Notice to Lessees and Operators of Onshore Federal and Indian Oil and Gas Leases (NTL-4A) (1980), available at http://www.blm.gov/pgdata/etc/medialib/blm/ak/aktest/energy/og_forms.Par.32669.File.dat/ntl4a.pdf.

[403] Bureau of Land Mgmt., supra note 399.

[404] Telephone Interview with Julie Weaver, Chief, Branch of Fluid Minerals Adjudication, Wyo. State Office, Bureau of Land Mgmt. (Oct. 8, 2009) (on file with author).

[405] Bureau of Land Mgmt., U.S. Dep’t of the Interior, BLM Manual, http://www.blm.gov/wo/st/en/info/regulations/Instruction_Memos_and_Bulletins/blm_manual.html (last visited Apr. 18, 2010) [hereinafter BLM Manual]; Bureau of Land Mgmt., U.S. Dep’t of the Interior, BLM Handbooks, http://www.blm.gov/wo/st/en/info/regulations/Instruction_ Memos_and_Bulletins/ blm_handbooks.html (last visited on Apr. 18, 2010) [hereinafter BLM Handbooks]. The Department of Interior also has a manual. U.S. Dep’t of the Interior, ELIPS Electronic Library of Interior Policies, http://206.131.241.18/app_dm/index.cfm?fuseaction=home (last visited Apr. 18, 2010).

[406] BLM Manual, supra note 405.

[407] BLM Handbooks, supra note 405.

[408] Id.

[409] See 5 U.S.C. § 553 (2006) (specifying the Administrative Procedure Act rulemaking provisions).

[410] See 43 C.F.R. § 3162.1(a) (2008) (providing that operating rights owners shall comply “with other orders and instructions of the authorized officer” (emphasis added)).

[411] See BLM Manual, supra note 405 (presenting BLM manual sections).

[412] See BLM Handbooks, supra note 405 (presenting BLM handbook sections).

[413] Bureau of Land Mgmt., Fluid Mineral Handbook, supra note 377. It makes many provisions, including specifying that stipulations are to be the least restrictive possible,
 id. at III-11, providing for certain determinations in the RMP for some oil and gas lease decision making, see id. at IV-1, and providing that “[c]onstraints in the form of conditions of approval (COAs) on applications for permit to drill (APD’s) are site specific requirements or measures imposed to protect resources or resource values. COAs must be reasonable and consistent with lease rights.” Id. at IV-2.

[414] See supra notes 147, 191, 314 and accompanying text.

[415] Bureau of Land Mgmt., U.S. Dep’t of the Interior, National Instruction
Memoranda, http://www.blm.gov/wo/st/en/info/regulations/Instruction_Memos_and_Bulletins/ national_instruction.html (last visited Apr. 18, 2010).

[416] Id.

[417] See, e.g., Instruction Memorandum No. 2010-037 from Dir., Bureau of Land Mgmt., to All State Directors (Dec. 18, 2009), http://www.blm.gov/wo/st/en/info/regulations/Instruction_
Memos_and_Bulletins/national_instruction/2010/im_2010-037__tribal.html (last visited Apr. 18, 2010); Instruction Memorandum No. 2009-167 from Dir., Bureau of Land Mgmt., to All Field Officials (July 7, 2009), http://www.blm.gov/wo/st/en/info/regulations/Instruction_Memos_and_
Bulletins/national_instruction/2009/IM_2009-167.html (last visited Apr. 18, 2010); Instruction Memorandum No. WY-2010-017 from State Dir., Bureau of Land Mgmt., Wyo. State Office to All Employees (Jan. 26, 2010), available at http://www.blm.gov/pgdata/etc/medialib/blm/wy/
resources/efoia/IMs/2010.Par.14095.File.dat/wy2010-017.pdf.

[418] See, e.g., Instruction Memorandum No. 2010-025 from Assistant Dir., Minerals & Realty Mgmt., Bureau of Land Mgmt., to All Field Officials (Dec. 4, 2009), http://www.blm.gov/wo/st/en/
info/regulations/Instruction_Memos_and_Bulletins/national_instruction/2010/IM_2010-025.html
(last visited Apr. 18, 2010) (expiring September 30, 2011).

[419] See Yates Petroleum Corp., 176 I.B.L.A. 144, 159 n.16 (2008) (pointing out that it was “BLM practice to continue using the guidance contained in [a] memorandum” issued by the BLM Wyoming State Office (IM No. WY-90-231) even though the IM had expired).

[420] See Instruction Memorandum No. 2009-225 from Assistant Dir., Minerals & Realty Mgmt., Bureau of Land Mgmt., to All Field Officials (Sept. 30, 2009), http://www.blm.gov/wo/st/ en/info/regulations/Instruction_Memos_and_Bulletins/national_instruction/2009/IM_2009-225.html (last visited Apr. 18, 2010); Instruction Memorandum No. 2009-078 from Assistant Dir., Minerals & Realty Mgmt., Bureau of Land Mgmt., to All Field Officials (Feb. 20, 2009), http://www.blm.gov/ wo/st/en/info/regulations/Instruction_Memos_and_Bulletins/national_instruction/2009/IM_2009-078.html (last visited Apr. 18, 2010); Instruction Memorandum No. 2009-044 from Dir., Bureau of Land Mgmt., to All Wash. Office & Field Officials (Dec. 19, 2008), http://www.blm.gov/wo/st/ en/info/regulations/Instruction_Memos_and_Bulletins/national_instruction/2009/IM_2009-044.html (last visited Apr. 18, 2010); Instruction Memorandum No. 2009-011 from Assistant Dir., Renewable Res. & Planning, Bureau of Land Mgmt., to All State Dirs. (Oct. 10, 2008), http://www.blm.gov/wo/st/en/info/regulations/Instruction_Memos_and_Bulletins/national_ instruction/2009/IM_2009-011.html (last visited Apr. 18, 2010).

[421] Instruction Memorandum No. 2009-225 from Assistant Dir. to All Field Officials,
supra
note 420.

[422] Instruction Memorandum No. 2009-078 from Assistant Dir. to All Field Officials,
supra note 420.

[423] Instruction Memorandum No. 2009-044 from Dir. to All Wash. Office & Field Officials, supra note 420.

[424] Instruction Memorandum No. 2009-011 from Assistant Dir. to All State Dirs., supra note 420.

[425] See, e.g., Instruction Memorandum No. 2002-053, from the Dir., Bureau of Land Mgmt., to All State Dirs., Assistant Dirs. & Field Officials (Dec. 12, 2001) (expiring September 30, 2003) (on file with author) (requiring preparation of a statement of adverse energy impacts); Instruction Memorandum No. 2003-233, from Dir., Bureau of Land Mgmt., to State Dirs. (July 28, 2003) (expiring September 30, 2004) (on file with author) (requiring use of the least restrictive mitigation); Instruction Memorandum No. 2003-234, from Dir., Bureau of Land Mgmt., to All Field Officials (July 28, 2003) (expiring September 30, 2004) (on file with author) (requiring use of the least restrictive mitigation); Instruction Memorandum No. 2004-110, from Dir., Bureau of Land Mgmt., to All WO & FO Officials (Feb. 23, 2004) (expiring September 30, 2005) (on file with author) (guiding leasing decisions during RMP revision); Instructional Memorandum No. 2004-110 Change 1, from Dir., Bureau of Land Mgmt., to All WO & FO Officials (Aug. 13, 2004) (expiring September 30, 2005) (on file with author) (guiding leasing decisions during RMP revision); Instruction Memorandum No. 2005-235, from Dir., Bureau of Land Mgmt., to AFOs (Sept. 13, 2005) (expiring September 30, 2006) (on file with author) (presenting APD processing timelines to comply with the Energy Policy Act of 2005); Instruction Memorandum No. 2007‑021, from Dir., Bureau of Land Mgmt., to All Field Officials (Nov. 8, 2006) (expiring September 30, 2008), http://www.blm.gov/wo/st/en/info/regulations/Instruction _Memos_and_Bulletins/national_instruction/2007/im_2007-021__.html (last visited Apr. 18, 2010) (providing for the use of best management practices). As mentioned, IMs issued since 1999 are available on the BLM website. See supra text accompanying note 415. See supra Part IV.C.3 for a discussion of IM 92-67, which is not available on the BLM website.

[426] Bureau of Land Mgmt., Surface Operating Standards and Guidelines for Oil and Gas Exploration and Development: The Gold Book (4th ed. 2007), available at http://www.blm.gov/pgdata/etc/medialib/blm/wo/MINERALS__REALTY__AND_RESOURCE_PROTECTION_/energy/oil_and_gas.Par.18714.File.dat/OILgas.pdf.

[427] See 43 C.F.R. § 3162.1(a) (2008) (providing that operating rights owners shall comply “with other orders and instructions of the authorized officer” (emphasis added)).

[428] Bureau of Land Mgmt., supra note 426, at 1.

[429] Id. at 2.

[430] Id. at 3.

[431] See id. at 9.

[432] Id. at 15.

[433] See id. at 15–36.

[434] Id. at 37.

[435] Id.

[436] Id.

[437] Id. at 38–41.

[438] See id. at 43–47, 49.

[439] Exec. Order No. 11,990, 3 C.F.R. 121 (1978), reprinted as amended in 42 U.S.C. § 4321 (2006); Exec. Order No. 11,988, 3 C.F.R. 117 (1978), reprinted as amended in 42 U.S.C. § 4321 (2006).

[440] Exec. Order No. 12,088, 3 C.F.R. 243 (1979), reprinted as amended in 42 U.S.C. § 4321 (2006).

[441] Exec. Order No. 11,593, 3 C.F.R. 559 (1971–1975), reprinted in 16 U.S.C. § 470 (2006).

[442] Exec. Order No. 13,186, 3 C.F.R. 719 (2002), reprinted in 16 U.S.C. § 701 (2006).

[443] Exec. Order No. 13,211, 3 C.F.R. 767 (2002), reprinted in 42 U.S.C. § 13201 (2006).

[444] Exec. Order No. 13,212, 3 C.F.R. 769 (2002), reprinted as amended in 42 U.S.C. § 13201 (2006).

[445] Id.

[446] U.S. Dep’t of Interior, ELIPS Electronic Library of Interior Policies: Secretary’s Orders, http://elips.doi.gov/app_so/index.cfm?fuseaction=home (last visited Apr. 18, 2010) (listing orders issued by the Secretary of the Interior); U.S. Dep’t of Interior, Office of the Solicitor—Solicitor’s Opinions, http://www.doi.gov/solicitor/opinions.html (last visited Apr. 18, 2010) (listing opinions of the Solicitor of the U.S. Department of the Interior).

[447] Sec’y of the Interior, Order No. 3294 (Jan. 6, 2010), available at http://www.interior.gov/
documents/Order_3294.pdf.

[448] See Press Release, U.S. Dep’t of Interior, Secretary Salazar Launches Onshore Oil and Gas Leasing Reforms to Improve Certainty, Reduce Conflicts and Restore Balance on U.S. Lands (Jan. 6, 2009), http://www.interior.gov/news/09_News_Releases/010610.html (last visited
Apr. 18, 2010) (presenting new policies that apply to BLM oil and gas leasing).

[449] See discussion supra Parts IV.B, IV.C.2–3.

[450] See discussion supra Part IV.C.1.

[451] 530 U.S. 604 (2000).

[452] Id. at 604, 618, 620, 621, 624.

[453] Id. at 607 (quoting United States v. Winstar Corp., 518 U.S. 839, 895 (1996) (plurality opinion) (internal quotation marks omitted)).

[454] Id. at 608 (citing Restatement (Second) of Contracts §§ 243, 250, 373 (1981), to explain remedies for a repudiation and define the terms “total breach” and “repudiation”).

[455] 538 F.3d 1358 (Fed. Cir. 2008).

[456] Id. at 1374.

[457] Id. at 1368, 1371–74.

[458] Followwill v. Merit Energy Co., 371 F. Supp. 2d 1305, 1309 (D. Wyo. 2005).

[459] Id. (citing Wyoming Supreme Court cases).

[460] Id.

[461] Barlow & Haun, Inc. v. United States, 87 Fed. Cl. 428, 431–32 (2009). Trona is a
sodium-rich mineral that is processed into soda ash, which is used in manufacturing many products, such as glass, soap, and paper. Id. at 431.

[462] Id. at 435–36.

[463] 17A Am. Jur. 2d Contracts § 329 (2004).

[464] Id.

[465] Id. § 330; see also Restatement (Second) of Contracts ch. 9, topic 5, introductory note (1979) (“The terms of the agreement or promise to a large extent define the obligation created.”).

[466] 17A Am. Jur. 2d Contracts § 331 (2004).

[467] Id.

[468] Id.

[469] Id. § 345.

[470] Id. § 348.

[471] Id. § 368. Conditions in a contract may also be express or implied. Id. § 454; see also Restatement (Second) of Contracts § 204 (1979) (stating that, where a term is essential to the determination of rights and duties under a contract, “a term which is reasonable in the circumstances is supplied by the court”).

[472] 17A Am. Jur. 2d Contracts § 343 (2004).

[473] Id. § 397; see id. § 339 (“A contract should be construed liberally to protect the public interest where that is involved in the case.”); Restatement (Second) of Contracts § 207 (1979) (“In choosing among the reasonable meanings of a promise or agreement or a term thereof, a meaning that serves the public interest is generally preferred.”).

[474] See 17A Am. Jur. 2d Contracts § 370 (2004); Restatement (Second) of Contracts
§ 205 (1979).

[475] 17A Am. Jur. 2d Contracts § 371 (2004).

[476] Id. §§ 371–372.

[477] See Restatement (Second) of Contracts ch. 9, topic 3, introductory note (1979) (discussing the effects of adoption of a writing as the final expression of agreement, referred to as an “integrated agreement,” the principal effect of which is “to focus interpretation on the meaning of the terms embodied in the writing”).

[478] See, e.g., Conner, 848 F.2d 1441, 1453 (9th Cir. 1988) (analyzing onshore leases and agreeing with the District of Columbia Circuit Court of Appeals’ view expressed in an offshore leasing case that “[p]umping oil and not leasing tracts is the aim of congressional [mineral leasing] policy” (quoting N. Slope Borough v. Andrus, 642 F.2d 589, 608 (D.C. Cir. 1980) (internal quotation marks omitted))); see also Devon Energy Corp. v. United States, 45 Fed. Cl. 519, 521 (1999) (finding that in passing the Mineral Leasing Act, Congress “sought to promote the orderly development of oil and gas deposits in publicly owned lands of the United States”
(citation omitted)).

[479] Bureau of Land Mgmt., supra note 83, at 1; see also 43 C.F.R. § 3101.1-2 (2008) (“A lessee shall have the right to use so much of the leased lands as is necessary to explore for, drill for, mine, extract, remove and dispose of all the leased resource in a leasehold . . . .”).

[480] Bureau of Land Mgmt., 1954 Lease Form, supra note 88, at 2; Bureau of Land Mgmt., 1965 Lease Form, supra note 88, at 2; Bureau of Land Mgmt., 1971 Lease Form, supra
note 88, at 2.

[481] Bureau of Land Mgmt., supra note 83, at 1.

[482] 43 C.F.R. § 3101.1-2 (2008) (making leases subject to stipulations, specific, nondiscretionary statutes, and reasonable measures that might be required).

[483] Bureau of Land Mgmt., 1954 Lease Form, supra note 88, at 2 (“The lessee agrees . . . [t]o take such reasonable steps as may be needed to prevent operations from unnecessarily:
(1) Causing or contributing to soil erosion or damaging any forage and timber growth thereon, (2) polluting the waters of the reservoirs, springs, streams, or wells . . . .”); Bureau of Land Mgmt., 1965 Lease Form, supra note 88, at 2 (requiring the same “reasonable steps”);
Bureau of Land Mgmt., 1971 Lease Form, supra note 88, at 2 (same).

[484] Boesche v. Udall, 373 U.S. 472, 477–78 (1963) (finding that onshore leases are subjected to exacting restrictions and are governed by the Secretary of the Interior in minute detail);
see supra Part V.A.

[485] Bureau of Land Mgmt., supra note 83, at 3 (emphasis added); see also 43 C.F.R. § 3101.1‑2 (2008) (stating that the right to develop oil and gas is subject to “such reasonable measures as may be required by the authorized officer to minimize adverse impacts to other resource values, land uses, or users” and that such reasonable measures include “but are not limited to” modification of the siting or design of facilities, timing of operations, and specification of reclamation measures); supra Parts IV.B, IV.C.2–3 (analyzing the reasonable measures provision). This same language is used in the July 2006 version of the modern lease form. Bureau of Land Mgmt., 2006 Lease Form, supra note 84, at 2. In the March 1984, June 1988, October 1992, and February 2003 versions of the modern lease form, “shall” was used rather than “must.” Bureau of Land Mgmt., 1984 Lease Form, supra note 84, at 2; Bureau of Land Mgmt., 1988 Lease Form, supra note 84, at 2; Bureau of Land Mgmt., 1992 Lease Form, supra note 84, at 2; Bureau of Land Mgmt., 2003 Lease Form, supra note 84, at 2.

[486] Bureau of Land Mgmt., supra note 83, at 3 (emphasis added).

[487] 176 I.B.L.A. 144 (2008).

[488] Id. at 155–56; see also Nat’l Wildlife Fed’n, 169 I.B.L.A. 145, 164 (2006) (holding BLM has authority to restrict the siting and timing of lease activities).

[489] 17A Am. Jur. 2d Contracts § 397 (2004).

[490] See Bureau of Land Mgmt., supra note 83, at 1.

[491] 43 C.F.R. § 3101.1-2 (2008).

[492] See supra Part IV.D.

[493] Bureau of Land Mgmt., 1954 Lease Form, supra note 88, at 2; Bureau of Land Mgmt., 1965 Lease Form, supra note 88, at 2; Bureau of Land Mgmt., 1971 Lease Form, supra
note 88, at 2.

[494] Black’s Law Dictionary 1029 (6th ed. 1990).

[495] Id.; see also 28 Words & Phrases 188–236 (perm. ed. 2003) (presenting judicial interpretations of the word “necessary” that generally indicate it does not mean an absolute right); id. at 23–31 (Supp. 2009) (presenting additional judicial interpretations of the word “necessary” that generally indicate it does not mean an absolute right).

[496] Bureau of Land Mgmt., supra note 83, at 1.

[497] 43 C.F.R. § 3101.1-2 (2008).

[498] See discussion supra Part V.

[499] See Black’s Law Dictionary 1029 (6th ed. 1990) (defining “necessary”).

[500] Restatement (Second) of Contracts § 250(a)–(b) (1979).

[501] Id. § 243.

[502] Mobil Oil, 530 U.S. 604, 609 (2000).

[503] Outer Banks Protection Act, Pub. L. No. 101–380, § 6003, 104 Stat. 555, 556 (1990), repealed by Pub. L. No. 104–134, § 109, 110 Stat. 1321, 1321-177 (1996).

[504] Mobil Oil, 530 U.S. at 609–14.

[505] Id. at 607, 618, 620, 624.

[506] Id. at 609, 615.

[507] Id. at 615–17. The leases were made subject to the OCSLA, sections 302 and 303 of the Department of Energy Organization Act, 42 U.S.C. §§ 7152–7153 (2006), regulations issued pursuant to these statutes in existence when the lease was issued, future regulations issued under these statues that provided for the prevention of waste and conservation of resources, and “all other applicable statutes and regulations.” Id. at 615.

[508] Id. at 616.

[509] Id.

[510] E.g., Bureau of Land Mgmt., supra note 83, at 1.

[511] Mobil Oil, 530 U.S. at 609.

[512] See id. at 616.

[513] Id. at 620.

[514] Id. at 620–21. While the Court’s statements regarding a “gateway” and the contract creating only an “opportunity” to pursue development were made in the context of outer continental shelf leases issued under the OCSLA, not onshore Mineral Leasing Act leases, this language probably has application to onshore leases as well, which are also conditional in nature. See Boesche v. Udall, 373 U.S. 472, 477–78 (1963) (describing how onshore lease rights are subject to “restrictions and continuing supervision”); see discussion supra Part V.A.

[515] See discussion supra Parts IV.B, IV.C.2–3.

[516] See discussion supra Part IV.C.2.

[517] Bureau of Land Mgmt., supra note 83, at 3; 43 C.F.R. § 3101.1-2 (2008).

[518] Bureau of Land Mgmt., supra note 83, at 3; 43 C.F.R. § 3101.1-2 (2008).

[519] 43 C.F.R. § 3101.1-2 (2008).

[520] E.g., Yates Petroleum Corp., 176 I.B.L.A. 144, 155–56 (2008).

[521] See, e.g., Bob Marshall Alliance, 852 F.2d 1223, 1227 (9th Cir. 1988); Conner, 848 F.2d 1441, 1451 (9th Cir. 1988); Sierra Club, 717 F.2d 1409, 1414–15 (D.C. Cir. 1983). Use of the terms “irreversible” and “irretrievable” in these cases is likely linked to the provision in NEPA that requires an EIS to consider “any irreversible and irretrievable commitments of resources which would be involved in the proposed action should it be implemented.” National Environmental Policy Act of 1969, 42 U.S.C. § 4332(2)(C)(v) (2006).

[522] Bob Marshall Alliance, 852 F.2d at 1227; Conner, 848 F.2d at 1444–45; Sierra Club,
717 F.2d at 1414.

[523] Sierra Club, 717 F.2d at 1414 (determining also that the decision to allow surface disturbance has been made at the leasing stage absent an NSO stipulation and that this represents an “irrevocable commitment” to allow some surface disturbance).

[524] Id. at 1415.

[525] Conner, 848 F.2d at 1451 (internal quotation marks omitted) (recognizing also that leasing that does not absolutely preclude surface disturbance represents an irretrievable commitment of resources).

[526] Id. at 1450.

[527] Bob Marshall Alliance, 852 F.2d at 1225, 1227.

[528] 457 F.3d 969 (9th Cir. 2006).

[529] Id. at 976.

[530] Id. at 975–77.

[531] 565 F.3d 683 (10th Cir. 2009).

[532] Id. at 718–19. New Mexico ex rel. Richardson appears to differ from, or certainly elaborate on, Tenth Circuit precedent. See Park County Res. Council, Inc. v. U.S. Dep’t of Agric., 817 F.2d 609, 624 (10th Cir. 1987), overruled on other grounds by Vill. of Los Ranchos de Albuquerque v. Marsh, 956 F.2d 970, 973 (10th Cir. 1992). In Park County Resource Council, the Tenth Circuit allowed leasing to go forward prior to preparation of a leasing EIS. Id. at 624.
The court determined that the leasing was not “unreasonable” because of the preparation of a substantial EA, the requirements for further mitigation measures prior to surface disturbance, the nebulousness of future drilling plans at the leasing stage, and the continuing supervision by federal agencies. Id.; see also Pennaco Energy, Inc. v. U.S. Dep’t of the Interior, 377 F.3d 1147, 1161–62 (10th Cir. 2004) (discussing NEPA requirements at the leasing stage in the context of coal bed methane leases and distinguishing Park County Resource Council). In another case, a challenge to 16 leases sold and issued in Utah, a district court held that the preleasing NEPA analysis was insufficient where the underlying land use plans used to support the leasing decision had not considered a no-leasing alternative and where BLM’s NEPA analysis was not supplemented to consider new information regarding wilderness characteristics on the lands at issue. S. Utah Wilderness Alliance v. Norton, 457 F. Supp. 2d 1253, 1264, 1267, 1269 (D. Utah 2006).

[533] Wilderness Society v. Salazar, 603. F. Supp. 2d 52, 60 (D.D.C. 2009) (presenting in both cases further analyses of NEPA compliance requirements at the leasing stage, including
site-specific impact analysis needs and consideration of the irreversible and irretrievable commitment of resources question); see also Pit River Tribe v. U.S. Forest Serv., 469 F.3d 768, 785–86 (9th Cir. 2006) (same); Ctr. for Native Ecosystems, 170 I.B.L.A. 331, 345 (2006) (citing
S. Utah Wilderness Alliance, 166 I.B.L.A. 270, 276–77 (2005)).

[534] See Richardson, 565 F.3d at 689; Bob Marshall Alliance, 852 F.2d 1223, 1227 (9th Cir. 1988); Conner, 848 F.2d 1441, 1443 (9th Cir. 1988); Sierra Club, 717 F.2d 1409, 1410 (D.C. Cir. 1983);
Park County Res. Council, 817 F.2d at 612–13; Northern Alaska, 457 F.3d at 976; Pennaco Energy, 377 F.3d at 1161–62; see also Marla E. Mansfield, Through the Forest of the Onshore Oil and Gas Leasing Controversy Toward a Paradigm of Meaningful NEPA Compliance, 24 Land & Water L. Rev. 85 (1989) (analyzing the decisions in Conner, Sierra Club, and Park County Resource Council and suggesting approaches to NEPA compliance at the leasing stage).

[535] Richardson, 565 F.3d at 716; Bob Marshall Alliance, 852 F.2d at 1225; Conner, 848 F.2d
at 1448–49; Sierra Club, 717 F.2d at 1412.

[536] Richardson, 565 F.3d at 718–19; Bob Marshall Alliance, 852 F.2d at 1225, 1227; Conner, 848 F.2d at 1449–50; Sierra Club, 717 F.2d at 1415.

[537] See Conner, 848 F.2d at 1444; Park County Res. Council, 817 F.2d at 622.

[538] Sierra Club, 717 F.2d at 1411–12, 1414.

[539] Conner, 848 F.2d at 1448, 1450.

[540] Northern Alaska, 457 F.3d 969, 976 (9th Cir. 2006).

[541] 284 F. Supp. 2d 81 (D.D.C. 2003).

[542] Id. at 92. See generally Michael D. Axline, Private Rights to Public Oil and Gas, 19 Idaho L. Rev. 505 (1983) (arguing BLM has authority to preclude lease development based on protective stipulations, particularly when  engaging in NEPA analysis at the APD stage).

[543] U.S. Const. amend V.

[544] Barlow & Haun, 87 Fed. Cl. 428, 438 (2009) (quoting Hughes Commc’ns Galaxy, Inc. v. United States, 271 F.3d 1060, 1070 (Fed. Cir. 2001) (internal quotation marks omitted));
see supra note 461 and accompanying text (discussing Barlow & Haun).

[545] Barlow & Haun, 87 Fed. Cl. at 438 (citing Sun Oil Co. v. United States, 572 F.2d 786,
818–19 (Ct. Cl. 1978)).

[546] See supra text accompanying notes 451–54, 502–13 (discussing Mobil Oil,
530 U.S. 604 (2000)).

[547] Barlow & Haun, 87 Fed. Cl. at 439–40 (holding at the motion to dismiss stage of a case involving BLM oil and gas leases that “[t]he Court is unable to ascertain . . . whether all the rights that plaintiffs allege have been taken were reduced to writing by the parties” and therefore denying the motion to dismiss the takings claims at that stage of the proceedings).

[548] See, e.g., Bureau of Land Mgmt., supra note 83 (presenting the current version of BLM’s standard oil and gas leasing form).

[549] See, for example, Tahoe-Sierra Pres. Council, Inc. v. Tahoe Reg’l Planning Agency,
535 U.S. 302 (2002), and cases cited therein.

[550] Bureau of Land Mgmt., supra note 83, at 3.

[551] Bureau of Land Mgmt., 1954 Lease Form, supra note 88, at 2; Bureau of Land Mgmt., 1965 Lease Form, supra note 88, at 2; Bureau of Land Mgmt., 1971 Lease Form, supra
note 88, at 2.

[552] Mineral Leasing Act, 30 U.S.C. § 187 (2006).

[553] See 43 C.F.R. §§ 3162.2-1 to -15 (2008) (presenting BLM’s drilling and producing requirements and regulations governing drainage).

[554] Bureau of Land Mgmt., Split Estate: Rights, Responsibilities, and Opportunities 2 (2007), available at http://www.blm.gov/pgdata/etc/medialib/blm/wo/MINERALS__REALTY__
AND_RESOURCE_PROTECTION_/bmps.Par.57486.File.dat/SplitEstate07.pdf.

[555] Id.

[556] Id.

[557] Id.

[558] Id. (emphasis omitted).

[559] Id.

[560] See discussion supra Parts IV.B–C, V.

[561] See discussion supra Part IV.B–C.

[562] See supra Part V.C.

[563] Powder River Basin Res. Council, 120 I.B.L.A. 47, 55 (1991) (“[A]n alternative under which development would be limited was both obvious and reasonable.”).

[564] Northern Plains Res. Council v. U.S. Bureau of Land Mgmt., No. CV 03-69-BLG-RWA,
2005 U.S. Dist. LEXIS 25238, at *7–8 (D. Mont. Apr. 5, 2005).

[565] Ken Kreckel, The Wilderness Soc’y, Direction Drilling: The Key to Smart Growth
of Oil and Gas Development in the Rocky Mountain Region 14 (2007), available at http://wilderness.org/files/Directional-Drilling.pdf.

[566] Id. at 25.

[567] Id. at 15.

[568] 2 Bureau of Land Mgmt., U.S. Dep’t of the Interior, Final Supplemental Environmental Impact Statement for the Pinedale Anticline Oil and Gas Exploration and Development Project 7-4 (2008), available at http://www.blm.gov/pgdata/etc/medialib/blm/wy/
information/NEPA/pfodocs/anticline/fseis.Par.82863.File.dat/vol2_app.pdf.

[569] Mineral Leasing Act, 30 U.S.C. § 209 (2006); Bureau of Land Mgmt., supra note 83, at 1–2; 43 C.F.R. § 3103.4-4 (2008).

[570] Copper Valley Mach. Works, Inc., 653 F.2d 595, 600 (D.C. Cir. 1981).

[571] See Bureau of Land Mgmt., U.S. Dep’t of Interior, Record of Decision and
Jack Morrow Hills Coordinated Activity Plan/Green River Resource Management Plan Amendment 3, 52 (2006), available at http://www.blm.gov/pgdata/etc/medialib/blm/wy/field-offices/rock_springs/jmhcap/rod.Par.9393.File.dat/00rod_cap.pdf (providing that leases that had been placed in suspension for nearly 10 years while the plan was developed for this 622,000-acre area would be reinstated within three years of adoption of the July 2006 record of decision); Bureau of Land Mgmt., Pinedale Anticline ROD, supra note 50, at 4 (providing that 49,903 acres of leases in this 198,037-acre project area would be placed in suspension as part of the decision allowing increased development in this area).

[572] See generally Getty Oil Co. v. Clark, 614 F. Supp. 904, 915–18 (D. Wyo. 1985) (discussing leases subject to a unitization agreement), aff’d sub nom. Texaco Producing, Inc., 84 F.2d 776 (10th Cir. 1988).

[573] Bureau of Land Mgmt., supra note 83, at 3; see also 30 U.S.C. § 226(m) (2006) (“The Secretary may provide that oil and gas leases hereafter issued . . . shall contain a provision requiring the lessee to operate under such a reasonable cooperative or unit plan, and he may prescribe such a plan under which such lessee shall operate . . . .”). BLM has regulations related to unitization agreements that are published at 43 C.F.R. § 3180.0-2 (2008).

[574] Bureau of Land Mgmt., 1954 Lease Form, supra note 88, at 2; Bureau of Land Mgmt., 1965 Lease Form, supra note 88, at 2; Bureau of Land Mgmt., 1971 Lease Form, supra
note 88, at 2.

[575] See Bureau of Land Mgmt., supra note 83, at 3; 43 C.F.R. § 3101.1-2 (2008).

[576] 43 C.F.R. § 3162.5-1(a) (2008) (providing that environmental review documents prepared when an APD is filed can be used to determine “any appropriate terms and conditions of approval”); Onshore Oil and Gas Operations, 72 Fed. Reg. 10,308, 10,334 (Mar. 7, 2007) (providing for the imposition of conditions of approval when an APD is approved).

[577] Onshore Oil and Gas Operations, 72 Fed. Reg. at 10,334 (providing that BLM will incorporate any mitigation requirements, including BMPs, as conditions of approval for an APD); Bureau of Land Mgmt., supra note 426, at 2 (recommending the “proactive incorporation” of BMPs by the operator).

[578] 43 C.F.R. § 3101.1-3 (2008) (providing for lease stipulations).

[579] Bureau of Land Mgmt., supra note 426, at 3, 17, 40–41.

[580] See Bureau of Land Mgmt., U.S. Dep’t of the Interior, Best Management Practices, http://www.blm.gov/wo/st/en/prog/energy/oil_and_gas/best_management_practices.html (last visited Apr. 18, 2010) (providing links to BLM BMPs).

[581] Univ. of Colo. Law School, Oil & Gas Drilling Best Management Practices in Colorado, Wyoming, Montana, New Mexico, Utah, http://www.oilandgasbmps.org (last visited Apr. 18, 2010).

[582] For example, when BLM approved expanded development on the Pinedale Anticline in western Wyoming, it allowed “exceptions” to (essentially elimination of) long-standing seasonal timing limitation stipulations used to protect big game on crucial winter ranges and greater sage-grouse breeding areas. See 2 Bureau of Land Mgmt., supra note 568, at 4-19; see also Bureau of Land Mgmt., U.S. Dep’t of the Interior, 2009–2010 Wildlife Exceptions, http://www.wy.blm.gov/pfo/wildlife/2009_10_exceptions.php (last visited Apr. 18, 2010) (presenting information on exceptions to stipulations granted in the Pinedale, Wyoming and Rawlins, Wyoming BLM Field Offices and noting BLM granted the majority of requests);
Bureau of Land Mgmt., U.S. Dep’t of the Interior, 2008–2009 Wildlife Exceptions, http://www.wy.blm.gov/pfo/wildlife/2008_09_exceptions.php (last visited Apr. 18, 2010) (same).

[583] See, e.g., Hall Sawyer et al., Influence of Well Pad Activity on Winter Habitat Selection Patterns of Mule Deer, 73 J. Wildlife Mgmt. 1052, 1059 (2009) (“[O]ur results suggest that wintering mule deer are sensitive to varying levels of disturbance and the indirect habitat loss may increase by a factor of >2 when seasonal restrictions are waived.”).

[584] See supra text accompanying notes 150–52.

[585] See supra note 147 (citing provisions and instances where BLM adheres to the 200-meter 60-day rule).

[586] 43 C.F.R. § 3101.1-2 (2008).

[587] Id.

[588] See discussion supra Part IV.C.2 (presenting arguments why the 200-meter 60-day rule does not preclude other more stringent reasonable measures).

[589] See discussion supra Part IV.C.3 (reviewing IM 92-67 and BLM Manual MS-3101).

[590] See supra note 170 (presenting an example of BLM citing the requirements of IM 92-67 long after its expiration date).

[591] See Bureau of Land Mgmt., supra note 147.

[592] See supra Part IV.C.3 (discussing this language in IM 92-67 and BLM Manual MS-3101).

[593] Id. (presenting arguments why this standard of proof is unwarranted).

[594] See Administrative Procedure Act, 5 U.S.C. § 706(2)(A) (2006) (providing that a reviewing court shall set aside agency action found to be “arbitrary, capricious, an abuse of discretion or otherwise not in accordance with law”).

[595] 43 C.F.R. § 3802.0-5(l) (2009).

[596] See Bureau of Land Mgmt., supra note 147, §§ 3101.06.B.2, 3101.06.B.3, 3103.12.A, 3101.13.A (presenting statements of BLM’s views on the importance of the UUD clause in BLM oil and gas development decision making).

[597] See supra text accompanying notes 231–33 (discussing the decision in Minerals Policy Ctr., 292 F. Supp. 2d 30, 42–43 (D.D.C. 2003)).

[598] See supra text accompanying notes 234–35 (discussing interpretations of the unnecessary or undue degradation clause by the courts).

[599] Bureau of Land Mgmt., U.S. Dep’t of the Interior, Final BLM Review of 77 Oil and Gas Lease Parcels Offered in BLM-Utah’s December 2008 Lease Sale 2 (2009), available at http://www.doi.gov/documents/BLM_Utah77LeaseParcelReport.pdf.

[600] Id. at 6–14, 23–33.

[601] Id. at 30.

[602] Id.

[603] Id.

[604] Id.

[605] See supra text accompanying notes 447–48 (discussing Secretary of the Interior Salazar’s energy reform efforts).

[606] See supra text accompanying notes 447–48 (discussing Secretary of the Interior Salazar’s energy reform efforts).

[607] Mineral Leasing Act, 30 U.S.C. § 226(g) (2006).

[608] Federal Land Policy and Management Act of 1976, 43 U.S.C. § 1732(b) (2006).

[609] Endangered Species Act of 1973, 16 U.S.C. §§ 1536(a)(1)–(2), 1538(a)(1)(B) (2006).

[610] See National Historic Preservation Act, 16 U.S.C. § 470h-2(f) (2006); Bald and Golden Eagle Protection Act of 1940, 16 U.S.C. § 668 (2006); Migratory Bird Treaty Act, 16 U.S.C. § 703(a) (2006).

[611] Federal Water Pollution Control Act, 33 U.S.C. § 1323(a) (2006); Clean Air Act, 42 U.S.C. § 7418(a) (2006).

[612] See 43 C.F.R. §§ 3161.2, 3162.1(a), 3162.3-1(f), 3162.5-1(a)–(b) (2008) (making mandatory provisions for environmental protection).

[613] Id. § 2920.7(b)–(c) (providing for mandatory terms and conditions for land-use authorizations so as to protect numerous environmental attributes and qualities).

[614] See, e.g., Bureau of Land Mgmt., supra note 83, at 3; see also discussion supra Part IV.B (considering the shall versus must language in the different versions of the standard lease form).

[615] See, e.g., Onshore Oil and Gas Operations, 72 Fed. Reg. 10,308, 10,334 (Mar. 7, 2007) (providing that approved APDs “will” contain conditions of approval that reflect necessary mitigation measures and will incorporate BMPs as conditions of approval).

[616] Bureau of Land Mgmt., supra note 83, at 1.

[617] 43 C.F.R. § 3101.1-2 (2008).

[618] See Federal Land Policy and Management Act of 1976, 43 U.S.C. § 1702(c) (2006) (providing that, among other things, multiple use includes renewable and nonrenewable resources such as recreation, range, timber, minerals, watershed, wildlife and fish, and natural scenic, scientific, and historical values); see also id. § 1732(a) (providing that management of the public lands is to be done under principles of multiple use and sustained yield).

[619] See id. § 1701(a)(12) (2006) (stating that under FLPMA one policy of the United States
is to manage the public lands in recognition of the nation’s need for domestic minerals);
supra Parts V.B.6, V.D.1 (discussing energy statutes and BLM regulations).

[620] See 5 U.S.C. § 706(1) (2006) (providing that a reviewing court can compel agency action unlawfully withheld or unreasonably delayed).

[621] Blancett, No. Civ.A. 04-2152(JDB), 2006 WL 696050, at *6 (D.D.C. Mar. 20, 2006); see supra notes 341–48 and accompanying text (discussing Blancett).

[622] As stated by the Supreme Court, these requirements are “mandatory as to the object to be achieved,” even if they leave discretion as to how to achieve the object. Norton v. S. Utah Wilderness Alliance, 542 U.S. 55, 66 (2004); see also Blancett, 2006 WL 696050, at *8 (quoting this passage from the Supreme Court’s decision).

Cities as Emergent Systems: Race as a Rule in Organized
 Complexity

By Charles Lord* and Keaton Norquist**

Human beings are now an urban species. Today, the majority of the world’s human beings live in cities. At the same time, cities are perceived as chaotic and mysterious, beyond the ability of policymakers to shape and control. Such perceptions have significant implications for governance and urban policy, and for justice and equity in cities. If the patterns of inequity in cities are the result of mysterious forces, then managing or governing for justice becomes impossible.

For example, environmental justice theorists have despaired of understanding whether the distribution of environmental hazards in cities is caused by market forces, or by racial discrimination. While it is clear that certain neighborhoods host a disproportionately high percentage of environmental “disamenities,” there has been no framework for understanding whether race is the cause of such inequity. Without pinpointing the roots of environmental injustice, there is no political, legal, or moral impetus to remediate overburdened urban neighborhoods.

We present a method for understanding cities not as chaotic and mysterious, but as complex, emergent systems that are amenable to study and to management. We argue that a close study of cities through the lens of emergence theory can reveal and make sense of urban patterns. In this Article, we apply that lens to environmental justice to identify the distributional patterns in cities and to identify the rules that create those patterns. As such, we argue that cities can modify the rules and the patterns in an urban system in the cause of justice.

I. Introduction

Human beings are now an urban species. At the dawn of the twenty-first century, the majority of the world’s human beings now live in cities—and by the middle of the century, eighty percent of human beings will live in cities for the foreseeable future.[1] At the end of the twentieth century some select cities in the developed world enjoyed a renaissance, as evidenced by slight increases in population and reductions in crime.[2] However, there is a wide sense that in the twenty-first century “even the best-positioned urban areas face severe demographic and economic challenges.”[3] The received wisdom is that either misery is a given for most urban dwellers, or that misery emerges in urban life through forces beyond our control.[4] Even as the global population of cities skyrocketed, urban scholars predicted the end of cities as successful human settlements.[5] Furthermore, the city has been treated as something of a mystery, and as such, as an intractable problem.[6] As Michael Batty wrote recently in Science, “Cities are still seen as manifesting a disorder and chaos.”[7]

Accepting the notion that cities are chaotic and mysterious, beyond the ability of policymakers to shape and control, has significant implications, not just for notions of governance and urban policy, but also for issues of justice and equity. That is, if cities are chaotic and unmanageable, then misery and injustice are a given for many if not most urban residents.
If cities display patterns of inequity and such patterns are the result of mysterious forces, then managing or governing for justice becomes impossible or unlikely.

For example, in our field of environmental justice, theorists have largely despaired of understanding whether the distribution of environmental hazards in cities is caused primarily by market forces, or by racial discrimination.[8] Thus, while the evidence is overwhelming that African-American and Hispanic neighborhoods play host to a disproportionately high percentage of environmental “disamenities,”[9] there has been no framework for understanding the role of race as a causal factor in distributional inequity. Without a fuller understanding of the roots of environmental injustice, it is hard to chart a way forward for overburdened urban neighborhoods.

But what if we could understand how and why misery arrives in urban neighborhoods? Is it possible to unpack the mystery and change the outcomes? Our project here is to evaluate whether it is possible to study cities in order to demystify the patterns in modern cities. Specifically, we examine whether race or the market plays the central role in the distribution of a host of environmental disamenities such as junkyards and polluting businesses in the city of Baltimore. We show that though there may be no explicit racism in the decisional records regarding land use and disamenities,[10] we can nonetheless identify that race was the critical factor in the patterns that emerged.

In this Article, we begin by examining a method for understanding cities not as chaotic and mysterious, but as complex, emergent systems that are amenable to study and to management. As we discuss below, though the great urban theorist Jane Jacobs first articulated this method for studying cities over forty years ago, it has never been fully explored.[11] Using this method as a lens for studying the city, we propose that the patterns in urban systems, and the rules that create those patterns, can be understood and evaluated.[12]

In Part III we look at one urban pattern: the distribution of environmental disamenities. Though there is not unanimity on the point, the overwhelming weight of the evidence suggests that one characteristic pattern of the twentieth century city was the unequal distribution of such disamenities.[13] Specifically, the evidence indicates that African-American neighborhoods hosted an unequal share of these land uses.[14] Our review of the studies shows that there has been very little work on whether the distributional patterns in cities over time are a function of race, the market, or both.[15] Absent a clear indication of the role of race as compared to market forces, there is little political and moral weight behind repairing the neighborhoods that are burdened with high levels of unwanted land uses.

In Part IV, we turn to a specific city and to its pattern of environmental harms. We looked at the city of Baltimore to determine whether there is a pattern of unequal distribution and whether race or market forces seemed to be the dominant rule in the pattern of environmental distribution. Through an exhaustive review of zoning conditional-use decisions, we found that in each decade from 1940 to 2000, the Zoning Board of Appeals and the City Council approved conditional uses such that African-American neighborhoods hosted significantly higher numbers of disamenities than did white neighborhoods.[16] By reviewing the data within each decade, we illustrate that race was the critical causal factor in the siting patterns.[17] Nothing in the zoning code or the decisional records illustrated overt racism in the land-use process in Baltimore over the period from 1940 to 2000.[18] Only by understanding the city as a complex system is it possible then to untangle the mystery of these outcomes and to unpack how race became a causal factor.

In Parts V and VI we use the model of cities as complex systems[19] to unpack the systemic rules that created the pattern of unequal distribution. Understanding cities as systems helps us to frame our data in a new way and to ask an important and unique question: How might race have emerged as a rule in a facially neutral system? Using the model of cities as emergent systems creates a lens through which to study the land-use system over time; a lens that helps us illustrate how explicit racism in the early part of the twentieth century was incorporated into a facially neutral zoning system over time. Using this approach, our data confirms that race, much more than market forces, served as the rule for generating disproportionate environmental impacts on African-American neighborhoods in one city—Baltimore.[20] Illustrating that race was the rule changes the approach to rebuilding urban neighborhoods. Evidence that race as a rule created the current conditions calls on cities to undertake a systemic analysis of the land‑use legal and policy system and to consider remedies to existing conditions.

We argue, in sum, that cities are not a chaotic mystery. A close study of a city through the lens of emergence theory can reveal, and make sense of, the distributional patterns in a city. In this Article, we apply that lens to the issues of environmental justice to identify the rules that create those patterns. As such, we argue that it is possible to understand and then to modify the rules and the resultant patterns in an urban system in the cause of justice.

II. Cities as Emergent Systems

Some urban scholars have begun to argue that cities are not disordered systems and in fact that “[b]eneath the apparent chaos and diversity of physical form, there is strong order and a pattern that emerges from the myriad of decisions and processes required for a city to develop and expand physically.”[21] Many urban theorists now argue that cities are complex adaptive systems that display emergent behavior,[22] and that “cities grow from the bottom up.”[23] In other words, emergence theory suggests that cities grow from the choices and behaviors of their individual residents and institutions and not from the dictates of the central planners.

As such, some argue that cities are self-organizing systems.[24] Such systems display an organized complexity in which patterns and shapes emerge over time through the interactions of individual actors.[25]
Self-organizing systems create order not from the decisions of a central authority, but rather order and patterns emerge from the decisions and behaviors of individual actors in the system responding to the system’s rules and its feedback loops “driven by diverse interests, agencies, and events.”[26] As Stephen Johnson writes, “The city is complex . . . because it has a coherent personality, a personality that self-organizes out of millions of individual decisions, a global order built out of local interactions.”[27] Patterns of change in a self-organizing system like a city can emerge at the edges of human consciousness—as a sort of macrodevelopment, through the interaction of multiple variables at a millennial scale.[28]

And yet, though cities are difficult to comprehend, they are not chaotic, nor are they a mystery. The system is complex because there are many actors, but it is organized because the various interactions of these countless individuals and institutions follow a network of systemic rules that create a “distinct macrobehavior.”[29] Understood as a problem of “[o]rganized complexity,” it is possible to study the city as a living ecosystem, capable of adaptive change.[30] In fact, researchers can draw on the methods of science to seek out and understand the rules that govern or pattern the behavior of individual actors.[31] In short, we can uncover and describe the local, systemic rules that drive the emergent structure that is the modern city.

Emergent systems are neither inherently good, nor inherently bad—essentially, an emergent system can work toward many different kinds of goals or patterns depending on the rules inherent in the system.[32] If an emergent system and its feedback loops (the rules) create outcomes that we do not like, then it is possible to seek a better system by changing the rules that drive the individual actors.[33]

Jane Jacobs argued four decades ago that the tactics for understanding cities are much like those used for understanding the life sciences, given that both present problems of organized complexity.[34] Specifically she called for a microscopic analysis of cities that begins with the identification of a specific factor or quantity in the system and then “painstakingly learn[s] its relationships and interconnections with other factors or quantities.”[35]
Jacobs argued that “[f]or cities, processes are of the essence,” and that with the focus on process comes an additional emphasis on the catalysts of these processes.[36] The rules at play in a system of organized complexity provide a mix of positive and negative feedback that push “the system toward a particular state based on the activities of the participants.”[37] Adjusting the feedback loop generates a new type of system.[38] Put another way, understanding the systemic rules is the first step toward understanding the feedback loops and then the patterns in an emergent system like a city and thus the first step toward social change. As Stephen Johnson argues,

When we come across a system that doesn’t work well, there’s no point in denouncing the use of feedback itself. Better to figure out the specific rules of the system at hand and start thinking of ways to wire it so that the feedback routines promote the values we want promoted.[39]

Understanding the city as a problem of organized complexity provides a powerful framework for studying its challenges and opportunities. Problems of organized complexity “present ‘situations in which a half-dozen, or even several dozen, quantities are all varying simultaneously and in subtly interconnected ways.’”[40] Though “the variables are many, . . . they are not helter skelter; they are ‘interrelated into an organic whole.’”[41] This science of cities can be used to develop empirical understanding of how cities function and then to inform operational tools to address a whole range of diverse issues.[42]

III. Patterns of Emergence in Urban America

One pattern that emerged in American cities in the twentieth century was the unequal distribution of environmental inequities on the basis of race. The overwhelming weight of the evidence suggests that African-American and Hispanic neighborhoods host a disproportionately high percentage of environmental harms.[43] The root causes of this distributional pattern, however, are still subject to debate. Some theorists argue that racism is the root cause for this pattern[44] and others argue that market forces cause this pattern.[45] Ultimately, a consensus has emerged that this pattern is a result of a mysterious confluence of race and the market, and, as such, there have been few, if any, studies that attempt to pinpoint the role of racism in creating this pattern.[46] Lack of clarity on the root cause has significant implications for the future of urban neighborhoods.

Over the past five decades, dozens of researchers have documented inequitable distributions of locally unwanted land uses (LULUs) in residential areas throughout the nation.[47] This body of research overwhelmingly indicates that LULUs are distributed in patterns that strongly correlate to race.[48]

Such studies are not without their critics. One central critique involves methodology—the choice of the unit of analysis and the definition of “minority neighborhood” are both somewhat controversial.[49] Ultimately, however, there is strong evidence that race was connected to higher exposure to environmental hazards, from a variety of environmental standard metropolitan statistical areas (SMSAs).[50] While an evaluation of the evidence “does not reveal inequities at every geographic level with regard to every pollutant analyzed, it confirms many of the widespread disparities observed in previous studies, particularly with regard to race, and especially with regard to African Americans.”[51]

The general patterns of environmental justice (EJ) have been borne out in cities, and it seems that urban planning and zoning may play a role in urban environmental injustice. Craig Arnold’s study of thirty-one census tracts in seven cities found that “low-income, high-minority neighborhoods contain a greater percentage of industrial and other intensive use zones than do high-income, low-minority neighborhoods.”[52] Arnold illustrates that industrial zones are created near residential homes in low-income communities of color, “creating the very sort of incompatibility of uses that zoning is designed to prevent.”[53] Arnold suggests that cities overzone to create more industrial tax base and emphasize putting industrial properties in black neighborhoods.[54] Similarly, he suggests that when some cities create more affordable housing they tend to site it in industrial zones.[55] Arnold also argues that some black neighborhoods receive less zoning protection than white neighborhoods because they serve as buffers between white neighborhoods and industrial zones. He writes that “[b]uffer zones are perhaps one of the major reasons why low income and minority neighborhoods have so much industrial and commercial zoning: the multi‑family housing, where low-income and minority people live, is purposefully placed near the industrial and commercial uses to create a buffer that protects high-income, white, single-family neighborhoods.”[56]

There are however, those who challenge this data on environmental justice and have questioned whether they principally reflect market forces and not racism. As Luke Cole and Sheila Foster put it, “As with most statistical research, studies that chart the disproportionate distribution of waste facilities simply establish correlations, not causation.”[57] As such, some commentators question whether EJ issues are “appropriately attributed to racism or other injustice or to a more benign explanation.”[58]

Essentially, there are those who have argued that the distribution of environmental harms is evidence of distributive injustice and not racial injustice. These distributive explanations can be categorized into two chief, interrelated arguments: 1) that the disparity is caused by social status, lifestyle choices, community preferences of certain racial and ethnic groups, or a combination of those factors and 2) that the disparity is caused by the operation of the free market.[59]

The first alternative explanation for the inequitable distribution of LULUs is that one’s social status, occupation, or preference to live near LULUs exposes him or her to environmental hazards.[60] There is indeed evidence that laborers in some cities may have chosen to live close to their places of work and that as such, may have inadvertently chosen to live closer to toxic pollution.[61] In 1992, the U.S. Environmental Protection Agency’s Environmental Equity Workgroup explained the disproportionate impacts of environmental hazards on people of color by noting that a “‘person’s activity’ is the main determinant of how much environmental exposure she bears.”[62] The workgroup also determined that “racially disparate environmental hazard exposure results from the fact that ‘a large proportion of racial minorities reside in metropolitan areas’ and ‘are more likely to live near a commercial or uncontrolled waste site.’”[63]

Others suggest that the community preference alternative negates the justice implications of distributive inequities.[64] Under this analysis, distributive justice is defined “according to the degree to which the location of LULUs meets community preferences.”[65] An undesirable land use in one community may not be undesirable in another.[66] Thus, an unequal distribution could, in theory, still be equitable if the distribution satisfied the host communities equally.[67] Under this analysis, “host communities make political and market-based determinations to permit” LULUs and that subsequently residents make “decisions either to remain in the community after the [LULU] was sited, or, in many cases, to migrate to a community playing host to” a LULU.[68]

There are certainly groups of people who are “concentrated in the most dangerous sectors of our workforce, agriculture and heavy industry.”[69] Often, these groups can be characterized by low educational attainment and poor English language skills.[70] Likewise, urban areas are home to a disproportionately high percentage of African-American and Latino residents.[71] Critics of the community preference alternative point out that it “raises, rather than answers,” important questions about the causes of the inequitable distributions of LULUs.[72] For instance, “Why are African Americans disproportionately segregated in cities and thus overexposed to a variety of pollutants? Why are farm-workers disproportionately poor and Latino?”[73]

Alice Kaswan argues that “the land use siting process and the dynamics of the housing market likely skew undesirable land uses toward poor and minority communities regardless of those communities’ preferences.”[74] Indeed, there is a substantial body of evidence indicating that residents of low-income and minority communities are relegated to distressed urban areas because “their residential choices are limited by their poverty and by various forms of discrimination.” [75]

Another common explanation for the distribution of LULUs is that market forces, such as residential mobility, caused the disparity.[76] Commentators note that empirical studies have failed to establish that decision makers “intentionally discriminated against people of color or the poor” in the siting of LULUs.[77] Indeed, the methodologies of the empirical studies “have failed to compare the demographics of the neighborhoods at the time the [LULUs] were sited.”[78] Instead of analyzing the inequities of the processes by which disamenities were sited, these studies have merely commented on the outcomes of mostly undisclosed siting processes.[79] Accordingly, researchers have left open the possibility that LULUs were not disparately sited in low-income neighborhoods, but rather that the “housing and job markets” influenced low-income residents to “come to the nuisance” because the areas around the LULUs offered the most affordable housing and most easily attainable job options.[80]

Critics of the free market analysis point to “the historical and present reality of race discrimination in the housing market [that] inevitably affects individual preferences and mobility in the housing arena.”[81] Critics also note a dearth of solid empirical evidence supporting the conclusion that low‑income and minority individuals choose to “come to the nuisance.”[82] Two of Professor Been’s empirical studies contradict this hypothesis,[83] and her national study “provides little support for” the theory that market dynamics following a hazardous waste facility siting changed the social, racial, or economic characteristic of a neighborhood.[84] Other studies have had mixed results.[85]

While there are a few researchers who have found support for the free market alternative by noting declines in income and increases in the percentage of minorities after LULUs were sited, this evidence is not universally applicable and remains “inconclusive.”[86] There are relatively few studies of postsiting housing market mobility, and those that have been conducted focused solely on hazardous waste facility siting (a rare event) and on a narrow geographic area.[87]

Whether the pattern of urban emergence is a function of distributive injustice or racial injustice[88] has profound implications for the future of cities and how current patterns might be remedied.[89] These arguments “echo[] constitutional equal protection jurisprudence, under which the disparate impact of a government action is not relevant unless it can be linked to an intent to discriminate” on the basis of race.[90] The U.S. Supreme Court has consistently held that the discriminatory racial impacts of an official government decision are insufficient to sustain an equal protection claim; there must also be proof of purposeful discrimination.[91] Absent purposeful discrimination that can be proved by inexplicably disproportionate effects, obvious contextual circumstances, or barefaced statements of legislators, the Equal Protection Clause is not suited to overturn a facially neutral law merely because it has a discriminatory racial impact.[92]

By accepting that the market may play some role in the current distribution of inequities, Luke Cole and Sheila Foster clarify that the environmental justice critique cannot therefore meet the judicially actionable standard, which depends on a single bad actor and overt racism.[93] They argue that for the purposes of the environmental justice movement, notions of racism need not be confined to the judicial standard, as the struggle for environmental justice is primarily a political and economic struggle.[94] However, even in the political realm, any struggle for racial equality, and any charge of racial bias, “draws its contemporary moral strength by being clearly identified with the history of the structural oppression of African-Americans and other people of color in this society.”[95] Every step away from the understanding of the role of race as compared to the role of market forces is a step further from the moral and political will to change current distributional patterns. As Cole and Foster state,

The studies that chart the disproportionate distribution of environmental hazards have been a wake up call for those in this country who care about social justice. However, in a sense, the studies are just a beginning . . . . [F]ocusing on distributional results alone obscures the social structure and institutional context in which environmental decisions are made. Absent a deeper focus on the processes that lead to racially disparate outcomes, the studies provide only an incomplete understanding of environmental racism.[96]

The lack of empirical studies untangling the role of race from the role of the market also carries implications for the debate over remedial action.[97] Treating current distributional patterns as a mystery or as part of the chaotic interplay of race and the market has profound implications for the legal and political foundations for changing those patterns. Absent a lens through which to examine the relationship between race and the market, and a method for examining the pattern of environmental distributions, it has been difficult to approach this mystery.

Addressing cities as emergent systems provides a theoretical and investigatory framework for better understanding the underlying processes at work in cities and thus the roles of race and of the market in the distribution of land uses in cities in the twentieth century. If we are serious about managing cities as emergent systems, we must study cities as a biologist would study a living system.[98] In order to effectively manage an emergent system, we must identify the potential drivers or catalysts in the emergent system and we must make some attempt to understand how these catalysts interact.[99] Studying cities as emergent systems should provide a sharper understanding of the role of various potential catalysts. Only then can we identify which catalysts need to be modified or managed, and how to manage them, in order to achieve the emergent outcomes we want to see in our cities.

With respect to environmental justice, when we study cities as emergent systems, we must attempt to understand what role racism played in creating the current distributional outcomes, independent of postsiting market dynamics. If race seemed to play a role independent of postsiting real estate valuations, then race is a catalyst in the land-use decision making and not just at a more general societal level. Such an outcome would suggest that race is or was a critical catalyst for the current emergent city. Such a discovery would provide the “contemporary moral strength,” and thereby the political justification, to seek systemic modification to eliminate racism or its resonance.[100] If race and postsiting market decisions seem inextricably linked, then racism might be less a critical catalyst in its own right, and the emphasis on system modification might be on economic power and social mobility.

To date, there have been few, if any, time-series studies on the siting of environmental disamenities.[101] While there is a great deal of speculation about the interplay between race and the market, there have been no studies that look closely at the demographics of neighborhoods at the time that disamenities are sited.[102] For this project, we have designed and field tested a method for evaluating the distribution of disamenities at the time of the siting decisions in an effort to establish whether race or postsiting market dynamics played a larger role in current distributional patterns of environmental disamenities.

IV. Understanding the Pattern: A Case Study in Emergence

Identifying whether race served as a catalyst in one emergent urban system requires a close study of the process of locating disamenities over time. Our first goal was to determine whether it is possible to study the distributional process at all. Our second goal was to determine whether race seemed to serve as a catalyst in the system independent of the market dynamics.

In order to isolate the role of race, as compared to market forces, as a catalyst, our team chose to study the zoning process in a single city—Baltimore, Maryland.[103] Local zoning ordinances are the chief means by which permitted land uses (including disamenities) are established and regulated in cities throughout the country.[104] Zoning ordinances establish the uses that are permitted as-of-right in certain districts, as well as the uses that require the discretionary approval of an adjudicative body, such as a board of zoning appeals.[105] Prior to New York City’s adoption of the first zoning ordinance in 1916, incompatible land uses were not resolved through democratic processes; instead, incompatible land uses were settled primarily through nuisance-based litigation.[106] Comprehensive zoning thus developed as a proactive—rather than reactive—response to the problems that arise from incompatible land uses.[107] In particular, zoning has long sought to separate noxious industrial uses from residential areas by restricting the industrial uses to specific zoning districts.[108] Accordingly, an uneven, concentrated distribution of LULUs should be expected in most cities because zoning generally aims to prevent LULUs from being spread evenly throughout residential areas.[109]

As far back as Baltimore’s incorporation as a city in 1796, the Maryland state legislature, called the General Assembly, granted the Mayor and the City Council “full power and authority to enact and pass all laws and ordinances necessary to . . . prevent and remove nuisances.”[110] Beginning in 1908, the Mayor and City Council codified their general power to regulate nuisances into an ordinance that looked more like a general zoning program and regulated a large number of potential nuisances.[111] The 1908 ordinance required that a certain class of buildings be “limited as to location.”[112]
The ordinance gave the Mayor “the power to approve or disapprove the location of buildings” that could potentially be objectionable to neighbors.[113] This class of buildings was described as “used for the carrying on of business, injurious to the residents of any neighborhood in the city.”[114]

Mayor James H. Preston was one of the first voices in Baltimore to advocate for a comprehensive zoning scheme modeled after New York City.[115] In 1916, Mayor Preston implored the Baltimore City Council to enact such legislation, noting that “[i]t is manifestly injurious to a purely residential neighborhood to have a factory, store, or other . . . business placed in a section which . . . should be occupied solely by residences.”[116] Not only did Mayor Preston “champion[] zoning as a means of stopping commercial encroachment in residential neighborhoods,” but he also promoted zoning “as a method of preventing conversion of houses into tenements or apartments, and as a technique for promot[ing] cottage development to the exclusion of block rows.”[117]

In 1921, Mayor Wiling F. Broening established a Zoning Commission that was responsible for “preparing a comprehensive zoning plan for Baltimore and submitting it to the City Council in the form of an ordinance.”[118] In accordance with the National Advisory Committee on Zoning’s suggestion that “zoning regulations . . . be adapted intimately to each part of [a] municipality,”[119] Baltimore’s Zoning Commission drafted “detailed maps which divided the city into districts by the use of land and the use, height, and area of buildings.”[120] As Garret Power explains,

The Use District Map divided the city into a hierarchy of Residence, First Commercial, Second Commercial, and Industrial Zones. In Residence Districts only dwellings were permitted; in the First Commercial Districts dwellings along with retail and wholesale business and light manufacturing were allowed; in the Second Commercial Districts business and manufacturing, except certain obnoxious uses, also were permitted; and in the Industrial Districts all uses were allowed.[121]

The Zoning Commission categorized downtown’s central business district as a First Commercial District, thereby assuring future retail and office uses.[122] Smatterings of other retail areas located at busy intersections were also categorized as First Commercial Districts.[123] The areas surrounding downtown’s central business district were categorized as Second Commercial Districts in anticipation of some heavier manufacturing uses.[124] In March 1923, the Zoning Commission proposed the aforementioned zoning regime to the City Council.[125] On May 19, 1923, the Council approved the proposal and Mayor Broening signed it into law, thereby establishing Baltimore’s first zoning ordinance.[126]

The ordinance in its final form provided for appeals to the Board of Zoning Appeals and then to the Baltimore City Court.[127] In 1926, the city finally set in motion its planning process to set the land-use zones and processes for land-use decision making, and the city finally completed the process in 1931.[128]

The new zoning ordinance created a Board of Zoning Appeals (BZA).[129] This new BZA, which consisted of seven mayoral-appointed members, was given the authority to either approve or disapprove special exceptions to the zoning ordinance.[130] In deciding whether to grant a special-use permit, the zoning board in Baltimore must find the following:

(1)    the establishment, location, construction, maintenance and operation of the conditional use will not be detrimental to or endanger the public health, security, general welfare, or morals;

(2)    the use is not in any way precluded by any other law . . . ;

(3)    the authorization is not otherwise in any way contrary to the public interest; and

(4)    the authorization is in harmony with the purpose and intent of this article.[131]

In Baltimore, the special-use provision addressed the fact that “[c]ertain uses exist . . . that, because of their unique characteristics, cannot properly be classified in any particular district without consideration, in each case, of the impact of those uses on neighboring land and of the public need for the particular use at the particular location.”[132] The purpose of the conditional-use provisions are also linked by the Zoning Code to the goal of maintaining district uniformity.[133]

In making its decision, the board must consider not only the nature of the proposed site itself, but also “the nature of the surrounding area and the extent to which the proposed use might impair its present and future development”[134] and the “proximity of dwellings, churches, schools, public structures, and other places of public gathering.”[135]

In short, special uses in Baltimore are reviewed on a case-by-case basis with a special emphasis on the impact on the surrounding neighborhood and on maintaining uniformity within districts. Such indefinite and subjective terms provide wide-ranging discretion to the adjudicative boards such as the board in Baltimore.[136] The discretion also provides ample opportunity for powerful private interests to overwhelm indigent residents before the boards.[137]

The development of Baltimore’s Zoning Code is divided into two major eras: 1931 to 1971, and 1971 to the present. As the 1931 to 1971 code proclaims, “[A]ll buildings and all uses of land shall be permitted in any use district, except . . . [those that] are excluded from such use district.”[138] If an appellant desired an excluded use, she had to seek an authorizing ordinance from the Mayor and City Council.[139] Though not specifically called special uses, the early code effectively functioned as a list of conditional or special uses.[140] During this era, the BZA was relegated to very minor appeals including appeals for nonconforming uses, temporary uses, and minor district boundary exceptions.[141] Conversely, the code from 1971 to the present is more restrictive because it specifies those uses that are permitted by right along with uses that must be approved.[142] The presumption is that a use is not allowed unless specified.[143] If an appellant desires a use that requires approval, she must seek approval from either the Mayor and City Council or from the BZA.[144] The BZA’s role has been significantly expanded in the new code.[145] These special-use appeals are all clearly defined for each use district in the new code.[146]

The post-1971 list of conditional uses includes forty-seven different categories of uses, including thirty-one that must be approved by the BZA[147] and twenty-two for which a city council ordinance is required.[148] Of those forty-seven different conditional uses, our team chose to study those that have clear environmental impacts: incinerators, solid waste management or recycling (including scrap yards and poultry killing or dressing), hazardous waste handling, penal and correctional institutions, parking, automobile repair, and large scale residential projects (which might have significant traffic impacts). While the structure and development of the two codes are notably different, they do not create a fundamental disparity that makes meaningful comparison impossible.[149]

Our team set out to locate the decisional record for “special use” permits for each decade between 1930 and 2000.[150] Finding those records would allow us to overlay the decisional outcomes with the demographic patterns for each decade. This analysis isolates the decision within the context of a single decade and allows our team to identify the intersection between race and the procedural outcomes at the time of the decision
and not just at the present time. Such analysis separates out the impact of race from postsiting market dynamics. Furthermore, we hoped that understanding the decision-making process and reading case files might provide some clues as to the role of race in the decision-making itself.

Our team found records in the Legislative Reference Library (for City Council decisions) and the City Archives (for BZA decisions) of over 10,000 special-use permits between the period 1930 and 2000 and pulled for closer analysis just those from our list of environmental impact special-use permits.[151] We then created a data set of over 1000 records by address, type of disamenity, and record number. We then located all of the records in a spatial database of Baltimore (see Figure 1). Through the Baltimore Ecosystem Study, our spatial map is linked to demographic data on race and income for each decade from 1930 to the present.

 

 

 


Figure 1: Special-Use Permits in Baltimore, 1940 to 2000[152]

While there is no guarantee that zoning variance records are available for every American city,[153] our success does suggest that it is possible in some cities to isolate the placement of environmental disamenities to a specific time and demographic context, and thus to identify whether there is a correlation between race and the location of disamenities at the time of the siting and also to analyze the correlation between income and the location of disamenities. In other words, such a dataset can help answer for a particular city whether there were correlations between race and siting and whether there was evidence of a postsiting market dynamic in the current distribution of disamenities.

Our team performed a statistical analysis for the intersection between race, income, and the location of disamenities.[154] Specifically, for each decade, the team looked at neighborhoods that were close to the zoning special-use permits approved for that decade (the disamenities), surrounded by other neighborhoods close to special-use permits. These neighborhoods can be described as “low distance” zones on the map because these neighborhoods are close to the disamenities for that decade. The team then isolated those neighborhoods that are farthest from zoning variance approvals surrounded by other neighborhoods that are a long way from those disamenities. We call these neighborhoods “high distance” zones, because these neighborhoods are a long distance from the disamenities for that decade. Some neighborhoods fall into a middle category and might be called neutral neighborhoods. In our maps, the low-distance (high-impact) zones are lighter and the high-distance (low-impact) zones are darker
(see Figure 2).

 

 

 

 

 


Figure 2: Disamenity Impact Zones 1940 to 2000

 

The team then analyzed the race and income data for the low-distance (high-impact) neighborhoods and for the high-distance (low-impact) neighborhoods for each decade (see Figure 3 below showing percentage of African-American residents for 1940 to 2000).


Figure 3: Percentage of African-American
Residents by Neighborhood in 1940 to 2000

 

 

Our analysis of the data shows that for each decade between 1940 and 2000, there was a correlation between race and the distance to disamenities. Specifically, the higher the percentage of African-American residents, the closer to disamenities, and the higher the percentage of white residents the further away those neighborhoods are from disamenities (see Figure 4). Beginning in 1970, the correlation between race and proximity to disamenities begins to weaken, and in 2000 there is no correlation.


Figure 4: Correlation Between Race and Distance to Disamenities

The data on income are also striking. Income data were not available for 1940 and there were no data on median income for the decades in question. Rather, the data provided income categories and the number of people in each tract that fell into each. Our team categorized the upper half of the categories as high income and the lower half as low income and then analyzed the census tracts with respect to distance to disamenities. For 1950, the data show a strong correlation between income and distance from disamenities. Specifically, the higher the percentage of people with high income the further the neighborhood is from disamenities (see Figure 5). That correlation is much less apparent by 1960.

 

Figure 5: Correlation Between Income and


Distance to Environmental Disamenities

The data also illustrate some correlation to poverty at the time of the decisions, with some poor whites also living closer to where disamenities are allowed. As noted, the link to poverty is significantly weaker by 1960, though it never fully disappears.

This data suggests a decade-by-decade correlation between race and the siting of disamenities at the time that the city made the decisions. The Baltimore zoning system placed unwanted land uses in neighborhoods with a high percentage of African-American residents such that African-American residents were much more likely to live close to disamenities in each decade between 1940 and 1970.[155] That correlation continued in 1980 and 1990 to a lesser extent and then disappeared completely in 2000.[156] These data powerfully refute the notion that African-American residents in Baltimore
moved to the nuisance and thus that the postsiting market forces created distributional inequities. Our spatial analysis makes clear that for each decade between 1940 and 2000, the zoning process in Baltimore placed disamenities disproportionately in black neighborhoods, which suggests that race, and not postsiting market forces, served as a rule or a catalyst in the distribution of Baltimore’s unwanted land uses during the period 1940 to 2000.

Our data therefore suggests that race operated as a rule in the zoning process and thus in the emergence of land-use patterns in Baltimore. What is not clear, however, is how race became a rule in a system that employs facially neutral operational language[157] and that did not overtly import consideration of race into land-use decisionmaking. What we do know is that race seemed to be a crucial factor in land-use decision making at least until 2000. What we do not know is how or why.

Looking at cities as emergent systems provides a crucial method for evaluating these data. Given that there is no overt racism in the ordinance itself, absent the forensic work called for by Jane Jacobs[158] there is no way to understand how race operated in the system after 1940. Emergence theory proposes that scholars can evaluate a single rule such as race, explore its relationship with other rules such as market forces, and try to understand the interplay between them.[159] Identifying the role of race provides a roadmap for reform, an indication of the root cause or systemic feature that injected race into the zoning system. Identifying how race became a rule in the zoning system is the first step to refashioning the system.

V. Race and Residential Patterns: A Legacy of Segregation

In order to understand how and why race became a hidden rule in land‑use distributions in Baltimore, we must look to the history of race and land-use patterns in Baltimore in the decades before the zoning system came into force. In the years after the Civil War, African-Americans lived across the city of Baltimore, in each of its twenty wards.[160] By the early twentieth century, however, block-by-block segregation had begun to give way
“‘to sizeable hemmed-in ghettos in East Baltimore, West Baltimore, and South Baltimore.’”[161] Then, in May 1911, Mayor J. Barry Mahool signed into law a segregation ordinance that was meant to provide “so far as practicable, for the use of separate blocks for white and colored people for residences, churches and schools.”[162] Organized and authored by progressives who agreed that “blacks should be quarantined in isolated slums in order to reduce the incidents of civil disturbance, to prevent the spread of communicable disease into the nearby white neighborhoods, and to protect property values among the white majority,”[163] the ordinances went through several iterations due to procedural flaws and in response to state court objections.[164] Finally, as Garret Power writes, “[T]he legal significance of housing segregation laws . . . was [short lived]” because the Supreme Court struck down a similar ordinance in Kentucky, which wiped out the Baltimore ordinance.[165] Power goes on to argue, however, that the “historical significance of Baltimore’s segregation ordinance remains” because the ordinance set the stage for “a covert conspiracy to enforce housing segregation, the vestiges of which persist in Baltimore yet today.”[166]

In response to the Supreme Court’s decision, Mayor Mahool’s replacement, Mayor James H. Preston, set out to replace the de jure segregation with de facto segregation, “enforced by a conspiracy in restraint of rental or sale” of housing to blacks on blocks that had been setout as white neighborhoods.[167] The organized plan was to use white property associations, the real estate board, the health department, and the city building inspector to ensure that African-Americans left the neighborhoods where they were in the minority and did not enter those neighborhoods that were already white.[168] Over time, the conspiracy grew and formalized, with white neighborhood associations adopting racial segregation as one of their top priorities and neighborhood protection associations passing restrictive covenants that prohibited the rental or sale of properties to blacks.[169] Up to as late as 1930, associations coordinated their efforts across neighborhoods and worked together to share information and enforce restrictive covenants.[170]

The zoning system also served to perpetuate and enforce segregation in the city. The majority of preexisting residential areas were categorized as residential districts, which not only shielded them from commercial and industrial intrusion, but also greatly restricted the construction of affordable housing, such as apartments and block row houses.[171] The zoning commission originally intended to follow Mayor Preston’s containment strategy to require that newly constructed dwellings in certain affluent—and mostly white—areas be constructed only as single-family cottages while permitting apartments and row houses in less affluent neighborhoods.[172] Maryland’s highest court, however, invalidated the zoning commission’s attempt to require that each parcel in a section of Baltimore’s Forest Park neighborhood be “‘constructed as a separate and unattached building’” because the city’s police power could not be used for the purpose of segregating social classes.[173] Though the zoning commission had to accept the court’s prohibition against one-class residence districts, the commission employed height districts to “segregate[] cottages from block rows and apartments.”[174] Nearly all of the newly annexed areas on the outer edges of the city were classified as extremely low-height districts; they were also required to have at least one side yard.[175] In practice, these measures combined to “assure[] that only detached or semi-detached dwellings would be constructed there.”[176] Height district maps pointedly restricted tall apartment buildings to various inner-city areas.[177] This segregation was deliberately “made to appear [as] a side effect of civil engineering, not the desired product of social engineering.”[178]

During this same period, other public and private actors, including banks and the federal government, began to use race as a rule in their decision making in a way that isolated black residents in certain neighborhoods of Baltimore.[179] In 1937, the Federal Home Owners’ Loan Corporation (HOLC) conducted a survey of residential neighborhoods in order to assign a security grade to each neighborhood based on the perceived risk of default.[180] HOLC was a New Deal federal agency assigned to refinance homes in danger of foreclosure.[181] “Among the criteria used to assess risk were occupation of residents, average annual income, predominant nationality, percentage of ‘negro families’ to total number of families, percentage of families on relief, and ‘threat of infiltration of foreign born, negro or lower grade population.’”[182] In addition, surveyors were instructed to estimate the rate of change occurring in a given population.[183] The neighborhoods deemed most unstable and highest risk were given a grade of D, were labeled hazardous, and outlined in red on the original maps—hence the term redlining.[184] Neighborhoods deemed in transition were labeled declining and were given a grade of C.[185]

The impact of redlining cannot be overstated—across the country banks and savings and loans refused to provide financing for homes and small businesses in the neighborhoods that received D grades.[186] In addition to the lack of financing for homes and businesses, Jane Jacobs noted that these neighborhoods were stigmatized and that as a result the middle class fled—a crippling blow to neighborhood stability.[187]

There can be no doubt that the HOLC reports had a profound impact on the stability of affected neighborhoods, or that the criteria were explicitly racist. Several of the redlined neighborhoods in Baltimore (see Figure 6) received those grades because of the “[n]egro concentration,”[188] or the “heavy concentration of foreigners.”[189] Also significant is that most of the Baltimore neighborhoods that received D grades had high percentages of black residents (twenty percent or more) and that the reports also noted the obsolescence of the housing stock,[190] the encroachment of industrial uses,[191] or the noise from business.[192] Of the seven neighborhoods that received
D grades, six had twenty percent or more African-American residents.[193]
The neighborhoods that received C grades or better were ten percent or less African-American.[194] Several of those neighborhoods were scored as
C (endangered) due to the “[i]nfiltration” of African-Americans and the others because of poverty or the obsolescence of the housing stock.[195]

 


Figure 6: Home Owners’ Loan Corporation
Zones (HOLC) for Baltimore City
[196]

Over the course of the early twentieth century, then, de facto and then de jure segregation forced blacks in Baltimore to live in certain neighborhoods. The HOLC surveys confirm that those neighborhoods suffered from dilapidated housing stock and also that those neighborhoods already hosted significant commercial and industrial activity.[197] Five of the six neighborhoods with twenty percent or more African-American residents that received a D had a significant amount of industrial “encroachment” or were in areas already zoned industrial or commercial.[198]

De facto segregation, and the public and private conspiracy that included banks and the original zoning system, coupled with the white flight to the suburbs, led to a dramatic change in the landscape of Baltimore.[199] During the period 1918–1930, the white population of the city declined by half and the African-American population increased from fifteen percent of population to thirty percent of the population.[200] By 1930, Baltimore had become “a black center surrounded by a white ring.”[201] Furthermore, a 1933 study found that the blighted parts of the city were predominantly populated by blacks, with black residents living in districts that had not yet been connected to the sewer, received few city services, and had no
garbage pickup.[202]

The historical analysis confirms that the prezoning residential patterns were set by racism and not the free market.[203] The evidence is clear that racism was an explicit rule that created an emergent pattern for Baltimore that put black residents in certain, specific neighborhoods defined by poor housing stock and a proximity to commercial and industrial uses. As such, race and racism was clearly and explicitly a rule in creating emergent patterns of settlement and distribution of LULUs up to 1940.

Taken together, this historical analysis and our data on zoning special-use permits and race suggests that somehow the facially neutral zoning process perpetuated the explicit racism of the prezoning period.[204]
The question, then, is how and why race continue to serve as a rule and a feedback loop in the emergent land-use patterns from 1940 to 2000. Unpacking the mechanism is the final step in understanding how race has served as a rule and whether the current land-use distribution system needs to be recalibrated with different feedback loops.

VI. Race as a Rule in Baltimore’s Zoning: 1940 to 2000

Professor Dara Roithmayr has developed a model to describe the processes by which racial inequalities become entrenched, or “locked-in,” societal institutions.[205] The first and perhaps most fundamental precept of the locked-in model is that present racial inequalities “can be traced to earlier events that have charted a particular course of history for different racial groups.”[206] For example, Professor Roithmayer points to research indicating that housing discrimination “earlier in the century produced a surplus in property value for white . . . . [homeowners who] then were able to pass down the value of that surplus . . . to their children, in the form of financing for a college education and down payments for homes.”[207]
Such asset surpluses have had a strong effect in cementing disparities between the haves and the have-nots.[208]

The second precept of the locked-in model is that affluent communities’ early anticompetitive advantages become self-reinforcing.[209] “As with economic markets, in race relations, early anti-competitive conduct can produce increasing returns for the early mover. In the context of residential segregation, for example, early monopoly advantage[s] . . . reproduce[d] [themselves] through a variety of mechanisms . . . .”[210] Finally, “racial disparities . . . persist indefinitely” unless there is some type of “intervening event.”[211] As racial inequality becomes locked in place, it may also become prohibitively expensive to eliminate.[212] Analogizing to the rules of the marketplace, Professor Roithmayr reasons that “[a]ny policy looking to remedy locked-in racial inequality would incur the structural and political switching costs of restructuring or modifying routine institutional practices. If switching costs increase as time passes, these costs may help to further cement in racial inequality as part of the U.S. social landscape.”[213]

Despite facially neutral standards, our variance data suggests that zoning perpetuated, “locked-in,” and exaggerated the effects of the earlier overt racism in land-use planning. In this way, race was incorporated as a rule in city planning through a facially neutral standard. In fact, the zoning variance analysis indicates that racism can be locked-in not just to societal dynamics but indeed that racism may be locked in as a rule in legal processes in such a way that some “intervening event” may be required to cleanse the legal system and reestablish its validity.

The first stage of the incorporation of race into the formal zoning process came during the creation of the zoning districts themselves. Not all preexisting residential areas were categorized as residential districts by the zoning commission.[214] In fact, the zoning commission’s “plan placed virtually all of south and southeast Baltimore in a large and inclusive industrial zone.”[215] Excepting certain affluent “enclaves” that were allowed to remain residential, the newly designated industrial zone swallowed numerous residential neighborhoods, including Fells Point, Locust Point, the Otterbein, Pig Town, and Fairfield.[216] Altogether, “approximately 11,000 dwellings—many of [which were] occupied by [African-Americans] and immigrants—were placed within the industrial zone.”[217] The industrial zoning designation would be a windfall for industrial factories.[218] Previously, large-scale industrial factories were reluctant to locate near residential areas because they would be vulnerable to private nuisance lawsuits brought by nearby homeowners who might seek to enjoin noxious uses or exact money damages.[219] Industrial zoning designations, however, would help remove this impediment because courts deferred to legislative declarations that particular areas should be used for industrial purposes.[220] In addition, the zoning designations would allow industrial companies to perform even the most noxious and intense industrial uses directly adjacent to dwellings; after all, seemingly any activity was permissible in industrial zones as a matter of legal right.[221] Because the zoning commission’s designation would ultimately be a legislative action by the city council, industrial factories would not be required to obtain discretionary permits from adjudicative boards.[222] By  classifying certain residential communities as industrial zones, the zoning commission ensured that these marginalized communities would be forced to accept noxious uses without the possibility of an adjudicative hearing—at which neighbors might convince decision makers not to permit certain activities so close to their homes—or private nuisance lawsuits.[223]

Soon after zoning went into effect, Baltimore’s white working class residents learned a valuable lesson from the affluent communities on the periphery of the city.[224] They began to realize that just as the middle class had been excluded from upper class communities through a variety of exclusionary zoning mechanisms, so too could they work to keep out others.[225] White working class residents feared both encroaching commercial uses—such as gasoline filling stations, groceries, and drug stores—and “rooming and apartment houses” that would deteriorate residential areas as part of a “negro invasion.”[226] Accordingly, community groups began springing up all over Baltimore.[227] By 1925, seventeen neighborhood improvement associations held meetings to discuss various perceived threats to their neighborhoods.[228] These neighborhood improvement associations would later prove to be extremely powerful institutions capable of rallying their members to pressure the BZA and city council to steer proposed LULUs away from their neighborhoods and into marginalized neighborhoods.[229]

Because the city council reserved itself the power to “amend, supplement, or change” the zoning districts at its own discretion,[230] the  council was quickly inundated with requests for zoning changes of individual parcels.[231] In some cases, community groups made requests to down-zone nearby undeveloped parcels from commercial to residential, thereby protecting their neighborhoods from anticipated commercial encroachment.[232] In other cases, shrewd business leaders made requests to up-zone residential areas into commercial districts, thereby seizing upon perceived market opportunities.[233]

The de facto segregation scheme had isolated black residents in certain neighborhoods that had preexisting industrial and commercial character and, as such, that scheme locked black residents into neighborhoods with lower zoning protection and a higher number of preexisting disamenities.[234] This pattern for Baltimore confirms studies in other cities, which indicated that exclusionary zoning has had the effect of perpetuating residential segregation.[235] Permitting some LULUs by right not only mutes the affected community’s voice, but also prompts its residents to leave because noxious industrial or commercial uses undermine “the quality of the neighborhood . . . [t]o the extent that . . . residents were displaced.”[236] Furthermore, as Jane Jacobs noted, conventional zoning is inflexible insofar as it is “based on the assumption that segregating uses (of building and land) from one another is desirable.”[237] Jacobs was concerned that conventional zoning creates rigidity in cities, designating separate uses to separate areas, and disallowing the possibility of adaptation and diversity.[238]

This rigidity inherent in conventional zoning exacerbated inequality. Our analysis suggests that the system benefits some neighborhoods over others, with the actual segregation of uses benefiting those neighborhoods that were initially free of noise and pollution since additional noise and pollution funneled to those neighborhoods that had historically experienced these burdens. Zoning in Baltimore did in fact segregate unwanted land uses—but it did not isolate them from all residents, just from white residents. The earlier racial segregation intersected with a zoning system that segregated unwanted land uses to further concentrate the unwanted land uses in the black neighborhoods during the period 1940 to 2000.

The seemingly neutral zoning decisional process then perpetuates and extends the earlier racism in two ways: First through the treatment of prior nonconforming uses, and second through the exaggeration of the earlier redlining through the “appropriateness” standard. The facially neutral decisional approach to prior nonconforming uses seemingly injected the earlier racism into the later zoning system because under the special-use process in Baltimore, a prior nonconforming use was allowed to continue if it existed before the code.[239] Because black residents were concentrated in areas with high percentages of commercial and industrial uses before the zoning code came into effect,[240] it seems likely that they were subjected to more such conditional or “special” uses in the period 1940 to 1970 as unwanted land uses came forward and were granted a special-use permit as prior nonconforming uses.[241] Our analysis of the case files for the some 1000 decisions we looked at suggests that a significant number of the conditional uses were granted on these grounds in the early years of the zoning system. Of the files we looked at, 14% of the special-use permits in the 1940s and 17% in the 1950s were granted on these grounds.[242] In the 1960s and 1970s, the number of special uses granted for prior nonconforming use dropped to 7% and then 5% respectively.[243]

The zoning decisional standards also extend the role of race and racism over the decades by exaggerating and perpetuating the effects of redlining. As noted, conditional uses are reviewed “because of their unique characteristics,” and with “consideration, in each case, of the impact of those uses on neighboring land and of the public need for the particular use at the particular location.”[244] In deciding whether to grant a conditional use, the zoning board in Baltimore must find that “the establishment, location, construction, maintenance, and operation of the conditional use will not be detrimental to or endanger the public health, security, general welfare, or morals;”[245] “the authorization is not otherwise in any way contrary to the public interest; and . . . [the authorization] is in harmony with the purpose and intent of this article.”[246] In short, the key decisional analysis focused on whether the proposed special use would be detrimental to the public health and general welfare of neighboring land. Such a decisional standard most likely explains in part the disproportionate impact of special-use permits on black residents and the continuation of race as a rule in land-use patterns. Because of redlining, black neighborhoods lacked investment and thus land and housing stock deteriorated.[247] At the time of the HOLC reports, black residents had been isolated in neighborhoods through de facto segregation that suffered from “heavy obsolescence”[248] in the housing stock. Continued lack of investment led to abandoned land or housing stock declines.[249] Conceivably, this provided a rationale for unwanted land uses because the neighboring land is either vacant or the buildings are already rundown.

A 1964 case illustrates the prophylactic force of the higher-quality housing stock and more pristine neighborhood conditions in white neighborhoods. In defeating a request for a variance for parking and storing cars at 3002 Gibbons Avenue, the opponent argued to the BZA: “We would hate this city to point to Hamilton as a place where they have a junk yard in a highly, or what was regarded as one of the best residential areas in this entire city.”[250]

The insidious impacts of the “appropriateness” analysis and its likely intersection with disinvestment were clearly visible when two landowners applied for the same use in the same year. In 1988, for example, a business owner applied for a conditional-use permit to establish an auto repair shop with a paint shop at 6540 Holabird Avenue.[251] Although the case was decided on procedural grounds the planning commission recommended to the BZA that the application be denied because the neighborhood was “very well maintained.”[252] That same year, another developer applied for a conditional-use permit for an auto repair and storage business at a vacant lot at 701 Dundale Avenue.[253] Because the lot was vacant, the BZA allowed the conditional use, arguing that it was a “creative use” for the site.[254]

Our database shows that applicants sought a significant number of special-use permits over the 1950s and 1960s for parking lots and junkyards.[255] In fact, 18% of the special-use permits we looked at in the 1930s, 27% in the 1940s, and 24% in the 1950s represented these two uses.[256] Such uses, according to Jane Jacobs, are particularly detrimental to neighborhood cohesion because they provide nothing to a neighborhood’s “general convenience, attraction or concentration of people” but make an “exorbitant” demand on the land.[257] These types of uses create dead zones along huge sections of a block or blocks but create no life on the street, no street traffic, and no chances for neighbors to connect.[258] Thus, these uses accelerate the cycle of neighborhood decay.[259] These uses also perhaps create a self-perpetuating legacy—with each such use providing a rationale under the “appropriateness standard” for more such uses on neighboring land.

It is important to note that while the two facially neutral decisional standards clearly extended the role of race as a rule in land-use distribution, there is some indication in our data that the correlation between race and special-use permits runs deeper than the ongoing effects of the de facto segregation and redlining of the 1920s and 1930s. A close analysis suggests in fact that the preexisting industrial uses and the original redlining were not, on their own, the cause for later distributional inequities. A look at the later concentration of disamenities in redlined neighborhoods indicates that the LULUs were not simply concentrated in redlined neighborhoods as a function of the preexisting uses and dilapidated housing stock. In fact, tracing the relationship between redlining and the decade-by-decade distribution of disamenities indicates that the original condition of the neighborhoods is less important than race in the subsequent siting of disamenities. In other words, neighborhoods that were redlined in the 1930s due to some combination of a high percentage of commercial enterprises, industrial encroachment, and racial makeup only received high numbers of disamenities in subsequent decades if the percentage of black residents stayed high or increased.

Our overlay of the redlining maps and the variance data shows a correlation between redlining and the siting of disamenities in 1940. However, as the racial characteristics of these neighborhoods change, the proximity to disamenities changes as well. As the neighborhoods become more black, they either stay high-impact or become high-impact. Redlined neighborhoods from the 1930s that show steady or increasing Caucasian populations see a drop in the impact from zoning in subsequent decades.[260]
A study of the concentration of disamenities in each decade in these neighborhoods over time suggests a strong correlation to race in the siting, and less to the original HOLC score.

Specifically, all of the areas with high disamenity impact in 1940 were listed either as “hazardous” (D) or “declining” (C) in the earlier HOLC reports. Of the hazardous (D) neighborhoods, all are high-impact disamenity zones during the 1940s.[261] Remember that six out of seven of these have African-American populations over 20% and that all neighborhoods with a significant percentage of African-American residents are listed as Hazardous.[262] The one D neighborhood that is all white (D-2) remains white through the 1970s.[263] This is the one D neighborhood that goes from being a high-impact neighborhood in 1940 to being a low-impact zone for disamenities in subsequent decades.[264] Neighborhood D-4 is in west Baltimore and is a black neighborhood in 1940 and stays that way over the rest of the twentieth century.[265] It is a high-impact zone for disamenities in 1940 and it stays high impact in subsequent decades as the black neighborhoods drift west (see Figure 3). Neighborhood D-5 is in south Baltimore and at the time of the redlining in the 1930s it is 50% black and it stays that way through 1970.[266] In 1940, neighborhood D-5 is a high-impact zone for disamenities,[267] but as Baltimore became home to more black residents, with black residents moving west, this neighborhood sees fewer disamenities in subsequent decades and ends up neutral in 1970. Neighborhood D-6 is 35% black in 1940 and in subsequent decades that percentage drifts upward.[268] In 1940, this neighborhood is a high-impact zone[269] and it is a high-impact zone in all subsequent decades. Neighborhood D-8 is 30% black at the time of the HOLC maps and that percentage drifts up from there, but not dramatically.[270] The neighborhood is zoned entirely commercial and the HOLC report suggests that it will convert to a business district[271]—as in other cities, there are residents and families trapped in this zone. This neighborhood was a high-impact zone in 1940 and in all subsequent decades.[272] Neighborhood D-9 was 40% black at the time of the HOLC analysis and the HOLC report values the neighborhood for conversion to business, while also remarking on the “heavy obsolescence” of the residential property and noise from business.[273] Through major demographic shifts over the next three decades, the neighborhood becomes largely black by 1970 and is a high-impact zone for disamenities in each decade.

There is a similar higher correlation to race and disamenities for the neighborhoods listed as “declining” (C) in the HOLC reports. Of the five declining neighborhoods that were high-impact zones in 1940 (1, 3, 4, 5, 7), three of the five list African-American “encroachment” and obsolescence as the rationale for that determination.[274] Of the C neighborhoods that are not high-impact zones for disamenities in 1940, all are white neighborhoods.[275] One very poor white neighborhood (C-11) that was listed as declining in the HOLC reports stayed white throughout the study period and is never a high‑impact zone for disamenities through 1970.[276] C-8 was a white neighborhood in 1940 and in that decade was a low impact zone for disamenities.[277] The zone was almost entirely black by 1970 as the black neighborhoods moved west, and by 1960 it was no longer a low-impact zone.

There are exceptions to these trends among the declining neighborhoods—exceptions that do suggest some poverty effect as well. Neighborhood C-13 was a mostly white neighborhood that was a low-impact zone in 1940 and in subsequent decades became a high-impact zone even as the population remained largely white.[278] The HOLC inspector for this neighborhood noted a mixture of “foreign” residents in the neighborhood at the time of the initial survey, noted an infiltration of “foreigners” into the neighborhood, and indicated a “heavy” load of relief families in the neighborhood.[279] Another dynamic that could well have been at play was an undercurrent of discrimination against recent, non-English speaking immigrants who had also been isolated in certain neighborhoods.

Of the neighborhoods in 1940 that were low impact for disamenities, only two (C-8 and C-14) were listed as declining and these were both white neighborhoods.[280] Inspectors noted for both areas that there was no infiltration of “foreign” residents.[281] All the rest of the low-impact zones were ranked as highly stable by the HOLC study and all were white neighborhoods.[282] For example, the neighborhood marked A-1 in central Baltimore was described as “very nicely residential neighborhood” with no detrimental influences.[283]

Some testimony from the 1950s suggests that applicants sought out black neighborhoods for unwanted land uses. For example, the attorney for local residents in the Board of Zoning and Appeals case number 943-50, an application for an auto repair shop at 2201 Windsor Street, told the Board,
“I don’t think [it’s] erroneous to say that now that the neighborhood is mostly colored, the owner seems to be more persistent to have a repair shop there.”[284] The attorney went on to argue that appellant

lives in Reisterstown and . . . 75% of his patronage is white. This neighborhood is colored. Let him go where his trade is. It will be more economical and it will have a tendency to make the protestants feel the city wants to help them in their ambition to have fine decent homes . . . . He will not have the same interest in keeping up the appearances of this community as these home owners, as he doesn’t live there.[285]

The opposition in this case had an attorney and managed to get the variance disapproved, but the testimony suggests that perhaps applicants targeted black neighborhoods for unwanted land uses.

In another 1950 case, the board approved an application to expand a preexisting junkyard in a commercial-use district inhabited by African-American residents.[286] The attorney for the residents said that the majority of the neighbors

are working people and haven’t time to come up and make their protest in person . . . . This is, of course, a non conforming use unfortunately for these people. The area is exclusively colored, I believe, and the Board realizes that they are in there, that is their home, it is not their fault but they of necessity have to live in that particular neighborhood. The junk yard is a serious threat both in the way it is being operated now and its location, to the health of the residents of the neighborhood and to the safety. In fact, the junk is being put all over the place[;] it is filthy and unfortunately existed before the zoning came in.[287]

Similarly, in what might be one of the first environmental justice cases in Baltimore, the National Association for the Advancement of Colored People (NAACP) stepped in to help neighbors fight an application for a variance for an operation to incinerate brake shoes at 2301 Boone Street.[288] Neighbors successfully defeated an application for an expansion to the brake shoe facility, referencing impacts on their health.[289] The NAACP submitted a letter protesting the expansion and when the applicant failed to appear the Board found for the neighbors.[290]

It is worth noting that in those cases where the opposition had a lawyer, the rate of disapproval was quite high. This suggests that access to legal services and the ability to raise money to fight special-use or conditional-use permits is central, and that lack of economic and legal resources in black neighborhoods could have contributed to the disproportionate number of special-use permits in black neighborhoods in each decade. Among the cases we looked at, of the fifty-eight cases in which an attorney appeared, the board disallowed the conditional use in forty-two of them.[291] This
seventy-two percent disapproval rate suggests that access to an attorney was very influential in the outcome of these cases, as it is much higher than the background percentage of disapprovals (or withdrawals), which is forty‑one percent for the case files that we reviewed.[292]

Taken together, these narratives and case statistics point to a number of critical dynamics in the zoning process that might also have served to inject race and racism into the land-use distribution system. Specifically, the testimony from these cases suggests that white applicants perhaps targeted special-use permits to black neighborhoods, and that those neighborhoods that could not afford a lawyer were disadvantaged in battling special-use permits. In addition, the testimony suggests that white neighborhoods with high quality housing stock could be insulated from special-use permits.

Legislative changes to the zoning maps that expanded the industrial or commercial zones in African-American neighborhoods could also have created disproportionate impacts in African-American neighborhoods. Indeed, Juliana Mantaay uncovered this dynamic in New York City,[293] and Craig Arnold’s multicity study found this to be a common issue in cities across the country.[294] We can assume that the same dynamic played out in Baltimore, though this would make an interesting additional level of analysis.

It is worth speculating as well on the reasons that the correlation between race and the siting of disamenities fell off after 1970 and disappeared by 2000. To begin with, the City of Baltimore was a largely black city by the year 2000, with very few white enclaves (see Figure 3).
In addition, to the extent part of the disparity in prior decades was likely attributable to the doctrine of “prior nonconforming uses,” as those uses worked through the system there would have been fewer opportunities to grant special-use permits each decade in poor and black neighborhoods on these grounds. Finally, it is possible that stricter limits on conditional uses in the post-1971 version of the code may have reduced the amount of disamenities in residential neighborhoods. For example, scrap yards were listed as “non-conforming” uses in the 1931–1971 code for residential districts.[295] For the period between 1971 to the present, the code allowed conditional approval of scrap yards in heavy industrial (M-3), with the presumption that they are not allowed in other districts.[296]

Another topic for further investigation is the expansion of black political power after 1970 and especially after 1980, and the impact on the distribution of disamenities. In 1970, African-American attorney Milton B. Allen won a city-wide election for State’s Attorney, benefiting from a vote split among four white candidates in the Democratic primary.[297] Allen lost a racially-tinged primary in 1974 to William Swisher.[298] In 1982, Kurt Schmoke beat Swisher in the primary and Schmoke went on five years later to be Baltimore’s first elected black mayor.[299] The record of city council membership is equally intriguing—it suggests patterns that are relevant to this analysis and require further study. Though no nonwhite members were elected to the city council before 1890, six African-American Republicans were elected to the Baltimore City Council between 1890 and 1930.[300] Between 1930 and 1955, no African-American candidates were elected to the council.[301] From 1955 to the present, there was at least one African-American member of the council, but not until redistricting in 1991 did African-American councilors take even eight of the eighteen seats on the council.[302] These data suggest a significant shift in black political power over the period from 1970 to 1990. Additional research is called for to better understand the correlation between that shift, the changing demographics in the city, and the distribution of disamenities between 1970 and 2000 and then into the twenty-first century.

Taken together, the data make clear that race and racism was a rule that created a significant feedback loop in the emergent city of Baltimore long after the de jure segregation ordinances had been struck down by the Supreme Court. Through first a de facto segregation scheme, and then through the injection of the earlier racism into the zoning system, race and racism created the land-use patterns of modern day Baltimore. At the same time, our data suggest that by the turn of the twenty-first century, unwanted land uses are no longer disproportionately sited in black neighborhoods. Several critical questions remain, however, about the connections between race and emergent land-use patterns in Baltimore and other cities. To begin with, policy makers must ask whether there are lasting impacts from the race-based feedback loops that seemingly operated in Baltimore for almost a century. In addition, we must ask whether other feedback loops have replaced race as a rule in land-use decision making.

VII. Conclusion

Our analysis of zoning special-use permits and their correlation to race during the period 1940 to 2000 has shown that race was a rule in the distribution of unwanted land uses during the twentieth century.
Our special-use data confirms that the zoning system in Baltimore distributed unwanted land uses on the basis of race and not a postsiting market dynamic. Explicit racism in the form of segregation ordinances and then segregation campaigns was imported into the zoning system through the operation of facially-neutral standards linked to “appropriateness” through redlining and through the doctrine of prior nonconforming uses, and perhaps through the decisions of private actors and the resources available to actors in the zoning system.

This study confirms methodologically that it is possible to evaluate the feedback loops that operated to define the emergent patterns in cities during the twentieth century. Specifically, our method of using emergence theory to study the rules in the complex system (the City of Baltimore) confirms that research teams can uncover data on siting decisions in the urban context, and that they can use those data to evaluate the correlation between the siting of disamenties and race and income data. Not every city will have zoning decisions in its archives, but for those that do our research method confirms that it is possible to evaluate the role of race and racism in
the emergent land-use patterns of the twentieth century American city.
Jane Jacobs, it would appear, was correct in positing that it is possible to study the city in the way that scientists approach a research project; and Stephen Johnson, it would appear, is correct in positing that emergent systems such as cities can be understood and that rules and feedback loops can be evaluated against cultural norms and expectations.[303]

Given that race was a rule in the emergent patterns in Baltimore during the twentieth century, cultural, legal, and political conceptions of justice require a significant reexamination of the land-use system and its outcomes even in the twenty-first century. Baltimore’s residents live in neighborhoods that are themselves a legacy of almost a century of decision making profoundly, if for many decades inadvertently, infected by racism.[304]
As racial inequality is now locked in place, it may be prohibitively expensive to eliminate.[305] Untangling the legacy may be difficult and costly.

The success of our methods suggests that major cities across the country should evaluate their land-use decision making over the twentieth century to investigate the extent to which race and racism played a role in the current distribution of land uses and should develop land-use distribution and investment plans that remediate historical patterns of racism and isolation. The next step for any city is to study its current land‑use system to identify the feedback loops at play, and to consider a remedial analysis to correct any continuing resonance of race. Such remedial analysis might consider remedial investments to counteract the effects of racism on isolated neighborhoods and might seek to ensure that the land-use distribution patterns of the twenty-first century reflect the desired political and constitutional norms.

 


* Environmental Studies Program, Boston College, and Visiting Scholar, Boston College Law School. This Article was supported by the National Science Foundation (NSF) under Grant BCS-0624159, “A Longitudinal Analysis of the Social Dynamics of Environmental Equity in Baltimore.” Many thanks to Jarlath O’Neil-Dunne and the University of Vermont for the remarkable spatial analysis and data set, and to David Seekel and Austin Troy of the
University of Vermont for the statistical analysis. Many thanks to my partners on the NSF grant, Morgan Grove, Geoff Buckley, and Chris Boone. We owe a huge debt of gratitude as well to the Maryland State Archives under the direction of Dr. Edward Papenfuse. We also want to thank Mike Klarman, Jim Ryan, Michael Willrich, and Zyg Plater for reading earlier versions of this Article.

** Boston College Law School Class of 2009.

[1] J. Morgan Grove, Cities: Managing Densely Settled Social-Ecological Systems, in Principles of Ecosystem Stewardship: Resilience-Based Natural Resource Management in a Changing World 281, 281 (F. Stuart Chapin, III et al. eds., 2009); see Larry E. Band et al., Heterogeneity in Urban Ecosystems: Patterns and Process, in Ecosystem Function in Heterogeneous Landscapes 257, 257 (Gary M. Lovett et al. eds., 2005).

[2] Joel Kotkin, The City: A Global History 148 (2005).

[3] Id. at 151.

[4] Michael Batty, The Size, Scale, and Shape of Cities, 319 Sci. 769, 769 (2008) (noting that throughout the 19th century commentators decried cities as “wretched” and arguing that “[t]hese sentiments have dominated our approach to cities to this day”); see also Kotkin, supra note 2, at xvi–xvii (arguing that the “sprawling” cities in the developing world lack functioning economies and stable political orders, while the cities in the West and developed portions of the East and South Asia “lack a shared sense of sacred space, civic identity, or moral order”).

[5] See Douglas W. Rae, City: Urbanism and Its End 2 (2003) (“[T]he city in which his business is designed to operate is gone . . . .”).

[6] Batty, supra note 4, at 770 (arguing the rules that have been used in the past to design the ideal city “rarely provide the quality of life for their inhabitants that such order anticipates”).

[7] Id. at 769.

[8] See infra Part III.

[9] This is our phrase for environmental hazards and unwanted land uses that have environmental effects.

[10] See infra Part VI.

[11] See generally Batty, supra note 4, at 769 (describing the “inadequate” understanding of the evolution of cities and the slow development of the field).

[12] See id.; infra Part II.

[13] See infra Part IV.

[14] See infra notes 155–56 and accompanying text.

[15] See infra text accompanying notes 43–59.

[16] See infra notes 155–56 and accompanying text.

[17] See infra fig.4.

[18] See infra notes 155–57 and accompanying text.

[19] See infra Part II for a full description of this model and its sources.

[20] See infra Part VI.

[21] Batty, supra note 4, at 769.

[22] The first to make the case was the great Jane Jacobs in the Death and Life of Great American Cities. See Jane Jacobs, The Death and Life of Great American Cities 428–34 (1961); see also Steven Johnson, Emergence: The Connected Lives of Ants, Brains, Cities, and Software 18 (2001).

[23] Batty, supra note 4, at 769.

[24] Grove, supra note 1, at 286.

[25] Johnson, supra note 22, at 46–48.

[26] Grove, supra note 1, at 292; see also Batty, supra note 4, at 769.

[27] Johnson, supra note 22, at 39.

[28] Id. at 98–99.

[29] Id. at 48.

[30] Id. at 52.

[31] Jacobs, supra note 22, at 439–40.

[32] Johnson, supra note 22, at 137.

[33] Id.

[34] Jacobs, supra note 22, at 443.

[35] Id. at 440.

[36] Id. at 440–41.

[37] Johnson, supra note 22, at 159.

[38] Id. at 162

[39] Id.

[40] Jacobs, supra note 22, at 433 (emphasis omitted) (quoting Warren Weaver, A Quarter Century in the Natural Sciences, in The Rockefeller Found., Annual Report 1, 9 (1958)).

[41] Id. (quoting Warren Weaver, A Quarter Century in the Natural Sciences, in The Rockefeller Found., Annual Report 1, 14 (1958)).

[42] Batty, supra note 4, at 770–71. This issue is as diverse as climate change and
“ethnic segregation and deprivation due to failures in job and housing markets.” Id. at 771.

[43] See, e.g., Jane Kay, Minorities Bear Brunt of Pollution, S.F. Examiner, Apr. 7, 1991, at A1, available at 1991 WLNR 44180.

[44] See, e.g., Kathy Seward Northern, Battery and Beyond: A Tort Law Response to Environmental Racism, 21 Wm. & Mary Envtl. L. & Pol’y Rev. 485, 550 (1997) (asserting that the “root causes” of environmental racism include “racially discriminatory exclusive or expulsive zoning practices”).

[45] Lynn E. Blais, Environmental Racism Reconsidered, 75 N.C. L. Rev. 75, 81 (1996).

[46] See Luke W. Cole & Sheila R. Foster, From the Ground Up: Environmental Racism and the Rise of the Environmental Justice Movement 58 (2001).

[47] Id. at 54–55, 167–83. For instance, researchers have concluded that low-income and minority communities suffer from inequitable distributions of LULUs in many states and cities. See, e.g., African Am. Environmentalist Ass’n et al., Our Unfair Share: A Survey of Pollution Sources in Our Nation’s Capital 6 (1994) (finding that even though Washington D.C.’s overall population is 65% African-American, the area with the least pollution is 88% white); Robert D. Bullard, Invisible Houston: The Black Experience in Boom and Bust 70–75 (1987) (finding that the distribution of municipal landfills and incinerators in Houston had disproportionate racial impact independent of class); Lauretta M. Burke, Nat’l Ctr. for Geographic Info. & Analysis, Environmental Equity in Los Angeles 46 (1993), available at http://downloads2.esri.com/campus/uploads/library/pdfs/5869.pdf (finding that poorer areas with higher populations of people of color have the greatest number of Toxic Release Inventory facilities and finding also that race is slightly better at predicting the presence of Toxic Release Inventory facilities than income); Susan Caris et al., The Social Burdens of Environmental Pollution: A Comparative Metropolitan Data Source 563, 569 (Brian J.L. Berry ed., 1977) (concluding that solid waste sites in Chicago are distributed inequitably by income and race); Council on Envtl. Quality, Environmental Quality: The Second Annual Report of the Council on Environmental Quality 192 (1971) (finding that air pollution in Chicago is inequitably distributed by income); Fla. Envtl. Equity & Justice Comm’n, Final Report 5 (1996) (finding that low-income communities and communities of color suffer disproportionate environmental impacts in Florida); Michael R. Greenberg & Richard F. Anderson, Hazardous Waste Sites: The Credibility Gap 158–59 (1984) (finding that communities with the greatest number of toxic waste sites are home to more low-income and African-American residents than other communities); Eric Mann, L.A.’s Lethal Air: New Strategies for Policy, Organizing, and Action 31 (1991) (documenting that 71% of African-Americans and 50% of Latinos live in areas with the worst air pollution, compared to 34% of whites); U.S. Gen. Accounting Office, Siting of Hazardous Waste Landfills and Their Correlation with Racial and Economic Status of Surrounding Communities 1 (1983), available at http://archive.gao.gov/d48t13/ 121648.pdf (noting that three of the four commercial hazardous waste sites in eight southern states were located in communities with a majority of people of color); Jeffrey M. Zupan,
The Distribution of Air Quality in the New York Region 2–3 (1973) (concluding that air pollution is distributed inequitably by income in New York); Peter Asch & Joseph J. Seneca, Some Evidence on the Distribution of Air Quality, 54 Land Econ. 278, 293 (1978) (concluding that people of color have higher pollution levels than whites in Chicago and Nashville); J. Tom Boer et al., Is There Environmental Racism? The Demographics of Hazardous Waste in Los Angeles County, 78 Soc. Sci. Q. 793, 807–08 (1997) (concluding that working class communities of color are most affected by hazardous waste treatment and disposal facilities in Los Angeles); Robert D. Bullard & Beverly Hendrix Wright, The Politics of Pollution: Implications for the Black Community, 47 Phylon 71, 76 (1986) (finding that even though African-American neighborhoods only account for one-fourth of Houston’s population, they host six of the city’s eight incinerators and all five city-owned landfills); Luke W. Cole, Empowerment as the Key to Environmental Protection: The Need for Environmental Poverty Law, 19 Ecology L.Q. 619, 624–28 (1992) (describing how all three of California’s Class I toxic waste landfills are in low-income communities that have populations consisting of a vast majority of people of color—between 63% and 95%); A. Myrick Freeman III, Distribution of Environmental Quality, in Environmental Quality Analysis: Theory and Method in the Social Sciences 243, 268–69 (Allen V. Kneese & Blaire T. Bower eds., 1972) (finding air pollution to be inequitably distributed by race, independent of income, in Kansas City); Kusum Ketkar, Hazardous Waste Sites and Property Values in the State of New Jersey, 24 Applied Econ. 647, 656–57 & tbl.6 (1992) (finding that in New Jersey, municipalities with the highest percentage of people of color had the largest number of toxic waste sites); William J. Kruvant, People, Energy, and Pollution, in The American Energy Consumer 125, 140 (Dorothy K. Newman & Dawn Day eds., 1975) (noting the inequitable distribution of air pollutants as it correlates to race and income); Robert A. Kutcher, Letter of Transmittal, in La. Advisory Comm. to the U.S. Comm’n on Civil Rights, The Battle for Environmental Justice in Louisiana….. Government, Industry, and the People, at ii, iii (1993), available at http://www.law.umaryland.edu/Marshall/usccr/documents/cr12en8z.pdf (concluding that there has been disproportionate siting of hazardous waste facilities in low‑income areas with high percentages of African-Americans in the industrial corridor from Baton Rouge to New Orleans); Paul Mohai & Bunyan Bryant, Environmental Racism: Reviewing the Evidence, in Race and the Incidence of Environmental Hazards: A Time for Discourse 163, 171–72 (Bunyan Bryant & Paul Mohai eds., 1992) [hereinafter Race and Environmental Hazards] (finding that Michigan’s commercial hazardous waste facilities are located disproportionately where people of color live); Marjorie W. Moore, Environmental Health and Community Action, N.Y. St. B.A. Envtl. L. Sec. J., Feb–May 1991, at 12, 12 (noting that five of Manhattan’s seven municipal bus depots are located in predominantly African-American and Latino neighborhoods); Harvey L. White, Hazardous Waste Incineration and Minority Communities, in Race and Environmental Hazards, supra, at 126, 131–32 (finding that communities of color had a much higher rate of hazardous waste facilities than white communities in the Baton Rouge area); Kay, supra note 43 (finding that the population for the California zip code bearing the greatest total pounds of toxic release was 59% African-American and 38% Latino); Christopher Boerner & Thomas Lambert, Environmental Justice in the City of St. Louis: The Economics of Siting Industrial and Waste Facilities 24 (Ctr. for the Study of Am. Bus., Working Paper No. 156, 1995) (concluding that for neighborhoods in St. Louis that host active waste facilities and inactive superfund sites, the percentages of poor people and people of color increased at a faster rate than nonhost neighborhoods).

[48] See, e.g., Cole & Foster, supra note 46, at 167–83; see also Benjamin A. Goldman, Not Just Prosperity: Achieving Sustainability with Environmental Justice 3–19 (1993) (cataloguing 64 studies that found disproportionate impact of environmental hazards according to race, income, or both). Luke Cole died in a car accident at the age of 48 during the drafting of this Article. He was a mentor to Charlie Lord and a great leader in the field of environmental justice. He will be sorely missed.

[49] See, e.g., Alice Kaswan, Distributive Justice and the Environment, 81 N.C. L. Rev. 1031, 1069 & n.155, 1070–73 (2003).

[50] Id. at 1069–70; see also James P. Lester et al., Environmental Injustice in the United States: Myths and Realities 13 (2001). James P. Lester and his colleagues evaluated a series of studies at three geographic scales—state, county and city. See id. at 7, 57. Their study found that across all scales environmental injustice is present in approximately 86% of the analyses that focus on percent of black population, 50% in the analyses of Hispanic population, and 35%–50% of the analyses of class. Id. at 151–54.

[51] Kaswan, supra note 49, at 1073.

[52] Craig Anthony (Tony) Arnold, Planning Milagros: Environmental Justice and Land Use Regulation, 76 Denv. U. L. Rev. 1, 9, 77 (1998).

[53] Id. at 81.

[54] Id. at 132–33.

[55] See, e.g., id. at 119.

[56] Id.; see also Kaswan, note 49, at 1116.

[57] Cole & Foster, supra note 46, at 58.

[58] Id.

[59] Id.

[60] Id.

[61] See Christopher G. Boone, An Assessment and Explanation of Environmental Inequity in Baltimore, 23 Urb. Geography 581, 589 (2002). This study of Baltimore in fact indicates that with respect to hazardous waste sites, white residents suffer disproportionate impacts as compared to black residents at the current time. Id. at 585. The authors suggest this is a function of the worker preference for living close to factories. See id. at 589.

[62] Cole & Foster, supra note 46, at 58–59 (quoting 1 Envtl. Equity Workgroup, U.S. Envtl. Prot. Agency, Environmental Equity: Reducing Risk for All Communities, Workgroup Report to the Administrator 13 (1992)).

[63] Id. at 59 (quoting 1 Envtl. Equity Workgroup, U.S. Envtl. Prot. Agency, Environmental Equity: Reducing Risk for All Communities, Workgroup Report to the Administrator 13–14 (1992)).

[64] Blais, supra note 45, at 81–82.

[65] Kaswan, supra note 49, at 1038.

[66] Id.

[67] Id.

[68] Blais, supra note 45, at 81. Professor Blais largely discounts the possibility that public, and for that matter private, actors are deliberately siting LULUs in low-income neighborhoods, minority neighborhoods, or both. Id. (“[N]one of the empirical studies [are] able to demonstrate any . . . invidious discrimination [by political and private officials who make siting decisions.]”).

[69] Cole & Foster, supra note 46, at 59.

[70] See id.

[71] Id.

[72] Id.

[73] Id.

[74] Kaswan, supra note 49, at 1038.

[75] Cole & Foster, supra note 46, at 59.

[76] Kaswan, supra note 49, at 1036–37.

[77] Vicki Been, What’s Fairness Got to Do with It? Environmental Justice and the Siting of Locally Undesirable Land Uses, 78 Cornell L. Rev. 1001, 1014, 1060–63 (1993).

[78] Cole & Foster, supra note 46, at 60–61.

[79] Been, supra note 77, at 1016.

[80] Id. at 1016–18; Cole & Foster, supra note 46, at 60; see also Kaswan, supra note 49,
at 1048–49 (“If at the time of an initial decision, an area had been unpopulated, or was white and affluent, then the siting decision itself was probably not politically unjust. But broader social injustices, like poverty and housing discrimination, could have led to a subsequent concentration of poor and minority residents, since they would be less able to flee undesired LULUs, or might be attracted to lower-valued housing in areas with LULUs.” (citations omitted)).

[81] Cole & Foster, supra note 46, at 61.

[82] Id. at 60.

[83] Id. at 207 n.17. In her article, Coming to the Nuisance or Going to the Barrios?, Professor Been found no evidence that communities became poorer or increased in minority population after the approval and construction of waste facilities. Vicki Been & Francis Gupta, Coming to the Nuisance or Going to the Barrios? A Longitudinal Analysis of Environmental Justice Claims, 24 Ecology L.Q. 1, 9, 27–29, 34 (1997). Similarly, in Locally Undesirable Land Uses in Minority Neighborhoods, Professor Been found that the southeastern waste sites studied by the United States General Accounting Office in 1983 were all sited in disproportionately African-American communities, and that these communities did not become poorer or increase in African-American population after the waste facilities were sited. Vicki Been, Locally Undesirable Land Uses in Minority Neighborhoods: Disproportionate Siting or Market Dynamics?, 103 Yale L.J. 1383, 1398–1400 (1994).

[84] Been & Gupta, supra note 83, at 9, 27–29, 34; see also Cole & Foster, supra note 46,
at 207 n.17.

[85] Cole & Foster, supra note 46, at 207 n.17. Some have shown an increase in poor and minority residents after a siting and others have seen a decrease. Id. All of these other studies are of a small geographic area. Id.

[86] See Cole & Foster, supra note 46, at 60, 207 n.17 (citing Been, supra note 83, at 1400–06) (finding that Houston waste sites studied in 1983 by Professor Bullard were originally sited in African-American communities, but the communities did not have disproportionately low incomes, and also finding, however, that the percentage of African-Americans rose and incomes fell after the solid waste facilities were sited); Douglas L. Anderton et al., Hazardous Waste Facilities: “Environmental Equality” Issues in Metropolitan Areas, 18 Evaluation Rev. 123 (1994) (finding no statistically significant racial disparity in the location of commercial hazardous waste facilities and finding evidence of economic decline in communities with commercial hazardous waste facilities, but no evidence of white flight); Thomas Lambert & Christopher Boerner, Environmental Inequity: Economic Causes, Economic Solutions, 14 Yale J. on Reg. 195, 202 (1997); see also Kaswan, supra note 49, at 1038–39.

[87] Kaswan, supra note 49, at 1037–38.

[88] Id. at 1035 (“Some commentators have suggested that ‘distributive injustice’—that is, evidence of disproportionate land use patterns—is not of regulatory concern unless it can be shown that the unequal [land-use] patterns were caused by identifiably discriminatory or biased processes.”).

[89] Id. at 1035–36.

[90] Id. at 1054.

[91] See, e.g., Washington v. Davis, 426 U.S. 229, 239 (1976); see also McCleskey v. Kemp, 481 U.S. 279, 279–80 (1987) (upholding death penalty conviction despite evidence of statistically disproportionate capital punishment convictions due to lack of discriminatory purpose in plaintiff’s immediate case). Though McClesky has been superceded by statute, see Cornelious v. Campbell, No. 1:06-cv-01500-TAG HC, 2009 WL 56006, at *5 (E.D. Cal. Jan. 7, 2009) (citing Antiterrorism and Effective Death Penalty Act of 1996, Pub. L. No. 104-132, 106 Stat. 1214), the original decision provides some important context here. The Court articulated three ways through which purposeful discrimination can be proved in its landmark decision Village of Arlington Heights v. Metropolitan Housing Development Corp. (Arlington Heights), 429 U.S. 252, 266–68 (1977). First, a law’s impact may be so plainly discriminatory that no nondiscriminatory justification would be possible. Id. at 266. In Yick Wo v. Hopkins, 118 U.S. 356 (1886), the plaintiff challenged a city ordinance requiring laundries to be located in brick or stone buildings unless a waiver was obtained, id. at 356–57. Upon producing evidence that over 200 waiver applications were denied to persons of Chinese ancestry whereas all waiver applications filed by non-Chinese persons were approved, the plaintiff convinced the Court of the city’s discriminatory intent. See id. at 359, 374. Similarly, in Gomillion v. Lightfoot, 364 U.S. 339 (1960), the plaintiff challenged a government’s redrawing of municipal boundaries that excluded virtually all of the city’s black voters while excluding not a single white voter, id.
at 340–41. The Court was once again persuaded that legislators had acted for no other purpose than racial discrimination. Id. at 347–48. However, cases such as Yick Wo and Gomillion are quite rare. Arlington Heights, 429 U.S. at 266 (“Absent a [statistical] pattern as stark as that in Gomillion or Yick Wo, impact alone is not determinative, and the Court must look to other evidence.” (citation omitted)). Second, the context and sequence of events leading up to the challenged policy can indicate purposeful discrimination. Id. at 267. For example, in Guinn v. United States, 238 U.S. 347 (1915), the Court invalidated a state law requiring a literacy test for voting that effectively exempted white citizens through a grandfather clause for descendants of those who were eligible to vote in 1866, id. at 347–48, 357. Though the law was facially neutral, its historical context made the legislature’s discriminatory purpose perfectly clear. See id.
at 357–58. The Court in Griffin v. County School Board of Prince Edward County, 377 U.S. 218 (1964), invalidated a policy that closed public schools in response to desegregation orders, effectively forcing residents to pay for children to attend segregated private schools, id. at 219. The facially neutral law’s discriminatory purpose was once again ascertained by looking at its historical context. See id. at 220–25. Third, the legislative or administrative history of a law can reveal explicit discriminatory purposes. Arlington Heights, 429 U.S. at 268. By examining statements made by lawmakers in the transcripts of its meetings or reports, courts are able to ascertain publicly stated motivations. See id. However, the real-world usefulness of this method is most limited because it would take an unusually shameless legislator to openly state a racially discriminatory motive. See Shira J. Schlaff, Comment, Using An Eruv to Untangle the Boundaries of the Supreme Court’s Religion-Clause Jurisprudence, 5 U. Pa. J. Const. L. 831, 857 (2003) (“Despite blatantly discriminatory comments at council meetings, the District Court held [in Tenafly Eruv Ass’n, Inc. v. Borough of Tenafly, 155 F. Supp. 2d 142, 152–58 (D.N.J. 2001),] that the law at issue was neutral because council-members did not explicitly state discriminatory reasons . . . .”).

[92] Arlington Heights, 429 U.S. at 253, 266–68. Even if a plaintiff is able to prove the existence of purposeful discrimination through one of the three methods mentioned in Arlington Heights, the law is not immediately invalidated. Id. at 270 n.21. Rather, the burden would then shift to the government to prove that it would have taken the same action even if it did not have discriminatory motivation. Id. Thus, the government is given an opportunity to articulate a nondiscriminatory rationale for its law. Id. This burden shifting poses yet another obstacle for potential plaintiffs in a judicial system that appears extremely hesitant to overturn facially neutral laws for violating the Equal Protection Clause. See id.

[93] See Cole & Foster, supra note 46, at 63–65.

[94] Id. at 65.

[95] See Gerald Torres, Introduction: Understanding Environmental Racism, 63 U. Colo. L. Rev. 839, 839 (1992).

[96] Cole & Foster, supra note 46, at 79.

[97] Id. at 60; see also Lawrence J. Straw, Jr., Environmental Justice: Racial Gerrymandering for Environmental Siting Decisions, 14 Va. Envtl. L.J. 665, 671, 679–80 (1995) (critiquing environmental justice advocates who argue that disparate impacts should be addressed even if unaccompanied by discriminatory intent).

[98] See Jacobs, supra note 22, at 439–40.

[99] See Johnson, supra note 22, at 108–09.

[100] Torres, supra note 95, at 839 (“The term racism draws its contemporary moral strength by being clearly identified with the history of the structural oppression of African-Americans and other people of color in this society.”).

[101] Kaswan, supra note 49, at 1090.

[102] Id.; see also Cole & Foster, supra note 46, at 79.

[103] Dr. Papenfuse and the staff at the Maryland State Archives are now managing the original zoning records from the City of Baltimore, and our success in accessing these records and analyzing them is based on their fine work. As noted, we did not know if an analysis such as ours was even possible. However, thanks to their good work and the work of the Baltimore city staff in preserving these records, such research is indeed possible.

[104] Kaswan, supra note 49, at 1106. There are a variety of zoning techniques that local governments employ to regulate and either encourage or discourage certain land uses. These techniques include historic districts, overlay districts, demolition delay ordinances, conservation districts, tree preservation ordinances, religious land-use exemptions, building moratoria, development impact fees, and inclusionary housing ordinances. See generally Julian Conrad Juergensmeyer & Thomas E. Roberts, Land Use Planning and Development Regulation Law 362–68 (2d ed. 2007) (discussing inclusionary housing); id. at 495–98 (discussing moratoria); id. at 508–40 (discussing impact fees); id. at 699–708 (discussing the Religious Land Use and Institutionalized Persons Act of 2000, 42 U.S.C. §§ 1988, 2000bb-2 to -3, 2000cc to -5 (2006)); id. at 810–814 (discussing historic preservation at the local level);
id.
at 862–64 (discussing conservation easements). Houston, Texas is the only major American city without a comprehensive zoning ordinance. Chistopher Berry, Land Use Regulation and Residential Segregation: Does Zoning Matter?, 3 Am. L. & Econ. Rev. 251, 251 (2001).

[105] See, e.g., N.Y. City Dep’t of City Planning, NYC Zoning History, http://www.nyc.gov/html/
dcp/html/zone/zonehis.shtml#how (last visited Apr. 18, 2010) (providing general information on the administration of New York City zoning regulations).

[106] See id.

[107] See id. (“The concept of enacting a set of laws to govern land use was revolutionary but the time had come for the city to regulate its surging physical growth.”).

[108] Kaswan, supra note 49, at 1106.

[109] Id.

[110] Act of Dec. 31, 1796, ch. 68, 1796 Md. Laws 1056, 1058, available at http://www.msa.md.gov/ megafile/msa/speccol/sc4800/sc4872/003181/html/m3181-1056.html (establishing the City of Baltimore); Mayor & City Council of Balt. v. Marriott, 9 Md. 160, 65 Am. Dec. 326 (1856).

[111] Balt., Md., Ordinance 155 (June 19, 1908); see also Smith v. Standard Oil Co. of N.J.,
130 A. 181, 181 (Md. 1929).

[112] Smith, 130 A. at 181 (citing Balt., Md., Ordinance 858 (Apr. 15, 1923), which amended Balt., Md., Ordinance 155 § 47, para. 12 (June 19, 1908)).

[113] Garrett Power, The Unwisdom of Allowing City Growth to Work Out Its Own Destiny,
47 Md. L. Rev. 626, 628 (1988) (citing Balt., Md., Ordinance 155 (June 19, 1908)). In 1923, the City Council expanded the Mayor’s authority to include garages, laundries, stores, and warehouses. Balt., Md., Ordinance 858 (Apr. 15, 1923); see also Power, supra, at 633.

[114] See Smith, 130 A. at 181.

[115] Power, supra note 113, at 627.

[116] Id. (quoting Some Legislation, Akin to New York’s “Zone Law,” Is Needed to Protect Valuable Property from Invasions that Are Ruinous to Property Values, Balt. Mun. J.,
Oct. 27, 1916, at 4).

[117] Id. at 644.

[118] Id. at 630 (citing Balt., Md., Ordinance 615 (July 15, 1921)).

[119] Id. at 631 (citing U.S. Dep’t of Commerce, The Preparation of Zoning Ordinances:
A Guide for Municipal Officials and Others in the Arrangement of Provisions in Zoning Regulations 5 (1931)).

[120] See id.

[121] Id.

[122] Id.

[123] Id.

[124] Id.

[125] Id.

[126] Id. at 633; see Balt., Md., Ordinance 922 (May 19, 1923); Balt., Md., Ordinance 154 (Apr. 16, 1924) (amending Ordinance 922 to change the locations of existing use districts). The original code was struck down twice for technical reasons. Goldman v. Crowther, 128 A. 50, 60
(Md. 1925) (invalidating Ordinance 922 on the basis that it deprived property owners of their rights under the state constitution without adequate justification); Tighe v. Osborne, 131 A. 801, 808 (Md. 1926) (invalidating Balt., Md., Ordinance 334 (Feb. 9, 1925)). After the invalidation of Ordinance 334, Baltimore finally got it right with the passage of Ordinance 522, Balt., Md., Ordinance 522 (Dec. 14, 1925), in December of 1925. Tighe v. Osborne, 133 A. 465, 470 (Md. 1926). This ordinance cured the problems of the previous law by excluding language allowing the zoning commissioner to make decisions with regard to the “general welfare,” and instead, properly limited the commissioner’s power to “prohibiting structures or uses of them which would menace the public security, health or morals.” See id. at 467 (upholding Ordinance 522 because by properly limiting the zoning commissioner to the “proper objects of police power,” it did not constitute an unlawful delegation of power by the City of Baltimore).
Note that the Goldman case came just before the Supreme Court upheld local zoning in Euclid v. Ambler Realty Co., 272 U.S. 305, 365 (1926), and that Tighe was post-Euclid. Thanks to Garret Power for pointing this out.

[127] See Balt., Md., Ordinance 922 (May 19, 1923).

[128] See Balt., Md., Ordinance 1247 (Mar. 30, 1931) (enacting Baltimore’s initial comprehensive zoning ordinance).

[129] Power, supra note 113, at 633.

[130] Id. The board also had the authority to grant exceptions where the zoning code created a hardship for a land owner. Id.

[131] Balt., Md., Zoning Code § 14-204 (2009).

[132] Id. § 14-101(b).

[133] Id. § 14-101(a).

[134] Id. § 14-205(a)(1), (3).

[135] Id. § 14-205(a)(4).

[136] See generally 3 Arden H. Rathkopf et al., Rathkopf’s The Law of Zoning and Planning § 61:1–:50, at 61-2 to 61-138 (4th ed. 2009) (describing the history and contours of the site‑specific discretionary review of proposed uses in the context of applicable zoning regulations).

[137] See id.

[138] Balt., Md., Ordinance 1247 § 3 (Mar. 30, 1931).

[139] Id. § 4.

[140] See id. § 1.

[141] Id.

[142] Balt., Md., Zoning Code §§ 3-101 to -103 (2009).

[143] Id. § 3-106.

[144] Id. § 14-102.

[145] See id. §§ 2-109 to -111 (establishing the BZA’s jurisdiction and authority).

[146] See, e.g., id. § 4-203.

[147] These uses include 1) alcoholic beverages and taverns (live entertainment and dancing), 2) after-hours establishments, 3) arsenals, 4) atomic reactors, 5) dry cleaners and laundries with more than four employees, 6) explosives, 7) firearm sales, 8) garages for repairs and service,
9) manufacturing and storage of combustible or toxic gases, 10) gasoline service stations,
11) sewerage pumping stations, 12) water filtration plants, 13) heliports, 14) junk or scrap storage and yards, 15) mining, gravel, sand, or other raw materials, 16) auto accessory stores, including repair and installation, 17) automotive testing grounds, 18) car washes, 19) petroleum distribution, pumping, or valve stations, 20) poultry and rabbit killing establishments, 21) public utilities such as antenna towers, 22) electric distribution centers, 23) overhead electric transmission lines, 24) repeater, transformer, or pumping stations, 25) radioactive waste handling, 26) recycling collection stations, 27) recyclable materials recovery facilities with outdoor storage, 28) rock crushing, 29) stables for horses, 30) tire and tire products, but with no tires or tire products within 200 feet of a residential district, and 31) waste disposal for landfill and land reclamation. See id. §§ 4.0-1 to 7.3-2; id. at 427–77 tbl. (containing a table of zoning uses).

[148] These include 1) adult entertainment and bookstores, 2) community correction centers, 3) drive-in dry cleaning facilities, 4) hazardous material handling and storage, 5) commercial or municipal incinerators, 6) peep show establishments, 7) penal and correctional institutions,
8) racetracks, 9) drive-in theaters, 10) commercial or municipal incinerators, 11) indoor recyclable materials recovery facilities, 12) drive-in drug stores, 13) multifamily homes containing 100 or more units, 14) drive-in restaurants, 15) homes for nonbedridden alcoholics or homeless people, 16) garages or open areas for four or more automobiles, 17) parole or probation field offices, 18) pawnshops, 19) photographic printing and developing, 20) planned unit developments,
21) bus passenger shelters, and 22) service and housing centers. See id. §§ 4.0-1 to 7.3-2;
id.
at 427–77 tbl. (containing a table of zoning uses).

[149] In fact, it is instructive to compare the conditional approval process for the seven targeted disamenity types across the two codes. First, just as ammonia manufacture is listed as a conditional use in the earlier code, so too is “Gases, combustible or toxic—manufacturing and storage” in the later code. Compare Balt., Md., Ordinance 1247 (Mar. 30, 1931), with Balt., Md., Ordinance 1051 § 7.2-1(c)(6) (Apr. 20, 1971). Second, though collection centers were only added to the zoning code in the 1990s, solid waste and recyclable materials facilities like scrap yards were listed as conditional uses in the 1931–1971 code for industrial districts. See Balt., Md., Zoning Code § 7-407 (2009); Balt., Md., Ordinance 1247 § 1 (Mar. 30, 1931). For the period 1971 to present, the code allowed conditional approval of scrap yards in Heavy Industrial (M-3) areas, with the presumption that they are not allowed in other districts. Balt., Md., Zoning Code § 7.407 (2009); Balt., Md., Ordinance 1051 §§ 7.3, 7.3-1(c)(5) (Apr. 20, 1971). Since recycling collection centers are a modern phenomenon, see, e.g., Liz Bowie, Baltimore Launches Quiet Revolution in Recycling but City Needs to Spread the News, Balt. Sun, Nov. 29, 1991, http://articles.baltimoresun.com/1991-11-29/news/1991333020_1_recycling-program-curbside-collection-baltimore (last visited Apr. 18, 2010), there is no basis for comparison across the two codes. Third, penal and correctional institutions have consistently required approval or were restricted in Residential Districts. Compare Balt., Md., Ordinance 1247 § 1, para. 8 (Mar. 30, 1931), with Balt., Md., Zoning Code § 4-204 (2009). During the period 1971 to the present, the code provided for the conditional approval of community correction centers in Industrial Districts. Id. §§ 7-308, -408(4). Fourth, garages, auto repair and open area parking have consistently required approval in Residential Districts, and since 1971 the zoning code has required conditional approval for the parking of four or more vehicles in every district except Community Commercial (B-3) and Central Commercial (B-5) Districts. Id. § 7.2-1. The 1971 code provides the same treatment for parking garages, except that parking garages are permitted by right in industrial districts. Balt., Md., Ordinance 1247 (Mar. 30, 1931). Finally, the 1931 code did not have a process for Planned Unit Developments. See generally Balt., Md., Ordinance 1247 § 1 (Mar. 30, 1931) (regulating “residential use districts” but not distinguishing between different scales of residential use development). Thus, housing developments of greater than 100 units did not have to undergo any particular process until the 1971 code came into effect; now these developments require a conditional use permit. Balt., Md., Ordinance 1051 § 4.2-1(d)(3)
(Apr. 20, 1971).

[150] Henceforth, we will use the term “special use” to describe these permits.

[151] The city council decisions are indexed by year in a summary of city council decisions. These decisional records and the indexes are in the Legislative Reference Library in Baltimore, Maryland. The BZA decisions for 1931–1971 are now housed at the Maryland State Archives and are organized chronologically by date. The BZA decisions for 1971 to the present are at the BZA in Baltimore and are organized chronologically by case file number. Dr. Papenfuse and the staff at the Maryland State Archives are now managing the original zoning records from the City of Baltimore, and our success in accessing these records and analyzing them is based on their fine work.

[152] Prepared based on extensive interviews with Dr. Jarlath O’Neil-Dunne, Geospatial Analyst, University of Vermont Spatial Analysis Laboratory.

[153] Telephone Interview with Dr. Edward Papenfuse, Md. State Archivist, in Balt., Md. (Jan. 5, 2009).

[154] To take into account spatial spillovers, David Seekel and Austin Troy of the University of Vermont calculated equity as the average distance between a census block group centroid and approved disamenities from the previous decade. See generally E. Talen & L. Anselin, Assessing Spatial Equity: An Evaluation of Measures of Accessibility to Public Playgrounds, 30 Env’t & Planning 595, 599 (1998) (showing another application of this distance calculation). They used Moran’s I and local indicators of spatial association (LISA) to assess spatial autocorrelation.
See generally Luc Anselin, Local Indicators of Spatial Association–LISA, 27 Geographical Analysis 93, 93, 115 (1995) (utilizing the LISA statistics to show both data “hot spots” and outliers). They used first order contiguity spatial weights matrices. Statistical significance was assessed with a permutation test (n = 999). They used Moran scatterplots to visually inspect for local instabilities in Moran’s I. See generally Luc Anselin, The Moran Scatterplot as an ESDA Tool to Assess Local Instability in Spatial Association, in Spatial Analytical Perspectives on GIS 111, 115–17 (Manfred Fischer et al. eds., 1996) (describing the Moran scatterplot technique and its application to local instability). To examine the relationship between the equity measure, race, and income they used the product moment correlation coefficient. The equity statistic was loge transformed prior to analysis. Proportions were arcsine square root transformed to stabilize variances. Because the average distance to disamenity is by design nonrandom over space, they adjusted the effective degrees of freedom according to Peter Clifford et al., Assessing the Significance of the Correlation Between Two Spatial Processes, 45 Biometrics 123, 124 (1989). Statistical analyses were completed in GeoDa, “a free software program intended to serve as a user-friendly and graphical introduction to spatial analysis for non-geographic information systems . . . specialists.” See generally Luc Anselin et al., GeoDa: An Introduction to Spatial Data Analysis, 38 Geographical Analysis 5, 5 (2006) (explaining the GeoDa program and its uses and the Spatial Analysis in Macro-ecology, or SAM, software); Thiago Fernando L.V.B. Rangel et al., Towards an Integrated Computational Tool for Spatial Analysis in Macroecology and Biogeography, 15 Global Ecology & Biogeography 321 (2006) (describing SAM, the Spatial Analysis in Macro-ecology software program, and its uses).

[155] See supra fig.3.

[156] See supra fig.3.

[157] “[T]he establishment, location, construction, maintenance and operation of the conditional use will not be detrimental to the public health, security, general welfare, or morals.” Balt., Md., Zoning Code §14-204(1) (2009).

[158] See supra notes 34–36 and accompanying text.

[159] See, e.g., Johnson, supra note 22, at 18–19.

[160] Garret Power, Apartheid Baltimore Style: The Residential Segregation Ordinances of 1910–1913, 42 Md. L. Rev. 289, 289–90 (1983).

[161] G.L. Buckley & C.G. Boone, “To Promote the Material and Moral Welfare of the Community”: Neighborhood Improvement Associations in Baltimore, Maryland, 1900–1945, in Environmental and Social Inequalities in the City Since 1800 (R. Rodger & G. Massard-Guilbaud eds., forthcoming 2010) (manuscript at 5, on file with authors) (quoting Sherry H. Olson, Baltimore: The Building of an American City 372 (rev. & expanded ed. 1997)).

[162] Power, supra note 160, at 289.

[163] Id. at 301.

[164] Id. at 302–06.

[165] Id. at 289.

[166] Id.

[167] Power, supra note 160, at 315; see also Buckley & Boone, supra note 161 (manuscript at 6).

[168] Power, supra note 160, at 315. When one property owner attempted to rent a unit on an all-white block to a black family, the real estate board and the health inspector paid him a visit and threatened endless code violations; he relented. Id.

[169] Buckley & Boone, supra note 161 (manuscript at 13, 21).

[170] Id. (manuscript at 14).

[171] Power, supra note 113, at 631, 648.

[172] Id. at 652–53.

[173] Id. at 653 (quoting Byrne v. Md. Realty Co., 98 A. 547, 549–50 (Md. 1916)).

[174] Id.

[175] Id.

[176] Id.

[177] Id. Specifically, tall apartment buildings were limited to the inner-city areas along Charles Street, University Parkway, Eutaw Place, and Lake Drive. Id.

[178] Id.

[179] Power, supra note 160, at 319; Sherry H. Olson, Baltimore: The Building of an American City 325 (rev. & expanded ed. 1997).

[180] Buckley & Boone, supra note 161 (manuscript at 18).

[181] Id.

[182] Id.

[183] Id.

[184] Id. (manuscript at 18–19).

[185] Id. (manuscript at 19).

[186] See Jacobs, supra note 22, at 301.

[187] See id. at 300–02.

[188] Home Owners’ Loan Corp., Area Description: City of Baltimore, Security Grade D, Area No. 1 (NS Form-8) (1937) (on file with authors) [hereinafter HOLC, Grade D, Area 1].

[189] Home Owners’ Loan Corp., Area Description: City of Baltimore, Security Grade D, Area No. 4 (NS Form-8) (1937) (on file with authors) [hereinafter HOLC, Grade D, Area 4].

[190] Id.; Home Owners’ Loan Corp., Area Description: City of Baltimore, Security Grade D, Area No. 5 (NS Form-8) (1937) (on file with authors) [hereinafter HOLC, Grade D, Area 5]; Home Owners’ Loan Corp., Area Description: City of Baltimore, Security Grade D, Area No. 6 (NS Form-8) (1937) (on file with authors) [hereinafter HOLC, Grade D, Area 6]; Home Owners’ Loan Corp., Area Description: City of Baltimore, Security Grade D, Area No. 9 (NS Form-8) (1937) (on file with authors) [hereinafter HOLC, Grade D, Area 9].

[191] HOLC, Grade D, Area 5, supra note 190; Home Owners’ Loan Corp., Area Description: City of Baltimore, Security Grade D, Area No. 8 (NS Form-8) (1937) (on file with authors) [hereinafter HOLC, Grade D, Area 8].

[192] HOLC, Grade D, Area 9, supra note 190.

[193] HOLC, Grade D, Area 1, supra note 188; Home Owners’ Loan Corp., Area Description: City of Baltimore, Security Grade D, Area No. 2 (NS Form-8) (1937) (on file with authors) [hereinafter HOLC, Grade D, Area 2]; HOLC, Grade D, Area 4, supra note 189; HOLC, Grade D, Area 5, supra note 190; HOLC, Grade D, Area 6, supra note 190; HOLC, Grade D, Area 8, supra note 191; HOLC, Grade D, Area 9, supra note 190.

[194] Home Owners’ Loan Corp., Area Description: City of Baltimore, Security Grade C, Area No. 1 (NS Form-8) (1937) (on file with authors) [hereinafter HOLC, Grade C, Area 1]; Home Owners’ Loan Corp., Area Description: City of Baltimore, Security Grade C, Area No. 2 (NS Form-8) (1937) (on file with authors) [hereinafter HOLC, Grade C, Area 2];
Home Owners’ Loan Corp., Area Description: City of Baltimore, Security Grade C,
Area No. 3 (NS Form-8) (1937) (on file with authors) [hereinafter HOLC, Grade C, Area 3];
Home Owners’ Loan Corp., Area Description: City of Baltimore, Security Grade C, Area
No. 4 (NS Form-8) (1937) (on file with authors) [hereinafter HOLC, Grade C, Area 4];
Home Owners’ Loan Corp., Area Description: City of Baltimore, Security Grade C, Area
No. 5 (NS Form-8) (1937) (on file with authors) [hereinafter HOLC, Grade C, Area 5];
Home Owners’ Loan Corp., Area Description: City of Baltimore, Security Grade C, Area
No. 12 (NS Form-8) (1937) (on file with authors) [hereinafter HOLC, Grade C, Area 12];
Home Owners’ Loan Corp., Area Description: City of Baltimore, Security Grade C, Area
No. 13 (NS Form-8) (1937) (on file with authors) [hereinafter HOLC, Grade C, Area 13].

[195] HOLC, Grade C, Area 1, supra note 194; HOLC, Grade C, Area 2, supra note 194; HOLC, Grade C, Area 3, supra note 194; HOLC, Grade C, Area 4, supra note 194; HOLC, Grade C, Area 5, supra note 194; HOLC, Grade C, Area 12, supra note 194; HOLC, Grade C, Area 13, supra note 194.

[196] This map was created by the geographic information system team by geo-coding the addresses from the HOLC reports.

[197] HOLC, Grade D, Area 4, supra note 189; HOLC, Grade D, Area 5, supra note 190; HOLC, Grade D, Area 6, supra note 190; HOLC, Grade D, Area 8, supra note 191; HOLC, Grade D, Area 9, supra note 190.

[198] HOLC, Grade D, Area 1, supra note 188; HOLC, Grade D, Area 5, supra note 190; HOLC, Grade D, Area 6, supra note 190; HOLC, Grade D, Area 8, supra note 191; HOLC, Grade D, Area 9, supra note 190.

[199] See Power, supra note 160, at 317–19; Sherry Olson, Baltimore 57 (1976).

[200] Power, supra note 160, at 316; see Olson, supra note 199, at 52–53.

[201] Power, supra note 160, at 316; see also Olson, supra note 199, at 52–53.

[202] Power, supra note 160, at 317. This pattern of isolation and withholding of basic services to black neighborhoods occurred during this period across the country. Cole & Foster, supra note 46, at 69.

[203] Power, supra note 160, at 325 (“The white majority, first through the segregation ordinances and then through a publicly sponsored conspiracy, enforced racial segregation in the city.”); see Olson, supra note 179, at 325.

[204] We considered providing demographic information on the BZA and the city council during this period. Certainly, changes to these bodies provide fertile ground for research into the disappearance of the disamenity gap in 2000. For the purposes of this Article, however, such data are not central. In fact, our primary goal here is to show how race was injected into the system, quite apart from the attitudes of the individual decision makers. We purposefully are not making a claim on the attitudes or behaviors of the individual decision makers after 1940, but rather seek to illustrate how earlier explicit racism can continue in the system.

[205] Dara Roithmayr, Locked In Segregation, 12 Va. J. Soc. Pol’y & L. 197, 197, 209 (2004).

[206] Id. at 209.

[207] Id. at 211 (citation omitted).

[208] See id.

[209] Id. at 210.

[210] Id. at 209–10.

[211] Id. at 210.

[212] Id.

[213] Id. (citation omitted).

[214] Power, supra note 113, at 660.

[215] Id.

[216] Id.

[217] Id. Historian Sherry Olson has documented this widespread pattern throughout Baltimore County. Olson, supra note 199, at 57 (“Half the [African-American] communities in Baltimore County were zoned for industrial or commercial use.”).

[218] Power, supra note 113, at 660.

[219] Id. (citing Jackson v. Shawinigan Electro Prods. Co., 132 Md. 128 (1918) (requiring money damages be paid to adjacent homeowners because noxious fumes from a recently constructed ferro-silicon plant in East Baltimore constituted a nuisance)).

[220] Id. (quoting Bove v. Donner-Hannah Coke Corp., 258 N.Y.S. 229, 236 (N.Y. App. Div. 1932) (“It is not for the court to step in . . . and condemn as a nuisance a business which is being conducted . . . at the very spot where the [zoning ordinance] said that it might be located.”)).

[221] See id. at 631.

[222] See id. at 660; Rathkopf et al., supra note 136, § 61:1–:50, at 61-2 to 61-136.

[223] See Power, supra note 113, at 660.

[224] See id. at 666–67.

[225] Id.

[226] Id. at 667 (citing Zoning Body Moves to Bar Row Houses, Sun (Balt., Md.), Jan. 4, 1924, at 3).

[227] Id. at 667–68.

[228] Id. at 667. See generally Buckley & Boone, supra note 161 (manuscript at 9–18) (discussing the concerns and meetings of various neighborhood improvement associations).

[229] Rachel D. Godsil, Remedying Environmental Racism, 90 Mich. L. Rev. 394, 396 (1991) (noting that a result of opposition to hazardous waste facilities by well-meaning environmentalists in affluent communities is that the sites are placed in predominantly poor, minority communities); Buckley & Boone, supra note 161; see also James Hamilton, Testing for Environmental Racism: Prejudice, Profits, Political Power?, 14 J. Pol’y Analysis & Mgmt. 107 (1995) (finding that levels of political activism were negatively associated with the probability of hazardous waste facility expansion).

[230] Balt., Md., Ordinance 922 (May 19, 1923).

[231] Power, supra note 113, at 636.

[232] Id.

[233] See id.

[234] See Jon C. Dubin, From Junkyards to Gentrification: Explicating a Right to Protective Zoning in Low-Income Communities of Color, 77 Minn. L. Rev. 739, 740–41 (1991).

[235] Yale Rabin has documented several instances of what he terms “expulsive zoning,” in which the dominant political power deliberately imposes zoning districts that allow LULUs by right. Yale Rabin, Expulsive Zoning: The Inequitable Legacy of Euclid, in Zoning and the American Dream: Promises Still to Keep 101, 106–18 (Charles M. Haar & Jerold S. Kayden eds., 1989); see also Dubin, supra note 234, at 740–41. See generally Arnold, supra note 52 (documenting the high level of LULUs in low-income, minority areas and discussing how new land use planning that involves these communities is the “next frontier” of the environmental justice movement).

[236] Rabin, supra note 235, at 102, 107–08.

[237] Jane Jacobs, Performance Zoning as an Alternative to Use Zoning (Nov. 28, 1972) (unpublished manuscript, on file with Burns Library, Boston College).

[238] Id.

[239] Balt., Md., Ordinance 1247 § 1, para. 11 (Mar. 30, 1931) (containing Baltimore’s initial zoning ordinance). The BZA allowed prior nonconforming uses to continue at a site when it found “that a non-conforming use [had been] established prior to the passage of the Zoning Ordinance [and had] not been abated.” See, e.g., Joseph Burman, No. 2-38 (Balt. Bd. of Zoning Appeals Jan. 11, 1938) (on file with authors).

[240] See Charles Lord & Keaton Norquist, Qualitative Analysis of Zoning Cases Reviewed in Maryland State Archives (Jan. 9, 2009) (on file with authors) (containing original case file photographs and spreadsheet); see also supra notes 215–17.

[241] Id.

[242] Id.

[243] Id.

[244] Balt., Md., Zoning Code § 14-101(b) (2006).

[245] Id. § 14-204(1).

[246] Id. § 14-204(3)–(4).

[247] See generally Jacobs, supra note 22, at 284–85 (describing impact on land and housing inside a “slum” and how it can be improved by “unslumming”).

[248] HOLC, Grade D, Area 4, supra note 189; HOLC, Grade D, Area 5, supra note 190; HOLC, Grade D, Area 9, supra note 190.

[249] See HOLC, Grade D, Area 9, supra note 190 (suggesting that in area 9, “[h]eavy obsolescence of residential property” caused an increase in commercial use for the property rather than continued residential use).

[250] Charles L. Hare, Appeal No. 87-64, at 28 (Balt. Bd. of Zoning Appeals Feb. 20, 1964)
(on file with authors).

[251] Patrick Sipes, Appeal No. 263-88 (Balt. Bd. Of Zoning Appeals Aug. 9, 1988) (on file with authors).

[252] Memorandum from Larry Reich, Dir., Dep’t of Planning, City of Balt., to Gilbert V. Rubin, Executive Dir., Bd. of Mun. & Zoning Appeals (Aug. 8, 1988) (on file with authors); see Patrick Sipes, Appeal No. 263-88X (Balt. Bd. of Zoning Appeals Aug. 16, 1988) (on file with authors).

[253] Nat’l Car Care Dev. Corp., Appeal No. 382-88X, at 1 (Balt. Bd. of Zoning Appeals Nov. 7, 1988) (on file with authors).

[254] Id. at 3.

[255] Through the 1940s and into the 1950s, there were a surprising number of chicken killing and dressing operations. Lord & Norquist, supra note 240.

[256] Id. Applications for these uses tapered off to 18% in the 1960s, 7% in the 1970s, and 12% in the 1980s. In the 1990s, of the files we reviewed we found an increase in applications for these two uses to 18%. Id.

[257] Jacobs, supra note 22, at 230.

[258] Id. at 231.

[259] Id.

[260] The analysis that follows is based on the demographic data in each of the neighborhood reports, see supra notes 179–98, cross-referenced with the disamenity-impact maps created by the University of Vermont using our special-use decisional data, see supra fig.2, and the demographic data maps for Baltimore created by University of Vermont, see supra fig.3.

[261] See supra figs.2 & 4.

[262] See supra text accompanying note 193.

[263] HOLC, Grade D, Area 2, supra note 193; see supra figs.3 & 4.

[264] See HOLC, Grade D, Area 4, supra note 189.

[265] See HOLC, Grade D, Area 2, supra note 193.

[266] HOLC, Grade D, Area 6, supra note 190.

[267] HOLC, Grade D, Area 5, supra note 190.

[268] HOLC, Grade D, Area 6, supra note 190.

[269] Id.

[270] HOLC, Grade D, Area 8, supra note 191.

[271] Id.

[272] Id.

[273] HOLC, Grade D, Area 9, supra note 190.

[274] HOLC, Grade C, Area 5, supra note 194.

[275] Areas C-2, C-6, C-8, C-11, C-12, C-13, C-14 are all in either neutral or low-impact zones. HOLC, Grade C, Area 2, supra note 194; Home Owners’ Loan Corp., Area Description: City of Baltimore, Security Grade C, Area No. 6 (NS Form-8) (1937) (on file with authors) [hereinafter HOLC, Grade C, Area 6]; Home Owners’ Loan Corp., Area Description: City of Baltimore, Security Grade C, Area No. 8 (NS Form-8) (1937) (on file with authors) [hereinafter HOLC, Grade C, Area 8]; Home Owners’ Loan Corp., Area Description: City of Baltimore, Security Grade C, Area No. 11 (NS Form-8) (1937) (on file with authors) [hereinafter HOLC, Grade C, Area 11]; HOLC, Grade C, Area 12, supra note 194; HOLC, Grade C, Area 13, supra note 194; Home Owners’ Loan Corp., Area Description: City of Baltimore, Security Grade C, Area No. 14 (NS Form-8) (1937) (on file with authors) [hereinafter HOLC, Grade C, Area 14]; see also supra fig.2. All of these are white areas. HOLC, Grade C, Area 2, supra note 194; HOLC, Grade C, Area 6, supra; HOLC, Grade C, Area 7, supra; HOLC, Grade C, Area 8, supra; HOLC, Grade C, Area 11, supra; HOLC, Grade C, Area 12, supra note 194; HOLC, Grade C, Area 13, supra note 194; HOLC, Grade C, Area 14, supra.

[276] See HOLC, Grade C, Area 11, supra note 275.

[277] HOLC, Grade C, Area 8, supra note 275.

[278] HOLC, Grade C, Area 13, supra note 194.

[279] Id.

[280] HOLC, Grade C, Area 8, supra note 275; HOLC, Grade C, Area 14, supra note 275.

[281] HOLC, Grade C, Area 8, supra note 275; HOLC, Grade C, Area 14, supra note 275.

[282] See, e.g., HOLC, Grade C, Area 1, supra note 194; HOLC, Grade C, Area 2, supra note 194; HOLC, Grade C, Area 3, supra note 194; HOLC, Grade C, Area 4, supra note 194; HOLC, Grade C, Area 5, supra note 194; HOLC, Grade C, Area 6, supra note 275.

[283] Home Owners’ Loan Corp., Area Description: City of Baltimore, Security Grade A, Area No. 1 (NS Form-8) (1937) (on file with authors).

[284] Transcript of Testimony at 8, A. Boombaum, Appeal No. 943-50, at 5 (Balt. Bd. of Mun. & Zoning Appeals Oct. 18, 1950) (on file with authors) (statement of Josiah F. Henry, Jr.,
Attorney for the Protestors).

[285] Id.

[286] Jerome Robinson, Appeal No. 483-50 (Balt. Bd. of Mun. & Zoning Appeals June 2, 1950).

[287] Transcript of Testimony at 5, Robinson, No. 483-50 (statement of Cyril R. Murphy, Jr., Attorney for the Protestors).

[288] L.W. Woolford, Appeal No. 288-58 (Balt. Bd. of Mun. & Zoning Appeals July 7, 1958).

[289] E.g., Transcript of Testimony at 8, Woolford, No. 288-58.

[290] Id.

[291] Lord & Norquist, supra note 240.

[292] Id. Of the 583 BZA case files that we looked at closely, either the applicants withdrew or the BZA denied the special use application in 237 of those cases, a disapproval rate of 41%. Id.

[293] See generally Juliana Mantaay, Zoning Law, Health and Environmental Justice: What’s the Connection?, 30 J.L. Med. & Ethics 572 (2002) (finding that people living in manufacturing zones are more likely to be poor and members of a minority group).

[294] Arnold, supra note 52, at 3.

[295] See Balt., Md., Ordinance 1247 § 1, paras. 6–7, 11 (Mar. 30, 1931).

[296] See Balt., Md., Zoning Code § 7-407 (2009).

[297] David Michael Ettlin, Milton Allen, City State’s Attorney, Dies at 85, Balt. Sun, Feb. 13, 2003, http://articles.baltimoresun.com/2003-02-13/news/0302130334_1_allen-state-attorney-baltimore/2 (last visited Apr. 18, 2010).

[298] Id.

[299] Alonzo Smith, Schmoke, Kurt L. (1949– ), in BlackPast.org, http://www.blackpast.org/
?q=aah/schmoke-kurt-l-1949 (last visited Apr. 18, 2010). Schmoke defeated Baltimore’s first African-American mayor, Clarence Burns, who had been appointed by outgoing Mayor William Donald Schaefer as he left to be Governor of Maryland. Id.

[300] Tom Chalkley, Party Hardy: Baltimore’s Republicans Soldier On, Despite the Odds, Balt. City Paper, June 19, 2002, http://www.citypaper.com/news/story.asp?id=3417 (last visited Apr. 18, 2010). But see Thomas E. Carney, Baltimore, in Encyclopedia of African American History, 1896 to the Present (2009), http://www.mywire.com/a/Enc-African-American-History-from-1896/Baltimore/9452069 (last visited Apr. 18, 2010) (suggesting that there was not a significantly large population of African-Americans in Baltimore prior to 1890, comparing 15% in 1890 to 60% in 1968).

[301] Id. (“During the 1930s and 1940s, African Americans had no role in city government, but as they began to populate the Democratic Party, they began to take control of their destiny.”).

[302] Balt. City Council, History of the Baltimore City Council, http://www.baltimorecity
council.com/history.htm (last visited Apr. 18, 2010); Roger Biles, Black Mayors: A Historical Assessment, 77 J. Negro Hist. 116 (1992). Clarence Burns, a black politician, was city council president before he became the incumbent for the mayor position.

[303] Jacobs, supra note 22, at 440–41; Johnson, supra note 22, at 105; see also Batty, supra note 4, at 770.

[304] The legacy of such practices may not be as remote as perhaps some believe. In 2009, the city brought suit against Wells Fargo for allegedly steering African-American residents into higher-interest subprime loans—termed “ghetto loans” by some Wells Fargo employees—even if the residents could afford cheaper traditional loans. Michael Powell, Suit Accuses Wells Fargo of Steering Blacks to Subprime Mortgages in Baltimore, N.Y. Times, June 7, 2009, at A16. A federal judge denied Wells Fargo’s motion to dismiss, allowing the city to go forward with its claim that it has suffered damages apart from the individual borrowers because of the number of vacant properties caused by the lending practices and the impact on the city’s tax base. Julie  Bykowicz, City Can Proceed with Wells Fargo Lawsuit, Balt. Sun, July 3, 2009, http://articles.baltimoresun.com/2009-07-03/news/0907020086_1_fargo-lawsuit-foreclosures (last visited Apr. 18, 2010).

[305] See Roithmayr, supra note 205, at 210.

Ahistorical Indians and Reservation Resources

By Ezra Rosser*

This Article is an in-depth exploration of the impacts of an Indian tribe deciding to pursue environmentally destructive forms of economic development. The Article makes two principal contributions. First, it establishes the Navajo Nation’s decision-making role. Prior mineral resource forms of development may have been formally approved by the tribe, but the agreements did not truly belong to the Navajo Nation. Extensive research into earlier agreements shows the heavy influence of the federal government and mining interests historically. Existing scholarship on reservation environmental harm tends to deflect tribal responsibility, attributing such decisions to outside forces. Without denying the challenges the Navajo Nation is facing, the Article calls for recognition, despite the romanticism that surrounds Indians and the environment, of tribal agency and responsibility for the proposed environmental destruction. Second, the Article argues that environmental organizations that make use of federal environmental review processes are complicit in the systematic denial of Indian sovereignty that federal primacy entails. Although there is a strong theoretical argument that the only limits appropriate for Indian nations are those of nation-states under international law, the Article concludes that the relationship between environmental organizations and Indian nations ought to be guided by international human rights law.

 

I. Introduction

Environmental degradation occurring on Indian reservations cannot be simply written off as yet another example of Indians getting screwed.[1] Instead, some tribes have begun, through their sovereign governments, deliberately seeking out the exploitation of their land and natural resources.[2] By choosing to prioritize economic development over the environment, Indian nations are challenging the instinctive “love” that progressives have for all things Indian.[3] Forced to choose between attacking the decisions of Indian nations on the one hand and turning a blind eye to harmful environmental policies on the other, progressives are faced with a classic apples-and-oranges dilemma. For their part, Indian governments pursuing economic development through environmental destruction have to grapple not only with non-Indian opponents—a familiar role for tribal governments—but also with tribal members less willing to make such a trade-off or adversely impacted by particular proposed projects.

Things were a lot simpler when Indians could easily and rightly be identified as the good guys and whites as the bad guys on environmental issues.[4] It is still the case, I believe, that such a mental shortcut is largely justified on most issues, from poverty to land rights to recognition of sovereignty, but it is becoming more complicated with regard to the environment. To explain why that is so, it is worth thinking about the broad trends that have defined the relationship between environmental destruction and Indian nations. For much of American history, the relationship was an oppressive one. Whites—whether in the form of the U.S. government, companies, or as individuals—simply took natural resources from Indian tribes or, by subordinating Indian agency, simultaneously exploited both Indian land and tribal members.[5] Later, recognition that tribes should at least formally play a role in approving natural resource use and extraction changed the relationship from oppressive to inequitable. Tribes were compensated for their environmental goods, but Indians received less and lost more than they should have.[6] Bad faith in the form of the failure of the United States to live up to its trust obligations, or a mere pro forma role for tribal leaders in decisions with an environmental impact, led to inequitable compensation for Indian tribes.[7] The relationship between tribes and environmental destruction is now entering the modern period, one in which the terms of such destruction are tribally accepted even if the relationship is not entirely tribally defined. Besides challenging romantic notions of Indians as the first environmentalists, tribal activities that harm the environment undermine the position of some Indian advocates that Indian policies should not be subject to critique or limitation because of the inherent sovereignty of Indian nations.

This Article makes two principal contributions. First, it establishes that the Navajo Nation freely chose to pursue an environmentally destructive form of economic development. Prior mineral resource-based development may have been formally approved by the Navajo Nation Council, but the agreements did not truly belong to the tribal government. Extensive research into the nature and royalty rates of the extraction agreements made up until the Navajo Nation’s coal-fired power plant proposal shows the heavy influence of the federal government and mining interests. Prior scholarship on reservation environmental harm tends to deflect tribal responsibility, attributing such decisions to outside forces. Without denying the challenges the Navajo Nation is facing, the Article calls for recognition, despite the romanticism that surrounds Indians and the environment, of tribal agency and responsibility for the proposed environmental destruction. Second, I argue that environmental organizations that make use of federal environmental review processes are complicit in the systematic denial of Indian sovereignty that federal primacy entails. Although there is a strong theoretical argument that the only limits appropriate for Indian nations are those of nation-states under international law, the Article concludes that the relationship between environmental organizations and Indian nations ought to be guided by international human rights law.

With environmental awareness on the rise and non-Indian governments increasingly voicing concern about various forms of pollution,[8] resolving the apples-and-oranges, incomparable goods problem is becoming an imperative for tribes and environmentalists alike. Instead of disagreement with regard to prioritizing sovereignty or the environment giving way to confrontation and litigation, it is imperative that Indian advocates and environmentalists accept two core principles. First, Indian nations have the right to deviate from non-Indian organizations and governments when it comes to environmental decisions. Simply identifying a group of people, tribal members or not, harmed by a tribe’s choices should not be enough to halt projects opposed by environmentalists. Second, the relational aspects of sovereignty limit what Indian nations can and should be able to do as far as environmental destruction that impacts non-Indians. Thinking about tribes as nations under international human rights law arguably provides the best way of recognizing the appropriate bounds on sovereignty when it comes to environmental destruction. While strong environmentalists will reject the first principle and Indian law advocates will be troubled by the second, the two are needed in order to prevent paralysis or backsliding on both fronts. Importantly, a human rights approach is an appropriate guide for environmental organizations and for tribes, regardless of whether the legal structure of environmental permitting remains federally defined.

Inspired by a reporter’s question of whether it was good that the Navajo Nation is now developing its own coal-fired power plant, this Article explores the evolving relationship between environmental destruction and Indian nations. The Navajo tribe’s experiences with this relationship provide the primary window on this relationship, but other tribes’ histories and decisions are also included.[9] In Part II, the often oppressive, and imposed, forms of environmental destruction of Indian land are presented, with a focus on coal leasing. Part III focuses on the stereotype of Indians as environmentalists and explores how, even after tribes formally regained some measure of decision-making power, inequities in bargaining and outcomes continued to exact forms of environmental injustice upon Native peoples. The Article shifts in Part IV to the current interplay between reservation poverty and environmental harms, focusing on the Desert Rock power plant proposal as an example of tribal acceptance of certain environmental costs in return for needed government revenue and reservation job creation. Three alternatives regarding tribal power—federal primacy, cooperative agreements, and nation-state treatment—are then explored. In Part V, I argue that the participation of environmental organizations in federally defined environmental oversight processes of reservation development reflects a denial of tribal sovereignty by such organizations. The Article concludes that treating Indian nations as subject to international human rights law provides the best way of respecting Indian sovereignty while also putting an outer limit on sovereignty when it comes to the environment.

II. Oppression and Exploitation

The Manhattan Project and America’s nuclear weapons program left its mark on the Navajo Nation. While shocking in its lasting impact on Diné workers and families, the effects of unprotected uranium mining are but reflections of a larger pattern of oppressive natural resource extraction.[10] As one former worker noted, Navajo miners were treated as “expendable,” were not informed of the dangers involved, and suffered grave health consequences.[11] Another ex-miner wondered why they were never warned of known health risks and asked, “Are we disposable to the government?”[12] Apparently so. As the New York Times reported, “Of all the chapters of the cold war and its aftermath in the United States, there are none, perhaps, quite as chilling as what happened to a generation of Navajo men and their families.”[13] Even long after the more than one thousand mines closed or were abandoned,[14] Navajos inhaled radioactive dust blown off of open-air uranium piles, drank contaminated water, and even slept on floors constructed of waste material.[15]

On April 19, 2005, the Navajo Nation Council passed the Diné Natural Resources Protection Act,[16] forbidding uranium mining “within Navajo Indian Country.”[17] Signed into law ten days later by Navajo President Joe Shirley, Jr., the Act declared that uranium mining was antithetical to Navajo Fundamental Law regarding protection of the Nation’s natural resources and to the teachings of medicine peoples regarding “harmony and balance in life and a healthy environment.”[18] The Act was also a condemnation of the “social, cultural, natural resource, and economic damage to the Navajo Nation from past uranium mining.”[19] Though the actions of the tribe were in opposition to the energy strategy of then-President George W. Bush, those opposed to nuclear energy and uranium mining celebrated the tribe’s uranium ban.[20] With mining companies attempting to set up shop on the borders of the reservation, it is too early for the tribe to declare victory.[21] But it is remarkable that, at least for now, “the Saudi Arabia of uranium,”[22] the Navajo Nation, is foregoing uranium-based jobs and royalties.

At the same time that the tribe is fighting to prevent uranium mining, the Navajo Nation is plowing ahead with a plan to build a new coal-fired power plant.[23] The proposed Desert Rock power plant would be a mine-mouth “clean coal” power plant built on the Navajo Nation, just south of two existing Four Corners area power plants.[24] Backing the plant are Diné Power Authority, an entity of the Navajo Nation, and the tribe’s partner, Sithe Energy, an off-reservation energy company eighty-percent owned by the Blackstone group, a large, publicly traded New York equity company.[25] As a mine-mouth plant, Desert Rock would be built right next to a reservation open-pit mine and the tribe would receive over fifty million dollars annually in taxes and in royalty payments for the extracted coal.[26] Additionally, under the agreement with Sithe Global, which is providing the start-up capital, the tribe has an option to purchase a share in the power plant itself.[27]

In the 2008 State of the Navajo Nation Address, Navajo Nation President Joe Shirley, Jr. highlighted Desert Rock’s significance: “[It] was envisioned as a way to make use of our abundant resource of coal, and bring economic prosperity to our people. . . . [T]his Project remains the most important economic, environmental, and energy challenge that the Navajo Nation has ever undertaken.”[28] The proposal is not without controversy: The State of New Mexico, a number of Navajo and non-Navajo environmental organizations, and even a Facebook group are united in opposition to the power plant.[29] The project’s future is uncertain, according to the Navajo Nation President, “because of the enviros . . . the doomsday advocates . . . [who] worry more about the ferrets, the squirrels, and the frogs, and the spotted owl, rather than the endangered Navajo people.”[30]

That President Shirley and the Navajo Nation Council have taken such strong stances on Desert Rock and on uranium mining attests to the relatively empowered sovereignty now enjoyed by the Navajo Nation. Though not necessarily incompatible positions,[31] the very fact that the tribe decided to aggressively go forward with one type of mining and energy development while spurning another highlights the impact of tribal decision making on American energy and environmental policy. The views of the Navajo Nation and non-Indian governments and organizations will inevitably conflict at times and, given the linkages between the tribe and non-Indians as well as the spillover effects of tribal choices, it is important to establish ex ante principals for resolving such conflicts. Historically, potential conflict was avoided by simply imposing non-Indian natural resource policies and environmental choices upon tribes, an imposition that, while straightforward in application, ignored or undermined tribal rights to self-determination.[32]

The “permanent home” of the Diné was formally recognized by the United States through an 1868 treaty.[33] “Diné” can be translated literally from the Navajo/Diné language as “the people” and commonly is not used as a term for “government,” which is instead called “the tribe” or the Navajo Nation.[34] Originally the Diné occupied territory defined by four sacred mountains (Mt. Blanca to the East, Mt. Taylor to the South, San Francisco Peaks to the West, and Mt. Hesperus to the North),[35] but following contact with non-Indians, their recognized land holdings have shrunk.[36] Nevertheless, now roughly the size of West Virginia, the Navajo Nation spans parts of Arizona, Utah, and New Mexico, and contained within its borders are Chaco Canyon, Monument Valley, and Canyon de Chelly.[37] It is a “beautiful, austere, and varied country,” with a population of more than 180,000, of whom only three percent are non-Indian.[38] An independent nation whose sovereignty is recognized by the U.S. government, the Navajo Nation has the most land of any tribe, and also the largest government bureaucracy.[39] From the capitol of Window Rock, Arizona, Navajo Nation President Joe Shirley, Jr. governs, along with the Navajo Nation Council and Navajo Nation Supreme Court,[40] in much the same way, and must confront similar challenges, as do those who work out of Washington, D.C.

It has not always been this way. The United States signed two treaties with the Navajo tribe, one in 1849 and the second in 1868.[41] The Treaty at Fort Sumner in 1868 marked the end of a particularly bad period for the Diné. After an 1864 military defeat at Canyon de Chelly at the hands of Kit Carson, Navajos were rounded up and forced on what became known as the Navajo Long Walk to Fort Sumner and the surrounding Bosque Redondo reservation where they were held captive.[42] They were only allowed to escape the bad conditions that characterized their captivity and return to a diminished version—no longer extending to the four sacred mountains—of their homeland with the signing of the Treaty at Fort Sumner.[43] By the treaty, the reservation was “set apart for the use and occupation of the Navajo tribe” and was established as “their permanent home.”[44] Although treaty ratification is an inherent recognition of tribal sovereignty, in practice the United States, until recently, treated the Navajo reservation as an area whose natural resources could be extracted or developed with only a limited say from a government representing the Diné.[45] The results were unjust and arguably tragic: The Diné suffered a range of environmental harms without benefiting as they should have, and the Navajo Nation’s ability to protect its citizens and afford them opportunities was significantly undermined for more than a century.[46]

The United States and non-Indian business interests were determined to extract natural resources located on reservations, including the Navajo.[47] Poor soil quality and infrequent rain limited the agricultural potential of the land, diminishing the impact white land greed had on the Navajo Nation relative to many other tribes.[48] Non-Indians, with the important exception of Indian traders and church groups, did not particularly push to live on the Navajo reservation.[49] But though not wanting to live in Navajo country, non‑Indians did and do covet the natural resource holdings of the tribe.[50]

A. Black Mesa Coal

In 1909, “[a] rapid reconnaissance was made by wagon” of the coal beds of Black Mesa by M.R. Campbell and H.E. Gregory.[51] While acknowledging the “fragmentary” nature of their data, they reported that “there is considerable coal in this field” and that it was of good quality.[52] They also reported that a small mine, producing 2500 tons annually “to supply fuel for the Indian school,” was already in operation at Keams Canyon.[53] The ability of turn-of-the-century explorers to locate the coal field owed itself in part to the relative shallowness, as little as six meters in depth, of the “overburden” separating the buried coal from the surface.[54] Black Mesa is located in northern Arizona and includes contested portions of the Navajo and Hopi reservations.[55] Later surveys would confirm the existence of a considerable amount—400 million tons—of strippable coal at Black Mesa.[56] But coal development on the Navajo reservation was slow for almost fifty years. In the 1930s, small-scale, cottage-industry-type family truck mines, employing between seven and nine men, emerged across the Navajo Nation.[57] This gave way to more formal commercial explorations only in the 1950s.[58] The first large lease, finalized in 1957, was between the Navajo tribe and Utah Construction and Mining Company for 24,320 acres in the eastern part of the reservation.[59] Large lease agreements signed in 1964 with Pittsburg & Midway Coal Mining Company for 11,157 acres near Window Rock, Arizona, and with Peabody Coal Company for 24,858 acres on Black Mesa, symbolize the “unprecedentedly intense commercial interest” of the early 1960s in Hopi and Navajo coal.[60] By 1971, Black Mesa alone was annually producing over one million tons of coal.[61]

The development of Black Mesa has not been without controversy. Winona LaDuke has called Black Mesa “the mother of all ecologically destructive mining complexes.”[62] In 1971, the Sierra Club and other environmental groups purchased full-page protest ads in papers such as the New York Times.[63] The headline: “Like Ripping Apart St. Peter’s, In Order to Sell the Marble.”[64] The body of the ad was similarly strong, noting that instead of being near the growing cities of California and Las Vegas, the mining and associated power plants were being “put . . . elsewhere, where no one will complain,” where they will face “[n]o ‘important’ opposition.”[65] Though framed as the destruction of sacred Hopi and Navajo sites, the environmental groups dedicated the bulk of the ad’s discussion of the harms to Indians to publicizing Hopi resistance to mining on Black Mesa.[66] But before discussing Hopi resistance and the Navajo experience, it is important to set the stage with the development of oil leasing, which preceded the rise of coal.

B. Oil and the Formation of the Navajo Nation Council

The Navajo Nation Council owes its existence to the discovery of oil on the Navajo reservation in 1922.[67] By the time coal leases were being worked out for Black Mesa, the Navajo council was firmly in place and the tribe did not suffer the same division between traditionalists and the tribal council as the Hopi tribe.[68] Today, the Navajo Nation Council concerns itself with all aspects of tribal governance; “[i]n its infancy, however, the group was associated almost exclusively with oil development.”[69] The first meeting was held on July 7, 1923, and immediately the council approved a fast track oil leasing arrangement.[70] This single-minded focus was deliberate: The Navajo Nation Council “was organized by the Bureau of Indian Affairs in order to produce a ‘legitimate’ body of Navajo who could lease Navajo lands to oil companies for drilling.”[71] According to Ward Churchill, this handpicked council marked the start of tribal self-governance.[72] The tribal council’s role, in the words of the first council’s chairman, Jake  Morgan, “is like an inner part of a sandwich. It comes between the Navajo tribe and the United States government.”[73]

Professor Kathleen Chamberlain’s excellent history of Navajo oil development powerfully documents the ties between oil companies, non‑Indian governments, and Navajo leaders.[74] Some Navajos had misgivings about the effect drilling would have on the earth,[75] but Chee Dodge, the first person selected to be tribal chairman, assured former New Mexico territorial governor Herbert J. Hagerman that the Navajos, accustomed to being under the U.S. government “for years and years,” wanted “to do what the government says” regarding oil development.[76] This, despite the fact that high production nationwide at the time Navajo land was to be opened up meant that the auctions held were arguably “against the welfare of the Indian owners.”[77] Significantly, on the question of whether to distribute the oil funds on a per capita basis to individual members or to have the tribal government hold and control the funds, the council decided not to go the per capita route.[78] Though with time oil was largely replaced by other natural resources, relegating funds to the tribe “served as the financial core of the future Navajo Nation government,” and is an important legacy of the oil development of the 1920s.[79]

At the peak in the late 1950s, royalties associated with oil leasing totaled $27.7 million and represented ninety percent of the tribal budget.[80] Royalty money allowed the tribe “to generate even more improvements and achieve quasi-autonomy.”[81] In 1955, a “rich find,” the Aneth Strip in southern Utah, occurred.[82] “Aneth meant oil—Big oil!”[83] According to the Bureau of Indian Affairs (BIA), the Navajo Nation’s auction of rights to the land the following year was the biggest sale in BIA’s history up to that time.[84] But despite the size of the Aneth oil field and the high quality of Hogback and Rattlesnake crude, the tribe’s return on its oil was just “one-eighth (or one‑sixth) of the assessed value of the oil produced.”[85] Diné living in southern Utah benefitted very little from the Aneth Strip’s oil wealth, despite congressional acts requiring that Utah use 37.5% of its royalties to improve the welfare of area Navajos.[86] But they remained poor, with neither the state of Utah, which squandered money that should have gone towards area Navajos, nor the tribe, which used royalty money for the general tribal budget, seeming to do much for those in the area.[87]

In 1977, southern Utah Diné rebelled, setting up roadblocks and “shut[ting] down operations” at the Aneth oil field.[88] The unrest began initially with forty to fifty Diné seizing control of a pumping unit, but the “occupying force” eventually “swelled to one thousand” people.[89] The Coalition for Navajo Liberation, a grass roots organization supporting the people of the Aneth region prior to the occupation, provided the institutional support for the protestors.[90] The occupation was sparked by a shooting—an oil worker “shot at” a Diné sheepherder on horseback, a story confirmed by empty shell casings on the scene—but ended up being an expression of frustration directed at the oil companies and local governments.[91] Though a compromise was eventually reached, addressing many of the protestor concerns and ending the oil field takeover, tensions remained high: The next year residents threw rocks at oil employees working to identify new well sites.[92]

The occupation of the Aneth oil fields was but a local, dramatic example of a generalizable truth regarding oil on the reservation and the Diné: “[T]he underground wealth of their land has not meant a better or easier life.”[93] From the first approval of oil leases, the tribe has had an uneasy relationship with oil extraction; the Aneth occupation was not the first rebellion against oil company operations on the reservation. Chamberlain reports that in 1933, “Navajos passed a resolution to cancel all oil or gas leases, even those extended by council in 1926 and renewed in 1931.”[94] Such a quick reversal is impressive considering that the council was formed in part to approve such leases.[95] The reversal also reflects the practical limits on the supposed authority of tribes during this period.[96] Laying blame squarely on the federal government, Chamberlain argues that “from 1923 forward, the Interior Department repeatedly failed to maximize revenues.”[97] Ultimately the history of oil leasing on the Navajo Nation, though both commencing and peaking earlier, mirrors that of Black Mesa coal leases.[98]

C. Hopi Resistance

Opposition to the Black Mesa mining made public a long-standing power struggle between the traditional form of Hopi governance and the centralized tribal council that had approved the leases.[99] In 1934 Congress passed the Indian Reorganization Act (IRA).[100] The brainchild of Associate Solicitor of Indian Affairs Felix Cohen and Commissioner John Collier, the IRA on its face officially ended the disastrous allotment policy and offered tribes a structure for once again having their governance rights recognized.[101] The IRA had a centralized, corporate, secular vision of tribal governance, and tribal approval was required before an IRA government was established.[102] The Diné voted against the IRA, but it was approved—part of what Professor Charles F. Wilkinson considers Collier’s “biggest error”—by one third of the eligible Hopi voters.[103] The Kikmongwi, the traditional religious leaders of the various Hopi villages, mostly opposed the change to a centralized government, and the majority of Hopi chose to not vote in the BIA election that put in place a new tribal IRA constitution.[104] By replacing separate Kikmongwi village-based leadership with a centralized government, the IRA facilitated greater access to natural resources on Hopi land,[105] but not without cost: The tribal council was seen as the “white man’s government,”[106] as an “imposed” secular and central authority,[107] and as such it lacked legitimacy.[108]

In their resistance to mining on Black Mesa, Hopi traditionalists would challenge a federal judge’s characterization of the tribe as “a timid and inoffensive people, peaceable with outsiders.”[109] The Hopi Tribal Council’s lease with Peabody was orchestrated by a non-Indian attorney ostensibly representing the tribe but who had close, ongoing ties to Peabody, an obvious conflict of interest, the details of which were uncovered by Professor Wilkinson.[110] The Kikmongwis’ protest eventually entered the court system, but the United States Court of Appeals for the Ninth Circuit treated their objections as if they were simply those of “62 dissident traditional Hopis.”[111] In resting its dismissal of the case on the sovereign immunity of the tribal council, the court was equally dismissive of the Kikmongwis’ challenge to the tribal council’s legitimacy and its power to enter into such an important lease.[112]

The lease signed by the Hopi Tribal Council in 1966 was an oppressive one. It contemplated a thirty-five-year lease with no “reopener, a standard provision allowing renegotiation after an agreed period, usually ten years.”[113] As a result, until it was renegotiated by Reid Chambers in 1987, the Hopi Tribe was receiving far less than even coal leases on public land produce.[114] Additionally, the Hopi were not protected from, nor adequately compensated for, the water use—three million gallons per day—needed to connect the mine with an associated power plant by coal slurry.[115] The power struggle between the Hopi Tribal Council and the traditional Kikmongwi form of Hopi governance drew attention to the lack of meaningful Hopi approval or involvement in the original lease.[116] Together, Peabody and the United States were intent on getting Hopi coal and they did, using formal approval to mask the oppressive nature of the lease in terms of both process and compensation.[117] The initial lease for mining on Black Mesa was approved by the United States Department of the Interior “[w]ithout even consulting the tribes,”[118] a tellingly open claim by the Interior Department to Black Mesa coal that “was still subject to the joint concurrence of the Navajo and Hopi tribal councils.”[119]

D. Navajo Experience

The Navajo Nation, perhaps because Black Mesa makes up a relatively smaller portion of the entire reservation compared to the Hopi or perhaps because the Navajo Nation Council enjoyed greater legitimacy, did not experience the same internal upheavals as a result of the leasing of Black Mesa. In her study of Black Mesa mining operations, Suzanne Gordon quotes Peter McDonald, former chairman of the Navajo Nation Council, as saying, “Strip mining doesn’t really bother me . . . because, first of all, any resource that is on the reservation under the ground is for the Navajo to utilize.”[120] Gordon went on to note that McDonald, unlike fifty-three families that had to be relocated, could tolerate the mine because of the geographical distance between the mine—it was “not in his backyard”—and Window Rock.[121] Black Mesa transitioned from a traditional rural, extended-family, herding‑and‑farming community located a great distance from formal sector employment to an area that by 1985 had staved off depopulation in large part because of mining.[122]

The difference between the vocal Hopi resistance and the somewhat more muted Navajo reaction to the initial Black Mesa lease arguably reflects the different position of the tribal council in the two tribes.[123] Though tribes are subject to limits on their sovereignty, the central Navajo government plays a more important and expanded decision-making role with regard to the direction of the tribe than was the case in prior generations.[124] Traditionally the tribe was organized according to extended family groupings, but though the clan system continues to have an important place in Diné society and in Navajo private law, the Navajo government has taken on many Anglo traits.[125] During the New Deal, the Navajo people voted against having their government formed according to Washington’s prescribed corporate structure, so unlike the Hopi they never approved an IRA constitution.[126] Nevertheless, their chosen form of governance has tended to centralize authority in Window Rock.

Efforts to decentralize and devolve government authority to local chapters more reflective of “tribal federalism” and the tribe’s form of dispersed governance precontact have met with only limited success.[127] Such  a concentration of authority is not entirely a matter of changing internal norms; rather, it reflects the heavy historical and logistical hand that outside influences have had on Navajo self-governance. External and logistical forces involving the relationship between tribes and the United States propel tribes to centralize authority even if traditionally tribal governance was more local.[128] (The challenges the Hopi Kikmongwi village leaders have had getting their authority recognized by the United States attests to this.)[129] Logistically, for ease of administration and perhaps for equal treatment reasons, the U.S. government, reflecting the same general cultural bias, has long sought to treat tribes as if they were interchangeable.[130] This manifests itself in one-size-fits-all approaches as well as a related indifference to cultural distinctions across, and within, tribes that might suggest alternative, individualized, policy approaches.[131] For a tribe attempting to get particular issues resolved, not only would it be counterproductive to have more than one voice on tribal matters, but also the United States may be unwilling to listen to more than one centralized tribal government.[132] When convenient, the United States has shown its willingness, as in the Hopi case, to use multiple sites or possibilities of legitimate tribal governance as a way to recognize only those leaders supportive of U.S. policies.[133] Similarly, when internal tribal dissent or disagreements between traditional and modern tribal authorities cause reservation instability or seem to threaten U.S. interests, the United States shows little toleration.[134] The message—replicate our strong central authority, particularly executive authority—has not been lost on the Navajo Nation. The Navajo Nation consists of 110 chapters, and while these chapters, each with its own chapterhouse, are local governments with some local control, there has been a rise in the importance of the central tribal bureaucracy.[135] Such centralization reflects the need—acknowledged as early as 1920 by tribal leaders—for a single tribal voice when dealing with BIA and other parts of the U.S. government, especially when it comes to natural resources.[136]

The Navajo Nation Council’s 1964 initial Black Mesa lease arguably is not as oppressive as the lease signed by the Hopi. Even if the Navajo Nation received the same royalty rights as the Hopi—something not in fact true[137]—the approval by the tribally accepted government perhaps saves this lease from an “oppressive” characterization.[138] But just barely, or at least that is the on-reservation view according to the United States Commission on Civil Rights’s 1975 report, The Navajo Nation: An American Colony.[139] The  Commission quoted Navajo Nation President Peter MacDonald’s take on the coal leases: “Well, we, the Navajos did not have an opportunity to even discuss the pros and cons of strip mining when it was put to us, that we leased the coal to the companies and that they were going to mine it, surface mining or strip mining.”[140] Without the opportunity to discuss mining, much less engage in meaningful debate about leasing, the Commission’s summary of development at the time as “no more than exploitation, with profits flowing off the reservation” seems fairly accurate.[141] Scholars who have focused on Navajo resource development tend to agree—laying blame on the federal government, federal attorneys, and BIA—that the leases did not adequately compensate the tribe.[142]

An argument can be made that the leases did reflect market rates, though structural and market forces depressed the amount the Navajo Nation received for its coal. The United States subsidizes coal development of public lands by opening up such land to coal extraction at bargain basement rates.[143] This essentially caps the amount the tribe can demand of coal companies given the ability of companies to choose between tribal and public land leasing.[144] Even though tribes control a disproportionate amount of U.S. coal deposits, their holdings are not enough to counteract the public land subsidies.[145] In his Ph.D. dissertation looking at Navajo and Hopi royalty rates, Brian Jackson Morton rejects the “hypothesis of buyer dominance,” pointing to the fact that the tribes received rates above the statutory minimum rate.[146] For those who accept market pricing as the definition of whether the Navajo Nation received adequate compensation, Morton’s claim that the leases gave Navajos the “prevailing rates” might seem dispositive.[147] Morton, however, argues that federal coal management shaped “the opportunity set facing the tribes.”[148] Federal public land and coal leasing policies controlled supply, ensuring both record profits for coal companies and tribal coal royalties that were small and suboptimal from a tribal perspective.[149]

How should the federal shaping of the “opportunity set” regarding the Navajo Nation’s leases be understood? For structuralists with a pro-Indian orientation, the low rates fit squarely into the larger “history of unmitigated malfeasance” on the part of non-Indians.[150] The Commission on Civil Rights’s general conclusion in 1975 regarding development was that “the federal government, faced with several alternatives, has consistently opted for the one of least benefit to the Navajo people and their land and the one most likely to perpetuate a welfare existence on the reservation.”[151] The Commission’s conclusion seems to reflect Sam Deloria’s criticism of the scholarly “tendency to find a devil to blame” in the Indian resource development policies of the 1960s.[152] But even taking into account Deloria’s concern, whether or not there were sinister motives does not change the fact that federal policies and market choices diminished Navajo returns on their coal.[153] Cheap public land, limited competition in bidding on Indian leases, a preference for leasing to non-Indian businesses, and a concentration of power in a few oligarchic firms combined to keep royalty rates low.[154] As a result, the Navajo Nation, having been “led into these prejudicial agreements by the federal government,” was “not getting a fair return on its energy resource leases.”[155] Under the first lease the tribe was compensated at a royalty rate of 37.5 cents per extracted ton, or about two percent of gross proceeds.[156] The rate was “artificially low,” even when compared with coal leases in the third world.[157]

In 1987, the Navajo Nation and Peabody Coal amended the royalty rate associated with Black Mesa leases.[158] The agreement that was reached did not reflect the value of the coal extracted and instead exploited the bargaining position of the Navajo Nation,[159] with the full knowledge of the Secretary of the Interior, who was charged with signing off on the agreement.[160] In 1985, Peabody Coal, aware that an Interior Department determination that the appropriate rate should be increased ten times from that of the initial lease, from 2% to 20%, decided to lobby the Secretary of the Interior David Hodel to delay release of this tribally supportive determination.[161] Stanley Hulet, a personal friend of Secretary Hodel, was paid $13,000 for a thirty-minute ex parte meeting with the Secretary, after which Hodel intervened on behalf of Peabody and “derailed the lease adjustment” that would have supported a 20% royalty rate.[162] This forced “the economically desperate Tribe to return to the bargaining table,” and ultimately to accept an offer far below what the lease adjustment would have been: The rate slipped from 20% to 12.5%.[163]

In 2003, the U.S. Supreme Court held in United States v. Navajo Nation (Navajo Nation I) that the Indian Mineral Leasing Act of 1938[164] did not provide the necessary grounds for monetary damages under the Indian Tucker Act.[165] On remand, the United States Court of Appeals for the Federal Circuit found a breach of trust based upon the federal role created by a web of applicable statutes.[166] In 2009, the Supreme Court again heard arguments on the case and, as could be predicted from the oral argument, decided to once again absolve the United States of financial responsibility for breach of trust.[167] After disparagingly introducing the plaintiff as “the  Indian Tribe known as the Navajo Nation,”[168] Justice Scalia made sure that this time the court of appeals would not find an alternative ground upon which to find the United States liable by declaring that the “case is at an end.”[169] Little solace could be found in Justice Souter’s weak—one paragraph—cry in concurrence that he was “not through regretting” that his position “did not carry the day” in Navajo Nation I.[170]

But regardless of the Supreme Court’s holdings in 2003 and 2009, Justice Souter’s dissent in Navajo Nation I identifies the exploitative aspects of the government’s collusion with Peabody: “The purpose and predictable effect of these actions was to induce the Tribe to take a deep discount in the royalty rate in the face of what the Tribe feared would otherwise be prolonged revenue loss and uncertainty.”[171] Professor Royster rightly labels this an “egregious case,” yet the Supreme Court twice immunized the U.S. government for the “overt breach of a common-law trustee’s duties.”[172] Thus, despite the coal being worth far more than the agreed-upon rate according to United States’s own experts,[173] Peabody and the United States together used the tribe’s dependant position and lack of information to push through and approve a lease amendment known to be exploitative.[174]

Getting a fair price for coal would be a challenge for the Navajo Nation even in the absence of the federal policies or practices—from subsidized public land to trust violations—of the last fifty years that have favored mining companies.[175] Navajo coal is valuable coal. Changes in federal law in 1969 to 1970 that limited the desirability and utility of high-sulfur coal typical of Appalachia or the East helped make Navajo low-sulfur coal more desirable to the energy industry.[176] Environmental regulations thus favor western coal, which “averages less than one percent sulfur by weight compared to five percent for Illinois coal,” making it “less of a pollutant when burned.”[177] Moreover, strip mining enjoys technological advantages over shaft mining that allow greater efficiency in extraction.[178] Balancing out these advantages were severe constraints on tribal leaders. Economic development through natural resource development will be discussed in more detail later in this Article, but suffice it to say that the possibility that mining might relieve some of the poverty on the reservation undercuts the tribe’s position in negotiations.[179] Tribal leaders are in a bad position to hold out too long since mining royalties are a critical source of funding for Navajo government administration and social services.[180] In his study of the Navajo economy, Professor Michael Joseph Francisconi likens the tribe’s reliance on money from mining royalties to “self cannibalization.”[181]

While a generalization, it is fair to say that mining companies have had “easy access” to Indian coal, and the U.S. government has encouraged mineral leasing by tribes.[182] The shenanigans—really the wrongful actions of the federal government and Peabody Coal—surrounding the Navajo Nation’s renegotiations of the royalty rate in the mid-80s suggests that Peter MacDonald was being optimistic when, in 1976, he used the past tense regarding the nature of exploitation of Navajo natural resources: “Until quite recently, mineral development on Indian lands was by industry with the assistance of the federal government. Industry selected the area to be developed and the federal government dictated the terms, conditions and procedures of the proposed development. This arrangement left the Indians with little or no control.”[183] Though Navajo coal is “a highly demanded, limited, and exhaustible resource,” to date the Navajo Nation has at best exercised partial control over the exploitation of coal on the reservation.[184]

III. Romanticism and Tribal Choice

Natural resource exploitation on reservations is antithetical to the stereotype of Indians as environmental stewards. With the publication, in print and as a public service television commercial in 1971 to 1972 of a stoic Indian crying because of pollution, “Indian and environmental concern became synonymous, and public discussion turned to whether America might somehow tap native wisdom in solving the environmental problems facing Mother Earth.”[185] The notion that Indians are by definition also environmentalists pervades popular culture and is thought by many academics to have explanatory power when considering reservation development.[186] This mental shortcut raises the challenge of any other stereotype—namely that although the romantic notion of tribes as environmental stewards does not hold for all tribes or for all points in time, the stereotype nevertheless is grounded on some element of truth.[187]

Professor Frank Pommersheim’s aptly titled The Reservation as Place illustrates the challenge of simultaneously accepting and rejecting the stereotypes of Indians as environmentalists.[188] In it, Professor Pommersheim first unequivocally states, “Land is inherent to Indian people; they often cannot conceive of life without it. They are part of it and it is part of them; it is their Mother. Nor is this just a romantic commonplace.”[189] But, after saying that the relationship that many have with reservation land has changed, Pommersheim cautions against the “disturbing utopic visions that endlessly romanticize the people and the land.”[190] Similarly, Armstrong Wiggins, a lawyer with the Indian Law Resource Center, argues that “sustainable development is part of the cultural and religious heritage of most Indian peoples,” but adds that it is “a mistake, however, to take too romantic a view.”[191] Professor Robert Laurence goes further, arguing that “romanticizing ‘Indianness’ can come very close to condescension and insult.”[192]

What is the stereotype? Born out of the idea that Indians are somehow different and less civilized, the stereotype is at once a description of Indians and also, by contrast, of non-Indians. In the early 1970s, Indians were popularly thought of “as the continent’s first conservationists.”[193] The romantic conception of Indians preceded the birth of the environmental movement; as early as the 1830s Indians were thought of romantically as “children of Nature,” unburdened by the troubles of civilized society.[194] In American Indians & National Parks, Robert H. Keller and Michael F. Turek provide a nice summary of the stereotype, namely that “Indians had always lived in harmony with nature, revered Mother Earth as sacred, and offered a special wisdom to non-Indians.”[195] More subtle versions of the stereotype assume, for example, that Indians will necessarily reach better decisions than non‑Indians or always favor preserving the environment over economic development.[196]

There is some truth to the stereotype. As Donald Fixico observes, “the ‘Mother Earth’ concept is one of the few universal concepts among American Indians.”[197] The “Indian ‘heritage’ of ‘environmental sensitivity’” positively has facilitated tribal takeover of environmental protection responsibilities, while also legitimizing arguably racist U.S. environmental policies.[198] Simply rejecting the stereotype risks ignoring the truths it contains. Professor Rebecca Tsosie argues that “[t]he cultural connections between Native peoples and the land” should not be dismissed “as a ‘romanticized’ notion that is of limited utility in a modern era.”[199] And studies confirming or making note of the central place of nature and land in Indian belief and value systems are ubiquitous.[200] What is required is to reject the stereotypes and the “environmental myths” surrounding Indians without “suppressing their historical associations with the land.”[201]

Given that the stereotype on its face seems a positive one, why must it be rejected? The answer is that the stereotype is too readily accepted as truth both when it is deployed to explain environmentally protective decisions and when it is used to block a tribe’s decision to participate in or cause environmental harms. The stereotype confines Indians to an ahistorical moment and potentially deprives tribes of their sovereignty. It is ahistorical because, while it is surely true that some tribes balanced concerns for the environment with economic development differently than non‑Indians, it is impossible to reduce the history of every, or even any, tribe so neatly in this way.[202] It is also ahistorical because in order to accept the stereotype, the pretension that Indian societies are static and have not always changed with time must also be accepted.[203] The stereotype is “dehumanizing” and “masks cultural diversity.”[204] It operates independent of reality, such that a “romantic conception of what ‘Indians’ should be is frequently inconsistent with what ‘Indians’ actually are today.”[205] The  stereotype of Indians as nature’s protectors should be corrected, according to Professors Robert Cooter and Wolfgang Fikentscher, because it is “misleading.”[206]

With regard to development, “misleading” is an understatement. The stereotype is not neutral with regard to the tradeoffs between the   environment and industry; as a consequence, the construction “Indian = environmentalist” lends itself to manipulation.[207] Those who want to derail particular environmentally destructive development on reservations embrace the stereotype and claim that what is being proposed is not keeping with tribal values.[208] It is worth quoting at length Nancy B. Collins and Andrea Hall’s powerful rejection of such use of the stereotype in their article, Nuclear Waste in Indian Country:

Environmentalists, in pursuit of “Indian’s best interests” may engage in stereotypical thinking, characterized by romanticism, which effectively deprives Native Americans of the right to make their own decisions about accepting waste on their lands. It is important to break down this malignant romanticism into its major component stereotypes so that we recognize them and strip them from our law and policy. Some of these stereotypes include viewing “real Indians” as historical, primitive, unsophisticated, and rapidly on their way to extinction; essentializing the hundreds of Indian tribes into one group; assigning Indians the role of guardian of our environment as well as theirs; failing to recognize Native American tribes as modern, twentieth century sovereign nations within the United States; and viewing Indians as dependent and in need of our protection and guidance.[209]

Though Collins and Hall focus on tribal acceptance of waste products, the above critique holds for other tribally accepted and environmentally destructive choices. The challenge such choices present is that they do not necessarily fit within the Indian as victim paradigm. Separating good from bad and right from wrong is easy when tribes are suffering from the policies or practices of non-Indians, without tribal involvement, that reflect environmental racism or environmental injustice.[210] It is much harder to know if environmental racism or injustice is involved when a tribe itself makes “an affirmative and informed decision to undertake an environmentally controversial project.”[211] But the full meaning of sovereignty is such that it cannot be the case that tribal choices depend on “satisfying the emotional needs of a romantic tradition.”[212]

A. Environmental Justice

The environmental justice movement provides some perspective on how harms suffered by and caused by tribes should be viewed.[213] Reports documenting the disproportionate environmental risks suffered by minority groups as a result of siting choices that concentrated industry, waste, and other harmful activities in minority communities led to recognition of environmental justice issues.[214] With race, for example, being “the most important variable associated with the siting of hazardous waste facilities nationwide,” there was a need to address the problem.[215] In 1991, at the First National People of Color Environmental Leadership Summit, a broad concept of social justice that recognized “both public health and economic opportunity as indispensible aspects of the quality of life” emerged.[216] Those at the summit concluded that “people should not be faced with choosing between an unsafe livelihood and unemployment.”[217] In 1994, President Clinton put the imprimatur of the President on the movement when he signed Executive Order 12,898, which required federal agencies to “make achieving environmental justice” part of their mission.[218]

The primary focus of the environmental justice movement has been to ensure that disadvantaged populations, whether defined along racial or socioeconomic lines, are not “shouldering an unequal share of the burdens of hazardous waste” and other harmful activities.[219] The term “environmental racism” conjures up images of whites deliberately targeting minority communities, but siting decisions can have a disparate impact even where overt racism is hard to identify or prove.[220] Though one may not find a Bull Connor equivalent in the site decisions of environmentally harmful activities, “[w]ell-meaning environmentalists and worried citizens of affluent communities” opposed to facilities in their communities may have a similar effect: the concentration of harmful activities in minority communities.[221] Lack of political power and limited ability to effectively participate in decision making may explain in part disadvantaged populations’ excess exposure to nearby hazardous facilities.[222] Cheap land can play a role, as can the hope among members of the affected community that any new facility would also mean new job opportunities.[223] Ultimately, as Professor Alice Kaswan argues, “unequal distributions are of concern regardless of whether they were determined by discriminatory processes or ostensibly neutral market factors.”[224]

Wholesale application of the environmental justice paradigm when considering Indian experiences, even if capturing tribal distributional burdens, fails to take sovereignty into account. Scholars often describe the history, including recent history, of Indian-white relations as one characterized by “exploitation of Indian people and their lands.”[225] Such a history would seem to lend itself to an environmental justice approach. Indeed, the New York Times ad against Black Mesa coal mining discussed earlier and critiques of the targeting of Indian reservations by the hazardous waste industry both seem in line with this justice-centered approach.[226] But Indian environmental issues often receive only passing asides in articles on environmental justice[227] and, by treating Indians as equivalent to any other minority group when looking at environmental racism, their unique sovereign rights are largely ignored.[228] The marginal place of Indians in the environmental movement generally[229] thus far has largely carried over to the environmental justice approach.[230] As Professor Robert A. Williams, Jr. explains, “Indian values and belief systems are not reflected in or accepted by our environmental law. . . . [I]n Indian visions of environmental justice, all land is sacred, but that does not mean that tribal lands should never be used by the people.”[231]

Environmental paternalism might be appropriate—and has been called for—when distributional justice is taken to be the sum total of environmental justice. Accepting the need for environmental paternalism requires that the group being “protected” be seen as unable to protect themselves.[232] Only when it is accepted that tribes are doing something “wrong” when they decide to prioritize economic growth, or that tribes are powerless to resist the interest of harmful industries, can a case for paternalism be made.[233] Consider for example the following quotes from two leading scholars:

Examples of outsiders to be opposed might be the corporate disposers of nuclear and other toxic waste who want to dump in South Dakota and Indian country . . . .[234]

Unfortunately, the cultural meaning of Mother Earth to many tribes becomes less important as their people seek sufficient education, well-paying jobs, modern health services, updated housing, and adequate food supplies.[235]

The first quote assumes that Indian tribes should never agree to accept nuclear or toxic waste in return for payments that would alleviate reservation poverty. There is nothing wrong with that position, but its paternalism is self-evident.[236] The same is true of the second quote: The word “unfortunately” only makes sense if well-paying jobs and adequate food supplies are not thought of as rightly being significant enough to alter the cultural meaning of Mother Earth.

Avoiding environmental paternalism requires expanding the understanding of environmental justice to include respect for sovereignty when it comes to Indians.[237] And, according to Professor Williams, environmentalists find it “difficult” to deal with tribal governments who are willing to entertain environmentally harmful siting proposals.[238] Yet there is some agreement among scholars and government officials that “addressing environmental justice in Indian country require[s] creative solutions utilizing tribes’ governmental status.”[239] Once tribal sovereignty is acknowledged to play a role in environmental justice, things get a lot more complicated: Indians must be distinguished from all other disadvantaged groups facing environmental injustice,[240] Indian rights to self-(re)definition must be respected,[241] and arguably Indian environmental perspectives should be incorporated to a greater extent into general environmental law.[242] This is not to suggest that the tensions between environmental justice as distributional justice and a broader understanding of environmental justice simply disappear. In the preface to his book on environmental justice in Indian country, Professor James Grijalva writes that “[o]ne of the main premises of this book is that tribes’ absence from the national dialogue and implementation of federal environmental programs is largely responsible for creating environmental injustice in Indian country, the concept that some minority communities suffer disproportionately higher environmental risks than many white communities.”[243] Professor Grijalva’s premise challenges tribal and environmental advocates because it asserts that tribes should play an expanded role while seeming to accept that results should be judged based on whether Indians bear a disproportionate burden. It is the potential conflict between distributional justice and sovereignty-informed environmental justice that animates tribally embraced projects or harms.

B. Contracts of Adhesion and Tribal Lands

Should tribal contracts or lease agreements with environmentally harmful industries be considered contracts of adhesion, as is true of Indian treaties? Or when a tribe decides to accept a payment, whether in the form of royalties, taxes, or jobs, in return for suffering environmental harm, does it do so “freely” and out of its own powers of self-determination? On the one hand, without having an adequate amount of freedom to walk away from environmentally harmful projects, the “choice” to accept such projects is arguably merely the illusion of choice, and the formal acceptance through contract hides the true tribal position. On the other hand, the presence of constraints or tribal needs alone preceding contract approval should not automatically taint all such agreements as adhesional.

Treaties between Indians and the United States have been likened to contracts of adhesion and have been interpreted in that way by the Supreme Court.[244] Recognizing the “power disparity” between Indians and the U.S. government in drafting treaties, the Court, starting with Chief Justice John Marshall, has consistently viewed treaties as “agreement[s] in which the negotiation process had not been one of arm’s-length bargaining between equal adversaries.”[245] In order to partially offset the adhesional aspects of the treaty negotiation process, the Court created a set of rules, or “canons of construction,” liberally favoring Indians, to be used when interpreting treaty ambiguities.[246] Importantly, the canons of construction inform treaty interpretation, but they do not invalidate treaty terms—whatever the failings or imbalances in the negotiations, the treaties are still valid instruments.[247] The United States stopped making treaties with Indians in 1871, and since then what used to be accomplished through treaty has been in part accomplished by agreement and contract between Indian tribes and
non-Indian governments.[248]

Power disparities between Indians and non-Indian interests did not go away with the end of treaty making; what changed was the form of the relationship and, to some degree, the contracting parties. The contracts of adhesion interpretative lens used for treaties fits imperfectly with contracts for environmentally hazardous or destructive activities—whether for the storage of nuclear waste or the mining of coal—between tribes and companies or between tribes and non-Indian governments. Dramatic proof that formal contracts are little more than adhesion contracts can be seen in  a  1948 Associated Press photograph.[249] The “photograph captured Fort Berthold Chairman George Gillette weeping as Interior Secretary
J.A. Krug signed the contract to acquire land that was home to 80% of the reservation’s population to build a reservoir.”[250] The resulting dam had “devastating effects” on the tribes affected and “almost totally destroyed” their way of life.[251] This was accomplished by a government-to-government contract and not by a treaty; yet, unequal bargaining positions make this supposed agreement akin to an adhesion contract.

Some of the commentary on reservation mineral leases blurs the line between non-Indian governments and non-Indian corporate interests, between power and economics, treating them alike as powers that disadvantaged tribes are forced to accept. Professor Donald Fixico’s thesis in The Invasion of Indian Country in the Twentieth Century is that the continued exploitation of tribal natural resources by American capitalism has forced Indian leaders “to adopt modern corporate strategies to ensure the survival of their nations and people.”[252] Similarly, Nancy Collins and Andrea Hall write, “[T]he federal government may force tribes, by the power of law or economics, to accept nuclear waste.”[253] According to this perspective, the subordinate position of tribes forces acceptance of environmental costs in return for compensation. Compensation, while it may “ameliorat[e] the unfair consequences of siting,” also “can be seen as deliberately exploiting the special status of these land-rich, economically poor, and isolated sovereigns in order to secure a dumping ground where the community is in a poor position to object to the infusion of economic incentives.”[254] Viewed this way, businesses with undesirable characteristics have the incentive to seek out “vulnerable” communities—whether Indian or with other disadvantaged groups—that have little choice but to accept payments for environmental harms.[255]

The problem with this perspective is that it denies the agency of affected communities and tribes by falsely equating economic need with deterministic outcomes. Considering the probusiness orientation of the U.S. government and its failures to live up to its trust duty to tribes, it may be fair to blur the line between government and corporate contracts with Indian nations.[256] But simply because a community is hurting economically does not mean that when it agrees to allow harmful projects it does so “unwillingly,” as one commentator has suggested.[257] Why is this important? Large multinational corporations bring to negotiations not only their own resources but knowledge of the tribal position. Tribal governments are heavily dependent upon both royalty receipts and U.S. government assistance.[258] For the Navajo Nation, “[c]hronic unemployment and an extremely low per capita income level . . . would seem to make the people of this area receptive to any form of industrialization, including mining.”[259] Companies engaged in harm-causing activities thus enter into negotiations from a position of strength, but acknowledging that economic conditions may favor accepting compensation for environmental harms does not mean that tribes are powerless to resist corporate interests or that they will never reject harm-causing proposals.[260] As Navajo Nation President Joe Shirley, Jr. explains, “The Navajo Nation is part of the modern economy. We do not oppose creating jobs, but there are lines we will not cross in order to make  money.”[261]

Elsewhere I have argued that the United States bears some responsibility for establishing the conditions in which tribes operate and which contribute to tribal acceptance of harm-causing contracts such as those with extractive industrial interests.[262] The bureaucratic management of tribal land that I highlighted there is just one aspect of a larger program of separating Indians from their land and resources.[263] The conflict between Indians and non-Indians has been seen by some scholars as fundamentally about control over resources and land, not about cultural conflict.[264] While  land is no longer simply taken, there has developed “a system of routine economic supervision, purportedly protective, that favors certain patterns of resource exploitation.”[265] Managing reservation land as if it were public land, the United States discouraged some forms of investment and encouraged others.[266] As Professor Robert L. Bee argues, “[p]olicy ad‑hoccery” may itself lead to “exploitation of Indian resources,” even if the intent of U.S. government agencies was entirely for the good of tribes rather than responding to corporate interests.[267] But regardless of motivation, the United States “encouraged industry to exploit Indian country’s wealth of natural resources,” even where not supported by tribes or tribal members.[268]

To illustrate the tremendous impact of federal resource management, it  is worth exploring both the tribal effort to block further development of the San Francisco Peaks and the imposition of mandatory livestock reduction by Washington in the 1930s. Though somewhat removed from the U.S. government’s encouragement of leasing for natural resource extraction, the two controversies illustrate the importance of tribal control over tribal resources. They also have had and will continue to have an impact on the forms of economic opportunities available to the Navajo Nation and to tribal members.

1. San Francisco Peaks

The tension between Indian interests and industrial interests is currently playing out dramatically in the courts in a case involving the San Francisco Peaks, one of the traditional four sacred mountains of the Diné.[269] The Peaks have spiritual significance for many tribes, not just the Diné, but the land itself is off-reservation federal forest land.[270] The United States Forest Service granted a special use permit to a ski resort, and in 2002 Snowbowl Ski Area sought permission to expand the resort and to spray the ski areas with artificial snow.[271] Even before the Forest Service approved the project, tribes for whom the Peaks are sacred objected, claiming that their religious rights were being violated.[272] To produce the artificial snow, the resort was going to spray up to 1.5 million gallons of treated sewage water a day onto the mountain as snow.[273] The Ninth Circuit highlighted the lower court’s findings that “highly variable snowfall” had resulted in operating losses for the owners of the ski resort[274] and that artificial snow was “needed to maintain the viability of the Snowbowl.”[275] For the tribes, this would be a form of desecration because it is quite literally the spraying of feces and dead bodies onto the sacred Peaks—feces because of the use of toilet wastewater, and dead bodies because of run-off from funeral parlors.[276] Such  treatment of a place of religious significance is, according to the plaintiffs, a substantial burden on the free exercise of religion and a violation of the Religious Freedom and Restoration Act of 1993 (RFRA).[277]

The Ninth Circuit ruled in favor of the Forest Service and Snowbowl, characterizing the claim as being based upon “diminishment of spiritual fulfillment,” which it held did not amount to a substantial burden.[278] The appeals court majority focused on the relatively small amount of land impacted—one percent of the Peaks—by the ski area and applied a restrictive reading of RFRA’s requirements.[279] Additionally, the majority seemed to find comfort in Arizona’s classification of the treated sewage water that would be used as being of an A+ grade, the highest mark possible under state law, signaling that it is suitable for irrigation of school grounds and crops.[280] Not discussed by the majority is that Arizona’s approval of similar treated waste for school grounds places students playing sports in the unenviable position of having to choose whether or not to dive for the ball or to let it get away so as to avoid excessive contact with grass that when wet smells of human waste.[281] In dissent, Judge William Fletcher noted that the Forest Service’s environmental impact assessment failed “to discuss either the health risks resulting from ingestion of the treated sewage effluent or the likelihood that humans—either adults or children—will in fact ingest the artificial snow.”[282] Moreover, the current owner of the ski resort purchased it in 1992 “with full knowledge of weather conditions in northern Arizona.”[283] After an extended critique of the majority’s treatment of RFRA, Judge Fletcher ends the dissent by highlighting the irony of the court protecting everyone’s recreational interest in “‘public park land’” to justify “spraying treated sewage effluent on the holiest of the Indians’ holy mountains,” when that land was originally taken by force from Indians.[284] Despite the strength of the dissent[285]and the importance of the case to the tribes involved, the Supreme Court decided against hearing arguments on the matter.[286] Sewage effluent, after all, was not being sprayed on the National Cathedral or a Judeo-Christian sacred site.[287]

2. Livestock Reduction

Diné who were alive in the 1930s still remember with anger the forced stock reductions of that period.[288] Sheep play a defining role in Navajo life: Herd size and social position are correlated, extended family life revolves around sheep, and the inheritance of grazing rights from generation to generation is often hotly contested.[289] Miss Navajo Nation contestants butcher a sheep as part of the pageant, held during the Navajo Nation Fair.[290] Mutton stands operating out of small trailers or in fairgrounds are found in most towns, and the butchering of a sheep is a part of how many celebrate major events such as weddings or large gatherings.[291] If anything, Navajo sheep culture was even stronger in the 1930s. In The Navajo Indians, published in 1930, the authors write, “Men, women, and sheep—the three are inseparable in Navajo life.”[292] The majority of Diné owned sheep and, together with goats, they were the source of cash.[293] Social status was primarily determined by herd size, with the wealthy raising sheep for sale on  the market and the poor having subsistence-level holdings.[294] Sheep simultaneously provided Diné their food and their livelihoods, and after returning from Fort Sumner in 1868, sheep numbers rose such that before the turn of the century Navajos were described as wealthy and self‑supporting.[295]

Navajo livestock reduction was instituted in 1933 in an effort to deal with severe overgrazing.[296] Spearheaded by the Commissioner of Indian Affairs John Collier, the program found support in the Roosevelt administration’s embrace of a scientific approach to problems.[297] The Navajo Nation Council, recognizing that even if it objected “the government would carry out stock reduction anyway,” approved the program in the hope that after doing so the tribe would be granted additional reservation land.[298] The forced culling of Navajo herds affected all livestock, with the reservation’s carrying capacity calculated in sheep units; according to the Department of the Interior, the Diné had double the number of sheep units that the land would support (one million compared to 500,000).[299] Navajos were paid for the animals killed, but at below market rates.[300] As a consequence, force rather than consent was used: “Agents went to herds and often shot the animals before the eyes of astonished, grieving families.”[301] Some of the animals “were merely shot and left to rot,” a level of waste that Navajos “were incapable of understanding.”[302] Removal and incarceration awaited those Diné who resisted stock reduction.[303] The supposed scientific necessity of reducing overgrazing—a 1931 Department of the Interior study concluded that every jurisdiction of the Navajo reservation “had more animals than it could conceivably support”[304]—does not compensate for the colonialist nature of the program imposed upon the tribe by the federal government.[305] The Executive Committee of the Navajo Nation Council was even told of the possibility that troops would be called in by Commissioner of Indian Affairs John Collier.[306]

In part by design—the stock reductions were especially targeted to hit those with the largest herds in order to reduce reservation inequality—the stock reductions had dramatic effects on the Navajo economy and on the welfare of Diné families.[307] With their herds halved, for many families government welfare took the place of prior self-sufficiency and wealth.[308] Although arguably undertaken with good intentions—preventing the negative long-term effects of overgrazing—the program also owed its existence to the construction of the Hoover Dam, which experts feared would get clogged with silt and quickly become “useless” unless erosion from Navajo lands was stopped.[309] The Roosevelt Administration’s program of “stock reduction rivaled the Long Walk in its devastating consequences” on the Diné people and on the tribal economy.[310] Professor Robert McPherson explains,

The livestock reduction of the 1930s was one of two major tragedies in the Navajos’ tribal memory. The trauma of the first tragedy, the round up and incarceration of the people at Fort Sumner between 1864–68, has been passed down by word of mouth for generations, as a time of defeat, degradation, and removal at the hands of the white man. The destruction of livestock in the 1930s was, to the Navajo, an economic form of the same thing—defeat, degradation, and removal.[311]

For the Navajo Nation, livestock reduction increased poverty, demonstrated U.S. control over reservation life, and necessitated a move towards other forms of economic growth.[312]

Livestock reduction and the San Francisco Peaks dispute are but examples of the pervasive control that the United States has over Diné life. The Navajo Nation’s current inability to protect off-reservation sites that are sacred to the tribe reflects the same power dynamic as the forced livestock reductions of the 1930s. Legal scholars describe the power of the United States over tribes in terms of congressional “plenary power”—Congress’s (near) absolute authority over Indian sovereignty—and as these two Navajo experiences show, the power dynamic takes on different forms.[313] Livestock reduction and the Peaks dispute share in the shaping of Diné life and experiences by the federal government. Non-Indians perhaps cannot fully appreciate the cultural significance of the Peaks to tribal members, but the government’s taking of half of the livelihood of most families obviously would have a long-term impact on Diné economic opportunities and wealth.

The outcome of these episodes would have been quite different if the tribe had had meaningful control. Looking just at the Peaks controversy might lead one to focus on the off-reservation status of the sacred site. But, as livestock reduction shows, the on-reservation line is not always sufficient to ensure tribal control over natural resources, whether involving artificial snow, grazing rights, or mineral leases. Another historical moment is illustrative: At one point early in the development of oil leasing on the reservation, the council wanted to go into partnership with an oil company rather than simply sell their oil.[314] The tribe was to put up the land and share in the expenses and profits: “It was a gamble the Tribe was willing to take in the hope of generating more income with which to meet the demands of the Navajo people for a better life in their homeland.”[315] The Secretary of the Interior, however, thought it was too big a risk, and as trustee for the tribe he rejected the proposal.[316] Maybe it was too big a risk and maybe the reservation was suffering from overgrazing, but by dictating such matters, the federal government was also defining the terms of economic possibility for the tribe.

Returning now to coal leasing and the question of tribal acceptance, one might conclude that Navajo coal leases were not coerced. Morton writes, “[G]iven the state of the reservation economies and intra- and intertribal factionalism, the tribal councils had good reasons (from their points of view) to approve standard leases.”[317] Once the “state of the reservation economies” is seen not as a given, but as a result of governmental policy (such as livestock reduction), the rejection of coercion stands on less solid ground. Without “viable economic alternatives,” tribes will be more receptive to environmentally destructive activities,[318] and therefore, U.S. government policies that in the past prevented or presently prevent the development of alternatives should not be separated from the question of coercion or whether the contracts are adhesionary. It is impossible to identify the exact moment when the Navajo Nation escaped from being told what it had to do and from having little choice in what contracts it accepted. As the San Francisco Peaks dispute makes clear, the United States–Navajo Nation power differential has not disappeared. Despite this, it is my position that the Navajo Nation is now entering a period where decisions regarding natural resource exploitation should be treated as “belonging” to the tribe.

IV. Acceptance and Development

The city of San Diego had a problem, too much trash, and a solution, the Campo Band of Indians was willing to accept the trash. The Band, in partnership with Mid-American Waste Systems, Inc., wanted to open a large solid waste landfill on the remote reservation.[319] The tribe’s revenue from the twenty-eight million ton capacity landfill was estimated to be $1.6 million a year.[320] The United States Environmental Protection Agency (EPA) approved the landfill in 1995, but a year later the United States Court of Appeals for the District of Columbia reversed, holding that EPA did not have authority to issue the approval.[321]

The attorney for the tribe at the time was Kevin Gover, who would go on to become the Assistant Secretary of the Interior for Indian Affairs from 1997 to 2000, a law professor, and now the director of the Smithsonian’s National Museum of the American Indian.[322] A law review article by Jana Walker and Kevin Gover on the proposed landfill unapologetically supports the Campo Band.[323] They argue,

Under certain circumstances, a solid or hazardous waste disposal project is a viable and appropriate form of industrial development for some Indian tribes. Waste disposal projects are not only extremely profitable, but also require little up-front cash. Moreover, waste disposal projects can provide job opportunities to reduce significant involuntary tribal unemployment. The drawback is, of course, the potential environmental problems.[324]

Potential environmental problems are treated in both the above quote and in the article as being of secondary importance and as something with which only the Campo Band should concern itself.[325] Walker and Gover assert that reservation wealth and job creation should be important elements to consider regarding the viability of disposal projects.[326] Stuttering economic development provided the impetus for this form of growth,[327] and, according to Walker and Gover, writing in 1993, the proposal “instilled a sense of pride and purpose in the Indian community. . . . [T]he Band has changed from a pocket of poverty and hopelessness to a community of Indian people united by a determination to succeed.”[328] But the court decision in 1996 blocked the tribe from reaping the expected improvements in education, housing, economic self-sufficiency, and government facilities planned in connection with the landfill.[329]

Campo Band’s decision to convert part of the tribe’s reservation into a receptacle for San Diego’s trash powerfully illustrates the challenge of such a path towards economic development. It goes beyond the scope of this Article to go into the full details of the Campo Band’s proposed landfill controversy,[330] but at least according to Walker and Gover’s account, the Campo Band “[chose] this form of development” freely and knowingly.[331] As  a choice it is not entirely novel: Indian–non-Indian relations have historically been defined by exchanges of land for money or promises.[332] Given the poverty and economic development challenges of many tribes, the basic decision of the Campo Band—acceptance of environmental harm in return for financial reward—is likely to be repeated, with local variation, by other tribes.

Popular stereotypes of gaming tribes aside, most tribes are still struggling economically. “Despite abundant natural resources of land, timber, wildlife, and energy, Indian reservations remain among the most impoverished areas in the United States.”[333] The success of Foxwoods and Mohegan Sun, along with media coverage of the large per capita payments made by some tribes, obscure “the overall depressed state of Native American economic development.”[334] Reservation unemployment and underemployment has long been common.[335] For many reasons, some of which affect all tribes and some which differ across tribes, poverty is a fact of reservation life.[336] It is now unfair to say, as one author has, that “[t]he reservation economy is the welfare state,” but some reservations can seem that way, especially to outsiders.[337] And importantly, “Indians do not want to be poor anymore.”[338]

The economic and social payoff for tribes whose environmentally destructive projects go forward can be significant. Successful projects allow tribes to invest in things such as education and government services.[339] Additionally, tribes may need “a viable economic base” in order to defend their sovereignty before the U.S. government.[340] Recognizing that poverty can threaten tribal survival, tribal governments do not merely react to outside economic interests.[341] While Professor Fixico writes that growing natural resource demands “have forced tribal leaders into two arenas—economics and law,” such language fails to appreciate the motivating power of poverty.[342] Just like non-Indians, Indian tribes feel the conflict between protecting the environment and economic growth, but when they decide to pursue growth with some sacrifice, that choice should not be dismissed as “capitalistic greed.”[343] As Sam Deloria argues, “[W]e cannot help but create confusion in American society if we blame the system for Indian poverty and then denounce opportunities for Indians to get themselves out of poverty.”[344] Despite Professor Fixico’s concern about “economics and law,” most scholars talk about Indian poverty with little focus on economics.[345] Tribes  have begun improving their economic situation by pursuing opportunities created by “the resource problems of the industrialized, affluent societies” that surround them.[346] Partly this pursuit reflects limited options,[347] but success also reflects advantages that tribes have when pursuing such opportunities.[348]

The Navajo Nation is no different. In Red Capitalism: An Analysis of the Navajo Economy, written in 1973, Kent Gilbreath argued that Navajos do not want “to isolate themselves from the surrounding society,” but rather “Navajos hope that self-determination will free them to pursue in an individualistic manner their own economic improvement while maintaining their cultural values.”[349] The problem is that hope has not turned into reality. In a 1981 introduction focused on Navajo economic development, Al Henderson highlighted the role energy resource development could play in eliminating reservation poverty.[350] But the goal he articulated, “achieving substantial reductions in the social and economic disparities between the Navajo and the rest of the United States,” has not been achieved.[351] In 2004, the U.S. per capita income was $30,547 and the unemployment rate was 5.7%; the Navajo Nation’s per capita income was $7734, one-fourth that of the United States, and the Navajo Nation unemployment rate of 48% was more than eight times that of the United States.[352] Today the Navajo Nation is hoping that the Desert Rock power plant will help combat unemployment and reservation poverty.

A. Desert Rock

Navajo Nation President Joe Shirley, Jr. would like to see the Desert Rock power plant operational. Desert Rock would create 400 permanent jobs and “provide more than $50 million annually to the Navajo Nation.”[353] Additionally, during the first four year period of the $3.4 billion power plant,[354] more than 2800 workers are expected to put in the more than ten million hours of expected construction work.[355] According to Desert Rock Energy Company, the plant “will support local prosperity” through the relatively high salaries to be paid its employees.[356] Though described in terms of benefits from a power plant, the agreement between the Navajo Nation’s Diné Power Authority and finance partner Sithe Global is largely about coal.[357] The power plant would be built next to a coal mine, thus avoiding the transportation issues of the mines on Black Mesa.[358] Two hundred of the four hundred jobs would be at the mine,[359] not the plant, and over half the projected revenues “are a direct result of the use of Navajo coal.”[360]

The agreement with Sithe Global includes an option for the Navajo Nation to buy into the plant itself, though doing so would require either a high capital outlay or the dedication of a significant portion of the coal revenue.[361] Though the mine and associated mine-mouth coal-fired power plant are being developed simultaneously[362]—unless the Navajo Nation decides to purchase equity in the power plant itself—the partnership form merely obscures the fundamental similarity to earlier coal leases. The arrangement is in line with a 1955 recommendation of geologists favoring partnerships rather than leases.[363] In 1974, the U.S. Commission on Civil Rights recorded the belief “that 50-50 partnership arrangements with major firms . . . might help avoid some of the abuses of outside exploitation.”[364] More recently, Richard Burnette, former Director of the National Congress of American Indians, urged tribes to “joint venture” their natural resource development.[365]

The tremendous capital requirements of constructing a power plant work against the tribe being able to open a Desert Rock–equivalent power plant without outside backing, in this case from a New York hedge fund.[366] A 1994 survey of tribal leaders reported that ninety-six percent of respondents said their tribe lacked capital, the most commonly agreed upon obstacle to economic development.[367] The Navajo Nation is partnering with Sithe Global—in fact, the Navajo Nation sought out Sithe Global, rather than the other way around[368]—in part because the tribe is not in a financial position to develop its coal resources on its own.[369] For the mining and energy companies, partnering rather than just leasing has the advantage of protecting against the tribe imposing an excise tax after the royalty agreement is finalized.[370] By reducing the distance between a tribe’s regulatory and entrepreneurial sides through the partnership, Sithe Global aligned its development plans with the Navajo Nation’s economic goals.[371]

Local and global environmental harms accompany Desert Rock’s economic promise. For that reason, many national environmental groups oppose the project: Center for Biological Diversity, Environmental Defense Fund, National Parks Conservation Association, Natural Resources Defense Council, and the Sierra Club.[372] They are joined by local groups such as Conservation Voters of New Mexico, Grand Canyon Trust, New Mexico Conference of Churches, New Mexico Citizens Alliance for Responsible Energy and Sustainability, San Juan Citizens Alliance, and Western Resource Advocates.[373] And on the reservation, Diné Citizens Against Ruining our Environment (Diné CARE) and Doodá Desert Rock Power Plant Committee (Doodá Desert Rock) are united against Desert Rock.[374] Doodá Desert Rock even has created a “cause page” with over 1700 members as of April 2010 on Facebook.[375]

The Draft Environmental Impact Statement (DEIS) supports plant construction.[376] Prepared for BIA by URS Corporation, the DEIS largely downplays and hides Desert Rock’s harmful environmental effects while playing up the economic benefits of the plant.[377] Additionally, though there were public comment periods preceding and following publication of the DEIS, the document itself is written in such a way that it is a challenge to follow.[378] For example, under “Global Air Quality Impacts,” after discussing global warming, although the amount of carbon dioxide (CO2) plant emissions is acknowledged, the report’s coverage of this form of pollution is truncated.[379] According to the San Juan Citizens Alliance public comments regarding the DEIS, it “completely fails to consider the impacts of 12.7 million [tons per year] of CO2” on world resources and global warming.[380] Instead of such information, in the section on “Global Air Quality” the DEIS focuses on the plant’s “unique and innovative design” that would make it “more efficient, in terms of power output versus fuel combusted, than other coal-fired plants in the region.”[381] As the DEIS acknowledges, such efficiency gains merely reflect technological improvements that have occurred since the prior plants were built, but the DEIS seems to suggest that the improvements alone warrant construction of a new coal-fired power plant.[382]

Desert Rock’s local environmental impacts are more thoroughly—and probably less controversially—detailed in the DEIS. The proposed location of the power plant is on a remote piece of tribal trust land south of Shiprock and Farmington, New Mexico.[383] The plant itself would be on 592 acres of leased land, with a footprint of 149 acres.[384] Associated transmission lines, water wells, roads, and a coal preparation area require far more land: 4630 acres.[385] The power plant would also require ten to twenty new water wells to supply a whopping 2795 gallons per minute (gpm), though the plans, per an agreement between the Navajo Nation and plant developers, call for an additional water use of 275 gpm to provide for Navajo municipal demand.[386] Desert Rock also involves the development of a new coal strip mine, the “Navajo Mine Extension Project,” on existing mineral leased areas.[387] North  of the proposal extension lies Navajo Mine, an area leased since the 1960s that provides 8.5 million tons of coal per year to the Four Corners Power Plant.[388] The Navajo Mine Extension Project would provide Desert Rock with 6.25 million tons of coal per year every year for fifty years—the design life of the plant.[389] Strip mining, which entails first removing all vegetation, will create localized dust clouds and will also leave a scar that the mining company would be required to reclaim.[390] But for the life of Desert Rock, and quite possibly longer, the mine itself would add to the impact of the plant.[391]

While power plant opposition groups like to call attention to the few Diné families who will be directly affected by the plant, the site selected is rural and sparsely populated even by reservation standards.[392] According to the DEIS, the majority of the “area is characterized as occasional low intensity livestock grazing and scattered dwellings, with primitive roads traversing the land.”[393] At times the description of the affected land in the DEIS, such as with “primitive roads” above, reflects the cultural, ethnocentric bias in favor of development that has long been used to dispose Indians of their land.[394] When discussing the existing land uses near a proposed water well, the authors of the DEIS seem unaware of the irony and assumptions that underlie the following: “The vacant and undeveloped land within the proposed water well field is permitted for livestock grazing with water tanks and corrals dispersed throughout.”[395]

 

 


Figure 1

 

 

How does such development affect the plant’s immediate surroundings? The physical structures, smoke emissions from the plant, and the 135 feet tall transmission towers would be eyesores, a form of visual pollution on the high  desert landscape (see Figure 1).[396] Dislocation of some families and reduction of some grazing areas is anticipated as well; the DEIS identifies one residence within a half mile of the plant and 148 residences within a half mile of proposed transmission lines, water wells, and access roads.[397] Finally, although the initial Prevention of Significant Deterioration (PSD) permit application submitted to EPA suggests that any increase in regional haze will likely have other natural causes, plant proponents had to acknowledge in their application that regional haze could increase.[398] For locals already familiar with haze from the area’s existing power plants, this impact was known and a source of anger, inflamed by a Durango Herald report that “Colleen McKaughan, an air-quality expert with the federal Environmental Protection Agency’s Region 9, said the Four Corners region has air so clean that it can absorb additional pollutants without harm.”[399]

Believing that the DEIS reflected bias and perhaps too close a relationship between URS Corporation, which prepared the DEIS, and Sithe Global, Diné CARE and the San Juan Citizens Alliance initiated a Freedom of Information Act[400] claim against BIA.[401] Represented by attorneys from the Western Environmental Law Center and the Energy Mineral Law Center in the Four Corners region, the complaint calls attention to the limited role that BIA had in preparing the DEIS and seeks records of contacts between URS and plant proponents.[402] San Juan Citizens Alliance’s position is that the use of URS to prepare the DEIS for BIA “has resulted in a predetermined conclusion” supporting Desert Rock.[403] In their response to the DEIS, they seek a review of the “‘third party preparation’” of the DEIS to “determine if URS Corporation and BIA were unduly influenced by Sithe.”[404] Certainly Diné Power Authority and Sithe Global could not have hoped for a more supportive review of the plant’s environmental impact.

In the waning days of the Bush Administration, EPA approved of Desert Rock—more precisely, it issued Desert Rock a permit to pollute—but the Obama Administration EPA quickly pulled the approval in order to allow itself to “reconsider its actions on several issues” related to Desert Rock.[405] Diné Power Authority (DPA) and Sithe Global seemed to have reached their goal when EPA issued a PSD permit on July 31, 2008.[406] As Desert Rock Energy Project noted, the PSD Permit “is the key permit among several regulatory approvals” needed for the development of the power plant.[407] Having been sued by Navajo Nation and Sithe Global for failure to act on the PSD application, the permit was issued in accordance with the consent decree that set July 31st as the deadline for EPA to issue a final permit decision.[408] The press release on the issuance of the PSD permit quoted Wayne Nastri, EPA Regional Administrator for Region IX, which includes the Navajo Nation, as saying, “The Desert Rock power plant will be one of the cleanest pulverized coal-burning power plants in the country.”[409] When the Obama Administration reversed its PSD permitting approval with its motion for voluntary remand, Desert Rock Energy company, of course, was not happy with the remand decision.[410] But for environmentalists, the voluntary remand signaled that EPA was beginning to “address legal and scientific concerns they contend were overlooked by the Bush [A]dministration.”[411] Irony was lost on EPA, which effectively put a roadblock in front of the Navajo Nation’s hoped-for power plant with the remand filing on the same day as the Navajo Nation’s “Sovereignty Day,” created in celebration of the Supreme Court’s recognition of the tribe’s right to tax energy companies.[412]

The Navajo Nation leadership is “staunchly” supportive of Desert Rock.[413] At the beginning of the project in 2004, President Shirley wrote to EPA, expressing the Navajo Nation’s excitement about the project’s progress.[414] In 2005, President Shirley again wrote the EPA: “I am writing you to confirm in the strongest possible terms that the Navajo Nation supports the efforts of DPA and Sithe Global Power LLC . . . and needs your dedicated assistance to conclude air permitting activities for the Desert Rock power plant in the very near future.”[415] Shirley, citing reservation poverty and unemployment statistics, called on EPA to quickly issue the PSD permit.[416] The letter also called attention to the forced out-migration of Navajos unable to find work on the reservation, a point that President Shirley would return to in subsequent State of the Navajo Nation addresses.[417] Two years later, when Shirley was still pushing EPA to issue a final PSD permit, he noted that Desert Rock would provide a third of the Navajo Nation government’s annual budget and would replace revenues lost with the closing of other plants and mines.[418] The letter concluded by quoting Senator John McCain:

Each of us shares a strong commitment to promote and defend tribal sovereignty, tribal self-governance, and tribal self-sufficiency. But my friends, these things we hold dear, will wither and die unless they are watered by a strong Reservation economy that produces a decent standard of living for all of our people. Unfortunately, as you well know, economic development success stories in Indian Country are still the exception and not the rule.[419]

The working relationship between the Navajo Nation and EPA was obviously strained by this point—President Shirley was no longer excited about the progress that had been made—and the lost revenue was impacting the tribal budget.[420]

The strongest statement of the Navajo Nation’s support for Desert Rock is President Shirley’s January 2008 explanation of why the Navajo Nation decided to sue EPA for failure to act on the PSD permit application.[421] The decision to bring suit reflected Shirley’s frustration that EPA had not approved “the cleanest coal-fired power plant in the United States” despite the “stringent emission standards imposed” by EPA on the project.[422] The statutory requirement was that EPA act upon a complete application within one year, but the Desert Rock application had been pending for almost three years by the time of President Shirley’s explanation.[423] In calculated language, President Shirley wrote:

EPA’s unlawful delay and its failure to issue the final PSD permit are inhibiting the growth and independence of the Navajo Nation, the largest sovereign Indian Nation in the United States. Today, we see prosperity, growth and development all around us, but not within our own borders. Every highway leading off the Nation leads to a flourishing economy, and every highway leading onto the Nation leads to economic silence. Once construction begins (which cannot start until EPA acts on the PSD permit), Desert Rock will be the largest economic development project in Indian Country in the United States.[424]

The letter continued by driving home the fact that the Navajo Nation Council—which voted sixty-six to seven in favor of the project’s lease—stood with President Shirley in supporting Desert Rock.[425]

Navajo government enthusiasm for Desert Rock is not shared by all. New Mexico Governor and 2008 Presidential Candidate Bill Richardson issued a statement in 2007 that said that he was “gravely concerned about the potential environmental impacts” of Desert Rock, adding that he believed the plant “would be a step in the wrong direction.”[426] Richardson argued that the plant, which would raise the state’s total CO2 emissions fifteen percent, would make his “aggressive greenhouse gas reduction goals difficult—if not impossible—to meet.”[427] And a little over a month before EPA issued the PSD permit, Governor Richardson and his attorney general wrote EPA with “serious concerns about the environmental impacts of constructing Desert Rock in a region already impaired by other large coal‑fired power plants.”[428] The concerns of the New Mexico Governor’s office were also shared by county and city governments in New Mexico and in other states.[429]

The Doodá Desert Rock Power Plant Committee spearheaded local opposition.[430] According to Doodá Desert Rock President Elouise Brown, “Doodá means ‘absolutely no!’ in Diné,” as in Absolutely No Desert Rock.[431] One thousand five hundred Four Corners residents signed a Doodá Desert Rock petition opposing Desert Rock that was submitted to the BIA Navajo Regional Office.[432] Doodá Desert Rock’s focus was on the interests of “the most impacted people [who] still reside within close proximity of the proposed power plant site.”[433] Powerful images of the faces and lives of those who would be displaced and those who would be most affected by the plant were captured by photographer Carlin Tapp, invited to take the photos by Doodá Desert Rock that were later exhibited in Santa Fe.[434] In December 2006, protestors prevented surveyors from accessing the proposed site by blocking trucks and later occupying the site.[435] Plant developers obtained a temporary restraining order against the occupiers, but the parties agreed to coexist so long as the site work was allowed to go forward.[436] A permanent “resistance camp” was built on January 20, 2007, on the land of Alice Gilmore,[437] and “day after day” the protestors—Diné and “a coalition of religious and environmental organizations”—“‘[sat] vigil’” near the plant site.[438] By July 2007, the vigil was down to “[a] handful of people, mostly Navajo women.”[439] But the outrage at the issuance of the PSD permit became celebration when the permit was revoked.[440] In February 2009, following EPA’s decision to voluntarily remand the permit, Doodá Desert Rock President Elouise Brown triumphantly asserted, “[T]he Desert Rock power plant is dead!”[441]

The challenge of Desert Rock opposition was expressed during a Desert Rock public hearing by a resident of Fort Wingate, New Mexico, who noted that the Navajo are divided on Desert Rock.[442] A less than sympathetic news article in the Albuquerque Journal was dismissive of local opposition: “[E]ven on this desert plot, where the nearest neighbors are cattle, sheep and raptors—and where the power plant is a guest of the Navajo tribe—the not-in-my-backyard syndrome has taken hold.”[443] Locals directly impacted by a particular development—here, a power plant—are more likely to object, whether the proposal is located on the Navajo Nation or is in Delaware.[444] Those in the immediate area would not like to “see” the plant developed, but as Diné Power Authority argued, “Much of the money can be expected to go toward existing social and health programs for the Navajo people, not just in the chapters surrounding the plant, but across the Navajo reservation.”[445] Consequently, local positions may not align fully with the rest of the tribe.

Focusing just on local opposition risks devaluing the challenges that “competing demands of conservation and development” force upon tribal governments.[446] The Navajo Nation can decide to protect some areas more than others without necessarily being blind to environmental concerns. Thus, the Navajo Nation, which “became the first American Indian tribe to authorize their own park system” in order “[t]o protect special places,”[447] can also choose places not to protect. In the San Francisco Peaks case, the Ninth  Circuit wrote, “The Navajo believe their role on earth is to take care of the land.”[448] But taking care of the land does not mean the power plant opponents are automatically in the right: “[E]ven though all land is sacred, a specific area may be considered as having less sacred value and development may be pursued on it.”[449] It may be that like Black Mesa, the proposed Desert Rock site is far enough from tribal power centers that Navajo Nation leaders believe it appropriate for such harmful development.[450]

Ultimately, Desert Rock detractors, both Navajos and non-Indians, must confront the Navajo Nation’s democratically elected leaders who seem to think that the project is in the best interests of the tribe as a whole. President Shirley’s reelection occurred in November 2006, well after public hearings and debate about Desert Rock began.[451] Navajos had not reelected an incumbent President in twenty-eight years, something of which President Shirley is very proud.[452] Similarly, an equally supportive council was not voted out of office, though Desert Rock opponents accuse them of “not listening to the people.”[453] These results would not be predicted by those myopically paying attention only to the “overwhelming opposition to the project by tribal members in the area,” but might if the entire tribe is considered.[454]

The subordinate relationship of the Navajo Nation relative to the U.S. government, operational here in the requirement that the plant is subject to EPA review,[455] puts Desert Rock opponents into an awkward position. With the tribal government firmly behind the plant, opposition groups, both local and national, end up hoping that EPA will act against the interests of the Navajo Nation’s government.[456] National environmental organizations seeking to derail Desert Rock largely avoided the issue of sovereignty in their responses, confining the discussion to technical critiques of the proposal and EPA actions.[457] Doing so obscures the choice made by such organizations to accept the appropriateness of the subordinate tribal position and to disregard the tribe’s democratic decision-making process when the results are not in line with the priorities of these organizations.[458]

Perhaps more tragically, Diné opposed to Desert Rock end up turning to an arm of the U.S. government when they do not accept the path of their own tribal government. After criticizing Desert Rock, an e-mailed public comment to EPA pleaded, “Our leaders in the Navajo Nation government do not seem to listen to our cry for help. Please help our people!”[459] EPA, however, is an imperfect place to turn to, for its role is inherently limited:

EPA acknowledges that there are supporters and opponents of this proposed project. EPA does not have a position on whether the [Desert Rock Energy Facility] is an appropriate land-use or public policy choice for the Navajo Nation, as the scope of our PSD permitting process is limited to evaluating compliance with PSD permitting requirements.[460]

Rather than focusing, as one participant whose comments at a public hearing were entirely in the Diné language, on “how we, as Navajo people, . . . allow our tribal government to exercise its sovereignty,” limited tribal sovereignty externalizes the debate.[461] After criticizing the tribal government, Navajos end up in the ironic, and arguably tragic, position of calling the U.S. government their “last hope.”[462]

B. Possible Limits on Tribes

Escaping this form of subordination requires rethinking the processes and limitations that currently define tribal rights to engage in environmentally destructive development. Desert Rock is emblematic of the current state of things; a project, even one fully supported by a tribe’s government, must go through EPA’s permitting process, during which environmental groups actively lobby against the project.[463] Although by law the U.S. government has a government-to-government relationship with Indian tribes, Indian governments lack the power to set their own terms for reservation environmental protection.[464] The history of the United States is replete with periods of environmental destruction in the name of economic development,[465] yet the Navajo Nation is not allowed to determine its own balance between these competing goods. Instead, the U.S. government and environmental organizations—even on-reservation groups—“respond to Indian proposals for development initiatives or alternative conservation practices that conflict with their own proposals” by relying on a U.S.-centric decision-making process.[466]

Before turning to the approach favored by this Article—that environmental organizations relate to Indian tribes as if the limits on Indian sovereignty regarding development and the environment approximated international human rights limits on nation-states—it is worth considering four alternative answers to the question of appropriate limits. The four alternative approaches for setting the limits of tribal environmental destruction considered are 1) federal primacy, 2) Indian trust doctrine, 3) cooperative regulation, and 4) tribal determination and international sovereignty. For reasons explained in Part IV, an international human rights approach does a better job than any of these alternatives at recognizing tribal sovereignty while not giving tribes a carte blanche. But even though this Article concludes by supporting a human rights approach, each of these alternatives is supported by valuable insights that ought to be incorporated into an environmental regime based on a tribal international human rights order.

1. Federal (Administrative) Primacy

As the Desert Rock controversy shows, federal administrative primacy largely defines the current environmental regulation of reservations. This is not to say that tribes and states play no role, but the regulatory framework is decidedly federal. Thus, Professors Judith Royster and Michael C. Blumm introduce “Environmental Protection” in their textbook, Native American Natural Resources Law, by writing, “This section explores the interplay of federal, tribal, and state authority for environmental protection in Indian country. In particular, these materials focus on which of the governments is authorized to carry out the federal environmental programs in Indian country.”[467] Within this framework, limiting state regulation of the reservations and granting tribes “treat[ment] as states” by EPA is sovereignty enhancing.[468] Tribes and Indian advocates have fought hard to gain this level of tribal control over the environment, which, generally speaking, reflects where tribes are today.[469] Though celebrating these advances with regards to federal recognition of sovereignty, it is important to remember that the overarching structure is federally defined.[470] Tellingly, the environmental provisions of the 2005 Indian Tribal Energy Development and Self-Determination Act,[471] while placing “greater practical decision‑making in the hands of energy tribes,” also mirror the existing federal environmental requirements.[472]

Federal primacy, in environmental law and generally, can protect tribes from the states. As the Supreme Court observed in 1886, historically states have been the “deadliest enemies” of Indians, and the federal government has consequently had to play a protective role.[473] Substituting state or local authority for federal oversight undermines the government-to-government relationship that has defined United States–Indian relations since the Trade and Intercourse Act of 1790.[474] The Supreme Court enshrined a uniquely federal-tribal relationship into the common law in Worcester v. Georgia,[475] a case dealing with an attempt by Georgia to impose state law upon the Cherokees in the 1830s.[476] Chief Justice John Marshall wrote, “The treaties and laws of the United States contemplate the Indian territory as completely separated from that of the states; and provide that all intercourse with them shall be carried on exclusively by the government of the union.”[477] The idea, Judge William Canby, Jr. explains, was that “[w]hen tribal interests, broadly viewed, were affected, the state was excluded.”[478] Professor Robert Clinton’s work on the Indian Commerce Clause of the Constitution shows that the framers’ original understanding was that states would have no powers over tribes and that federal “power is broad vis-à-vis the states.”[479] Not contemplated by the framers, according to Professor Clinton, was the Supreme Court’s transformation, beginning at the end of the nineteenth century, of the exclusive federal-tribal relationship of international sovereigns into plenary power over tribes.[480] Though there is no “true constitutional benchmark to orient the federal-tribal discourse on sovereignty,” tribes seem to be stuck, at least for now, with the plenary power doctrine.[481]

The heavy hand of the federal government extends to environmental matters and arguably should serve as a check on the role of states. While environmental laws that affirm tribal sovereignty are a factor in preempting state authority, plenary power also plays a role.[482] State assertions of jurisdiction over reservation land and resources arguably undercut tribal sovereignty even when states act seemingly with the best of intentions. The state of New York in 2001 decided to sue General Motors (GM) because of the chemical pollution being discharged by a GM plant located near the St. Regis Mohawk reservation.[483] After noting the history of an exclusive federal-tribal relationship, a law review article on New York’s proposal argues that the offer to help “should be viewed with skepticism.”[484] The problem with this seemingly supportive stance of the state, according to the article, is that it “extends the reach of states, generally chipping-away at the seemingly ever-dwindling sovereignty of tribal peoples in the United States.”[485] According to this perspective, the federal government acts as “a shield against the states’ gentleman’s sword, such as New York’s encroachment upon the federal-tribal relationship,” preventing the erosion of tribal sovereignty and authority over the environment.[486] The same perspective can be seen in the decision of the Alaska Inter-Tribal Council and the Yukon River Inter-Tribal Council to oppose transfer of National Pollution Discharge Elimination System primacy, which would transfer permitting authority from EPA to the State of Alaska, because such a transfer would “subvert Tribes legally recognized right to government-to-government consultation.”[487] Such a strong enforcement of a state-tribal line may seem out-of-place when states and tribes are in agreement, but it protects tribes when states and tribes disagree and tribes face the insistence that they yield to conflicting state interests.[488]

Federal environmental law also provides space for tribal environmental enforcement and—so long as tribes remain within federally determined parameters—for tribes to make some decisions regarding their level of environmental protection versus development.[489] A classic example is that tribes can reclassify reservation air quality under EPA’s PSD regulations, as the Tribal Council of the Northern Cheyenne chose to do in 1976, over the protests of strip-mining coal companies.[490] The Ninth Circuit upheld the reclassification with language indicative of a move towards treating tribes as states by EPA: “[S]tates and Indian tribes occupying federal reservations stand on substantially equal footing,” the court stated, adding that it could not find “Congressional intent [in the Clean Air Act] to subordinate the tribes to state decisionmaking.”[491] The tribe’s PSD air quality reclassification required EPA’s approval and the decision had as much to do with the role of EPA as the tribe’s actions, but despite such a caveat, the decision “set an enduring legal and political precedent for Indian country environmental law.”[492]

Treating tribes as states was the EPA’s solution to two related problems: filling the gaps of federalism and determining the extent of tribal powers. The United States is popularly conceived of as having only two levels of government—federal and state—with tribes “effectively neglected, if not completely omitted” from consideration.[493] EPA moved away from the “basic strategy of not mentioning Indian tribes”[494] with its 1984 Policy for the Administration of Environmental Programs on Indian Reservations.[495] Three years after Nance v. EPA, EPA committed to Indian tribes playing a “lead role for matters affecting reservation environments” and taking on responsibilities “under terms similar to those governing delegations to States.”[496] While treating tribes as states (TAS) arguably fails to accord tribes their proper due as sovereign nations, under such a policy tribes can establish reservation environmental protection levels. TAS operates under federal guidelines and tribes are not free from EPA involvement, but tribes can do some things under TAS—like set water quality standards that are higher than federal or state standards—that might be surprising.[497]

TAS, even though it is part of federal primacy over reservation environmental regulation, is arguably an attractive option. Professor Lincoln Davies concludes his in-depth study of the Skull Valley Band of Goshute Indians’ proposal to store nuclear waste on their reservation by advocating a “mechanism by which tribes can have guaranteed sovereignty equivalent to what we afford states today.”[498] Facing an uncertain future and a shrinking tribe, the Goshutes hoped that storing nuclear waste would “revitalize their nation” through project-related jobs and payments.[499] The willingness by some tribes to accept nuclear waste, according to Professor Saleem H. Ali, should not be discounted as merely a sign of desperation; rather, the choice “should be seen as a self-conscious (and, perhaps, misplaced) attempt to invigorate self-determination, absent other avenues to do so.”[500] Initial environmental impact statements supported the Goshute proposal.[501] Just as Bill Richardson actively opposed Desert Rock, the governor of Utah played a similar role—going so far as to attempt to create a land moat around the reservation to block transportation routes to the proposed storage facility—in trying to derail to Goshute project.[502] In 2006, Senator Orrin Hatch declared the nuclear storage plan “stone cold dead.”[503] In many ways Desert Rock and the Goshute nuclear proposal are analogous examples of tribes considering environmentally harmful forms of economic development. After presenting the Goshute proposal controversies, Professor Davies argues that tribes should have the right to opt into a state‑like type of sovereignty.[504]

The attractiveness of federalizing tribal sovereignty is that sovereignty is recognized but is also subject to a natural limit. Professor Davies’s solution and EPA’s TAS both require that tribes “submit to” aspects of federal law.[505] The thinking behind such a requirement is simple: “because the actions of every sovereign entity in this country can affect the others, there is a need to moderate such [transboundary environmental] harms in an evenhanded and fair way.”[506] Certainly the Goshute proposal has externalities affecting those off-reservation (to give just one example, one would predict that land values of parcels near the nuclear storage facility would fall), just as Desert Rock would impose local and global externalities. Under Professor Davies’s proposal—which for power plant development is close to the current state of the law under EPA’s permitting scheme—the allowed form and degree of tribal environmental destruction for economic gain would be moderated by the federal government, just as the federal government has the same role for states.[507] As Professor Davies acknowledges, this externality solution is above all else a “practical” one, but is it appropriate for the Navajo Nation?[508]

The trouble with federal primacy is found in the moderation’s unidirectional nature. Dealing with the externalities of sovereigns is a crucial part of any regime, but leaving the “evenhanded and fair” setting of limits entirely in the federal government’s hands is an imperfect solution at best.[509] Besides undermining tribes’ claims to be independent nations with separate sovereign authority,[510] federal primacy in environmental regulation and enforcement fails to take into account other differences between tribes and states. For example, should the Navajo Nation have more rights to pollute the environment than, say, Delaware in order to help bridge the income gap between the reservation and the rest of the United States? Or, to take another example, should EPA public participation practices be required, or should a tribe be able to set different standards for public involvement and forms of acceptable dissent? Federal primacy answers these and all other questions by insisting that standard federal guidelines applicable to states should also apply to Indian nations.

2. Indian Trust Doctrine

The core idea of federal (administrative) primacy, that the United States should determine the extent of permitted environmentally harmful forms of reservation development, also is supported by the Indian trust doctrine. An  enhanced version of the Indian trust doctrine when it comes to the environment is presented most fully by Professor Mary Christina Wood over the span of three law review articles.[511] Professor Wood argues that when it comes to development that directly or indirectly impacts the reservation environment or land base, at times the trust doctrine requires federal judges to block tribal council approved projects.[512] By operating independently of statutes or administrative agency practices, the Indian trust doctrine arguably limits reservation development more than does federal administrative primacy.[513] In order to appreciate the potential applicability of the trust doctrine on tribally supported development such as Desert Rock, it is worth exploring Professor Wood’s arguments in depth.

According to the Indian trust doctrine, the United States has a trust relationship with Indian tribes that should guide policy and judicial review.[514] The Supreme Court’s rejection of the breach of trust claim in Navajo Nation  I, upheld in Navajo Nation II, suggests that the trust doctrine approach may get only limited support from the courts. In Navajo Nation I, the Court acknowledged “the undisputed existence of a general trust relationship between the United States and the Indian people.”[515] But in Navajo Nation I and II, the Court ultimately twice forgave the Secretary of the Interior’s clear breach of the trust obligation that is supposed to run to Indian tribes.[516] What amounts to judicial skepticism regarding trust doctrine enforceability does not, however, mean that the trust doctrine necessarily has no teeth nor that federal policy should not reflect the doctrine. Were it to be taken more seriously by all branches of the U.S. government than it was in the Navajo Nation decisions,[517] the trust doctrine arguably would involve the imposition of an outer limit on tribal development decisions impacting reservation land.

According to Professor Wood, underlying the trust doctrine is protection of the possibility of tribal separatism and the tribal land base.[518] Since development decisions can imperil the land base and consequently tribal separatism, Professor Wood argues that the trust doctrine requires the rejection of certain environmentally harmful forms of development.[519] The  conflict between the trust doctrine and self-determination when it comes to development can be seen in Professor Wood’s formulation of the doctrine itself. Professor Wood writes, “[T]he core principle of the trust doctrine remains a duty to protect a viable native separatism and tribal sovereignty,”[520] but these are really two principles—separatism and sovereignty—which at times align but at times conflict. Professor Wood resolves these conflicts in favor of the environment, preservation of traditional ways of life, and dissidents, asserting that maintaining viable separatism can justify overturning development decisions of tribal councils.[521] The trust doctrine, she argues, requires that when the tribal council makes a shortsighted or wrong decision regarding the tradeoff between development and the environment, secretarial approval should be withheld and federal courts should step in to block such development.[522]

In writing that the trust doctrine requires federal review of tribal council decisions,[523] Professor Wood accepts a narrowing of tribal sovereignty as a necessary consequence of the United States’ trust obligation to Indians. Though administrative approval regarding tribal land use is vested in the U.S. Department of the Interior for many tribes and land-use decisions, in practice tribal council decisions are treated deferentially and Professor Wood does not view the federal approval process as providing a meaningful check on tribal council decisions.[524] Institutional review of tribal council lease and development decisions would therefore be with the federal judiciary. Federal courts have hesitated to be actively involved in tribal matters, dismissing claims because tribal sovereign immunity prevents an “indispensible party,” the tribal government, from being subject to suit.[525] The involvement of a less hesitant judiciary would be driven by the challenges of dissident tribal members opposed to the actions of their own tribal council.[526] For Professor Wood, the trust doctrine requires that non‑Indian judges and courts review tribal council decisions and administrative approvals to “ensure the perpetuation of the land base as an attribute of native sovereignty.”[527]

Professor Wood argues that there is no inherent contradiction in tribal sovereignty and the simultaneous probability that if federal courts follow her aspirational version of the Indian trust doctrine they will overturn tribal council decisions.[528] The counterargument is acknowledged: “Any judicial invalidation of a transaction initially approved by a tribal government naturally strikes many as an invasion into tribal prerogative. Indeed, some advocate complete control by tribal councils over all tribal lands and resources, without any federal approval role.”[529] The question of whether federal courts are the appropriate forum to decide what is beneficial for Indian country is also acknowledged: “Judicial intervention in this context may intrude on the sovereignty of tribes by substituting a court’s notion of what is in the best interests of the tribe for a determination made in the first instance by the tribal government itself.”[530] But the thrust of Professor Wood’s argument is that when it comes to long-term leasing or environmentally harmful development, such decisions cannot be left to tribal governments. Professor Wood argues that tribal councils may not provide dissenters—what under her framework are federal court plaintiffs—”adequate remedy,” essentially a challenge aimed at what should be assumed regarding tribal government processes.[531] They also may fail to adequately take into account the position of traditionalists or future generations.[532] Finally, tribal councils, Professor Wood cautions, may be unable to resist powerful non-Indian interests seeking access to tribal resources.[533]

The Indian trust doctrine can prevent non-Indian interests from acquiring access to reservation resources otherwise available with permission of the tribal council. Sovereignty and federal review are not in conflict, Professor Wood argues, because sovereignty absent federal review is impossible: “Self-Determination will prove a hollow concept if industry and the government exploit it to serve the interests of the majority society at the expense of the native nations. Indeed, it will become nothing more than continued colonialism under the banner of native sovereignty.”[534] Or put differently, “[w]hat often amounts to an automatic deference to tribal councils effectively eliminates any restraint against transfer of Indian lands and resources. Taken to its extreme, this policy may resurrect the specter of Termination under the more palatable banner of Self-Determination.”[535] This is strong language is supported by Professor Wood’s position that “tribal councils frequently capitulate to development proposals even when individual tribal members strongly oppose the development for religious and spiritual reasons.”[536] Capitulation language echoes the concern tribes are entering into contracts of adhesion, the difference being that while the concern in Part III.B was with unfair contracts, Professor Wood favors a heightened standard of environmental protection for reservation, relative to off-reservation, development.[537] This aspirational version of the trust doctrine requires that the U.S. government “insulate tribal lands from the priorities of the non-Indian market,”[538] based on a “federal fiduciary duty to protect a tribe’s territory against market encroachments of the majority society.”[539] The argument ultimately is that Indians are different and traditional ways of life must be protected from “the development and pollution that now plagues nearly every sector of the majority society.”[540]

By elevating the tribal member objections to tribal council actions from internal tribal matters to the level of the trust doctrine enforceable by federal courts, Professor Wood ends up prioritizing the environment and the idea of static reservation ways of life over tribal sovereignty. The argument is made that federal administrative and judicial oversight “does not amount to a per se intrusion into the internal affairs of the tribes as long as the federal government directs its authority primarily against the non-Indian entity seeking to do business with the tribe.”[541] But this argument does little to address situations, as in the Desert Rock proposal, where a tribe initiates the proposal or where a tribe is working in partnership with a non-Indian entity. Additionally, Professor Wood advocates “a role for the trust doctrine in protecting the more traditional elements of native separatism.”[542] But I find the romantic assertion that traditionalists enjoy special priority vis-à-vis (generally speaking, democratically elected) tribal councils that should be protected by the United States government similarly unconvincing.[543] It is true that “tribal council decisions often prompt fierce protests by other tribal members who wish to maintain a more traditional, land-based way of life on their reservation and who may consider such industrial development both a desecration of their lands and a harbinger of cultural extinction.”[544] However, that does not mean that Indian trust doctrine enforcement is the best way to deal with such protests.

Though conceptually the trust doctrine could be considered federal primacy’s cousin, because of the strength of Professor Wood’s arguments, it is worth fully considering her Indian-trust-doctrine-based approach to environmentally harmful activities on reservations. Ultimately, I have no better counterargument than Professor Wood’s own summary of the argument against federal enforcement:

[C]onflict over development is not uncommon in other governments, and the existence of conflict alone may not justify judicial interference. Self-determination can flourish on reservations only if the federal government leaves tribes to set their own priorities. The tribal governments carry the mantle of authority, and while their actions may meet with dissension within the tribe, part of the price of sovereignty may be improper or unwelcome management by tribal governments. Federal intrusion of any kind may be fundamentally incompatible with tribal sovereignty.[545]

The difference is that while Professor Wood finds these reasons not compelling, I do, and as a consequence I do not think the federal government—particularly federal courts—should be in the position of passing judgment on tribal development decisions.

3. Cooperative Regulation

The third alternative approach for setting the limits of tribal environmental destruction is cooperative arrangements between Indian nations and local governments. Pollution is not bound by lines in the map—environmental issues off-reservation impact nearby Indian tribes and vice versa. Projects, whether a power plant or a waste facility, often serve Indian and non-Indian communities,[546] and for tribes the economic gains may be based primarily on off-reservation demand.[547] Overlapping concerns and impacts, such as where there is “mutual interest” in “the same natural resources,” seem to call for a cooperative approach to environmental regulation.[548] Scholars have taken note: Cooperative agreements have become a preferred solution for tribal-state conflicts, including environmental ones.[549]

There are practical reasons to support cooperative agreements, and scholarship or case studies on environmentally destructive activities proposed by tribes frequently end with a call for cooperation. An article on indigenous commercial fishing, after a section introducing all the problems, concludes that “[a] plausible approach for addressing these conflicts is the creation of joint agreements between indigenous peoples and state or federal governments, explicitly establishing the parameters of indigenous fishing rights.”[550] Jana Walker and Kevin Gover make cooperative agreements the final suggestion for how tribes could improve the “legal infrastructure” to encourage economic development, and their description presents the many positives of such agreements:

Cooperative agreements can be essential for environmental control because pollution does not respect political boundaries. Neither tribes nor states can effectively regulate regional environmental quality without the cooperation of the other. Joint regulatory programs avoid jurisdictional disputes by allowing the parties to agree on who will regulate a particular activity for a particular period of time. Moreover, cooperative agreements lower intergovernmental tensions that can damage the overall quality of state/tribal relations and also provide greater flexibility for both tribal and state policy-makers in the future. Finally, environmental agreements stretch limited tribal and state funds by reducing administrative and service costs. Given the limited resources of most tribes and the twenty-year head-start on environmental regulation enjoyed by states, cooperative agreements may give tribes the ability to call upon state resources and expertise in creating tribal programs.[551]

These benefits underlie a similar ending to another article: “Given the high mobility of air pollutants and the interdependence of state and tribal jurisdiction, it is imperative for Tribes and States to come together and work cooperatively for environmental protection.”[552] Yet another author believes “negotiation may produce a more useful means to build relationships between Indian tribes and federal officials.”[553] But will “tribes and states [working] together to achieve compromises acceptable to both sovereigns” really work for nuclear waste?[554] Or for a new coal-fired power plant in the four corners?

Cooperative regulation in theory avoids the pitfalls of federal primacy—tribal sovereignty is not diminished when tribes agree to share regulatory authority with states or localities—while also directly dealing with cross-border externalities. Cross-deputization agreements have helped tribes police reservations, and these practical agreements to work around Supreme Court limitations on jurisdiction over non-Indians show the potential of cooperative agreements generally.[555] Professor Alex Tallchief Skibine has “advocated a return to a relationship based on consent,” with tribal, state, and federal jurisdictional responsibilities established by negotiation.[556] But importantly, Professor Skibine’s hope is that the new “treaties, compacts, covenants, or agreements which would outline the elements of the new relationship” would be negotiated between tribes and the United States—period.[557] Cooperative regulation in contrast involves negotiation with all levels of non-Indian government which, given an emphasis on practical local solutions to local problems, means there is “room—abundant room—for tribal negotiations with the states in areas where local concerns control.”[558] The “increased cooperation” between tribes and all levels of non-Indian government is described as “a major positive development” by Professor Charles Wilkinson and the American Indian Resources Institute.[559] Similarly, Professor Rebecca Tsosie concludes that with a “foundation of mutual respect and appreciation for the complex issues at stake, Indian nations and states can likely make better decisions about the future than any single judge or court system.”[560] After presenting the rise in cooperative agreements and in state laws authorizing negotiation with tribes, Professor Matthew Fletcher writes, “Tribal-state agreements are exercises of sovereignty.”[561] But Professor Fletcher’s far more interesting claim is that cooperative agreements actually are “a means of earning governmental legitimacy” for tribes, because the signing of such agreements is itself a form of recognizing tribal government legitimacy.[562] But, in my opinion, much depends on the content of the agreements; after all, as Professor Robert Laurence reminds us, “one of the ways for a tribe to lose sovereignty is by voluntary surrender of it.”[563]

Having written about the dangers of uncritical support of cooperative agreements elsewhere, I focus here on the limits of such agreements when facing a particular controversy.[564] Even if cooperative agreements worked ex ante, without endangering tribal sovereignty, cooperative agreements would not likely be a successful mechanism for setting the limits of tribal environmental destruction in the context of a controversial proposal. Ex post—once a viable project is proposed and supported by a tribe—states or localities opposed to the project are not likely to enter into cooperative agreements that would permit the project to go forward.[565] Once the Navajo Nation decided to pursue Desert Rock, a cooperative agreement was not going to resolve the dispute, nor would either the tribe or local non-Indian governments concede regulatory authority to the other side. Cooperative agreements are not the deus ex machina of environmental regulatory conflicts and, while they would be “a mainstay of Indian law utopia”[566] and can help set the advance terms of some proposals with cross-border impacts, it is important not to overstate the potential of cooperative agreements.

4. Tribal Determination and International Sovereignty

Unqualified tribal determination of the trade-offs between development and the environment is the fourth alternative approach for setting the limits of tribal environmental destruction. The key feature of this alternative is that tribes truly control their environmental protection.[567] This means more than allowing tribes some administrative authority over a range of possibilities set by federal guidelines and historically provided by federal agencies.[568] Under this approach, Indian nations set their own priorities, regulatory methods, and pollution tolerance levels independently, without reliance upon federal enabling statutes or EPA oversight.[569] The long history of federal control of reservation life, continuing in a perhaps muted form through the present self-determination period, makes such a state of “full sovereignty” hard to imagine.[570] Moreover, focus on “the terms of sovereignty” alone risks undermining or diverting attention from claims important to Indian communities, but that do not fit neatly into struggles over jurisdiction.[571] Most articles on Indian issues focus on working within the existing constraints or making minor tweaks to the federally designed system, and consequently some scholars will reject this alternative as unduly utopian.[572]

Tribal determination at its fullest involves removing federal oversight of development on Indian land. In the environmental context, tribal determination would involve movement from federal to tribal primacy:

[F]ederal policy must recognize that tribal communities are fully capable of evaluating waste project proposals and making good decisions for themselves. . . . Congress must avoid environmental paternalism and instead show its confidence in tribal decision-making. If and when a tribal community decides that it wishes to pursue such a project, Congress should not only accept, but also respect that decision.[573]

As shown in the above quote, project decisions under this alternative are in tribal hands.[574] The law should assume that Indian nations will make good decisions regarding project developments, either because advocates truly believe tribes always will or because tribal sovereignty means tribes should have the space to make decisions non-Indian governments would not support. “Tribes are fully capable of deciding for themselves when projects will or will not serve their best interests,” and therefore, according to this perspective, environmental paternalism, even if motivated by concern for environmental justice, is not appropriate.[575] Such insistence on the ability of tribes to decide for themselves also reflects frustration at non-Indian assumptions of tribal incompetence.[576]

For many readers, the full tribal control approach will evoke arguments that Indian tribes should be considered sovereign nation-states under international law. The approach this Article concludes with, developed in Part V, borrows from international human rights law but should not be confused with full tribal control as nation-states. Aspects of the U.S.-tribal relationship, such as the history of treaty making, reflect recognition of tribes as international actors. But in Johnson v. M’Intosh,[577] Chief Justice Marshall accepted the doctrine of discovery, under which the Christian nation that discovered new land not only gained title to that land, but also Indian “rights to complete sovereignty, as independent nations, were necessarily diminished.”[578] Chief Justice Marshall later characterized Indian tribes as “domestic dependent nations,”[579] a description that stuck.[580] Though the Supreme Court continues to be comfortable with it, pro-Indian advocates have not quietly accepted diminished tribal sovereignty. For some scholars, discontent is expressed in largely doctrinal terms, often critiquing the Supreme Court’s narrowing of tribal jurisdiction over non-Indians or the Court’s inconsistency.[581] For others, the way forward cannot be found in U.S. precedent but instead in international law.[582]

An extensive body of scholarship rejecting the “domestic dependent” qualifier asserts that Indian nations should be understood and treated as international sovereigns. Though a 1961 article declared that “[t]he possibility of the international status of the Indian nations is of little more than academic interest” at the time of the article, many of the debates in the Indian law field revolve around related questions.[583] For example, should plenary power be rejected because of its racist origins and incompatibility with true sovereignty?[584] How should Indian rights as U.S. citizens be impacted by their simultaneous status as tribal members? And should the U.S. government have the power to limit tribal choices regarding on‑reservation development or land use? Numerous scholars have answered these questions by drawing upon the international law of states, either analogizing between tribes and nation-states or insisting that Indian nations are equivalent to all other nations and should be treated as such.[585] While one could imagine recognizing tribal determination over project approval without recognizing other aspects of nation-state sovereignty, defining the powers of Indian nations according to international sovereignty standards would involve an expansion of the scope of independent tribal determination.[586]

V. Environmentalists and Tribes

The center should not hold. The current federal permitting process requires that Indian nations fend off indirect attacks on their sovereignty by environmental organizations.[587] It also seems to put environmental organizations in the position of having to either give up on their larger environmental goals or participate in the colonialism of federal environmental primacy. The alternative approaches explored so far—federal primacy, Indian trust doctrine, cooperative regulation, and tribal determination as international sovereigns—all contain valuable attributes, but all fall short in some way or another. Federal primacy provides a way of dealing with the externalities of environmentally destructive reservation projects, but only by denying tribes the right to set their own path. Indian trust doctrine does much the same, but instead of decisions being determined by federal agency guidelines, they are made by federal courts. Cooperative regulation recognizes the importance of cross-border relationships and impacts, but has few solutions for situations of necessary conflict. Full tribal determination and international sovereignty allows tribes the greatest freedom to decide for themselves how to balance economic development and the environment, but besides being perhaps overly utopian, it fails to take into account potential local and global externalities of tribal projects. Given the shortcomings of the federal primacy, Indian trust doctrine, cooperative solutions, and nation-state solutions, let me suggest a more radical alternative: international human rights law. Established and emerging international human rights law related to sovereignty, development, and the environment, I believe, contains the promise of resolving the impasse between tribes and environmentalists while avoiding the pitfalls of colonialism inherent in federal primacy.

There are two important limitations to the argument that follows. First, the concern of this Part is the relationship between environmental organizations and Indian nations, not the relationship between the U.S. government and tribes. Why the distinction? The U.S. government’s Indian policy is well-established and unlikely to change dramatically for the better.[588] One can believe that the “severe limitations” the United States places on Indian sovereignty “does not change the fact that natives are still entitled to their full sovereign rights,”[589] without necessarily writing about the need for revolutionary change in federal Indian law.[590] Second, this Part’s argument does not explore all the dangers of environmental organizations adopting a human rights approach to tribal authority. Though I believe a human rights approach is promising, this Article should not be the final word on the subject. Hopefully, further scholarship in the area will explore the implications of a relationship between tribes and civic society based on human rights precepts rather than federal supremacy and shed light on possible adverse unintended consequences of the proposal.

This Part’s focus is on how environmental organizations respond to Indian nations that reach different conclusions regarding the trade-offs between economic development and the environment. The Part leaves the work of asserting that the U.S. government should take greater account of international human rights regarding indigenous peoples to others and focuses how environmentalists relate to Indian tribes regardless of federal primacy.[591] Progressives who work on environmental matters often instinctively support tribal sovereignty, yet when it matters—when a tribe is proposing an environmentally harmful project—they end up using U.S.  government processes to try to block tribes. My argument is that environmental organizations should base their relationships with Indian nations on norms and laws of international human rights regarding indigenous peoples. Doing so might lead environmental organizations not to oppose some projects and, when they do object, to channel their concerns through tribal and perhaps international institutions rather than U.S. processes.

A. Role of Environmental Organizations

The Hopi Tribal Council voted 12-0 on September 28, 2009, to ban environmental groups such as the Sierra Club and the Natural Resources Defense Council from the Hopi Reservation.[592] Two days later, Navajo President Joe Shirley, Jr. issued a press release saying he stood with the Hopi Tribal Council and described environmental organizations as being “among the greatest threat[s] to tribal sovereignty, tribal self-determination, and our quest for independence.”[593] Tribal Counsel for the Hopi Tribe, Scott Canty, accused environmental organizations of wanting to work with tribes “only on terms set by environmental organizations,” adding that they “blindly pursue their agenda without any real regard to the sovereignty or legitimate economic interests of the Hopi tribe.”[594] Similarly, President Shirley argued that “[e]nvironmentalists are good at identifying problems but poor at identifying feasible solutions,” continuing, “Most often they don’t try to work with us but against us . . . . They support tribes only when tribes are aligned with their agenda.”[595] Coverage of the ban on environmentalists countered the Hopi Tribal Council and Navajo President’s position by pointing out that some of the active environmental opposition groups were on-reservation, grassroots organizations.[596] The ban, and the reaction against the ban, reflects the heated nature of the current tribal-environmental debates and the tensions created by the existing structure of reservation environmental regulation.

The insight that seems to be escaping environmental organizations, I argue, is that by using the federal environmental regulatory scheme against tribal projects they are complicit in the subversion of Indian sovereignty. Although non-Indian groups and environmentalists can delay projects on tribal lands by “challenging the adequacy of the EIS in federal court,” should they?[597] Even though the federal government and federal Indian law are unlikely to radically change,[598] this does not mean environmental organizations that know, or should know, better[599] should not change the nature of their relationship with Indian nations. In the context of Desert Rock, by attempting to stall the project through the EPA permitting process, environmentalists in practice accepted and relied upon federal primacy.[600] By doing so they accepted the colonizing myth that “the United States has the right to boss Indian nations around without their consent. After all, America belongs to the Americans,”[601] or to American environmentalists in this case. Environmental organizations need not conclude that the Navajo Nation is a nation-state under international law—that it is “a sovereign as Bolivia is a sovereign”—to realize that federal primacy does not adequately respect Indian sovereignty.[602]

Environmental organizations ironically recognize indigenous rights to self-determination in other countries to a greater extent than they seem to in the United States. The environmental community has pushed foreign countries, international institutions, and corporations to respect the rights  of  international indigenous communities.[603] Basing their indigenous environmental policies on the principles of “free, prior, and informed consent” (FPIC) when it comes to indigenous peoples globally, environmental groups recognize indigenous rights to make decisions about development that will affect them and to benefit from development projects that go forward.[604] However, when it comes to Native Americans, environmental organizations take a different tact. Support for Indian nations when they oppose development or seek environmental redress turns into reliance upon federal primacy to block tribes when there is not issue alignment.

This Part explores what it would mean for environmental organizations to treat Indian tribes the way they treat indigenous groups globally. I make two principle arguments in this Part. First, I argue against an international sovereignty approach to indigenous peoples and in favor of international human rights as the basis for the relationship between tribes and environmental organizations. I argue that environmental organizations should replace domestic reliance upon federal primacy over the reservation environment with a modified version of the internationally-used principles of free, prior, and informed consent when it comes to development in Indian country.[605] Second, I discuss the heightened governance responsibilities that tribes might have under a human rights framework. To the degree to which tribes have embraced, or decide to embrace, international human rights when convenient, I argue they must also accept the limitations on sovereignty that comes with such an embrace of the human rights framework. The pressing problems of reservation poverty and global climate change may present a competing goods problem today, but human thriving for Indian nations and all peoples in the long run will require healthy economies and a healthy planet. That environmental organizations should unilaterally lay down the power over reservation development that they have by virtue of federal primacy’s colonializing aspects is an important conclusion of this Part, but the focus on how environmental organizations relate to Indian tribes should not be taken to mean that how Indian tribes relate to the environment is of lesser importance.

1. A “Rights” Approach to Indigenous Sovereignty

The environmental problems associated with treating Indian tribes as nation-states under international law caution against internationalizing Indian sovereignty. True, recognizing Indian nations as international equivalents to nation-states would be a rejection of plenary power and federal primacy, but it would also involve wholesale acceptance of the international legal order regarding states and their environmental choices. Indian nation-states would have tremendous freedom to engage in environmentally destructive development. Although institutions such as the United Nations (U.N.) have provided some avenues for the participation of non-governmental organizations in global governance,[606] the continuing structural weakness of international environmental law prevents environmental organizations from being able to block Indian nation-state supported projects as effectively as they can through the current EPA process.[607] Consequently, were Indian tribes to become nation-states under international law, environmental groups would have far fewer outlets to provide meaningful objections. They could lobby the United States to pressure tribes, but the U.S. government would not have the hammer of plenary power or EPA permitting. The only available option might be a local one, supporting tribal members or Indian organizations (such as Doodá Desert Rock) in their efforts against on-reservation projects.

Arguably this is as it should be: The “imperial pretence” that indigenous peoples have less right to sovereignty than European powers would be put aside and Indian nations would be subject to the same limitations as other nation-states.[608] Indians are not to blame if the international community has not succeeded in setting up an adequate scheme for limiting the potential nation‑states.[609] In the case of coal, the same government that pulled the Navajo Nation’s PSD permit has been unwilling to commit itself to reducing greenhouse gases and has severely dampened the impact of various multinational environmental efforts.[610] Environmentalists may object that these failures are the result of U.S. government policy and not something they should be charged with, but the stalled international order does reflect the environmental movement’s inability to garner the necessary political capital, especially in the United States. Just because international environmental law (IEL) would not be able to prevent harmful projects from going forward if tribes are recognized as nation-states does not itself justify denying international status to Indian nations.[611]

Indigenous peoples have struggled to be incorporated into the international environmental legal regime. Reliance on state-centered approaches and treaties between states as the means of developing IEL “did not leave any room” for indigenous environmental concerns.[612] It was not until 1992 and the Rio Declaration on Environment and Development, coming out of the U.N.’s Rio Earth Summit, that the “vital role” of indigenous people and their right to “effective participation” in environmental management was recognized.[613] The U.N. Declaration on the Rights of Indigenous Peoples (the Declaration), adopted by the General Assembly in September 2007, though not environmentally focused, states in Article 29, “Indigenous peoples have the right to the conservation and protection of the environment and the productive capacity of their lands or territories and resources.”[614] The United States and three other countries did not sign onto the Declaration, but the Declaration remains a “powerful statement” on indigenous rights supported by most of the world.[615] Yet, indigenous peoples remain on the periphery of international environmental law and, perhaps because their claims to international sovereignty are not taken seriously, they have made few inroads into the IEL canon.[616]

The attraction of international law also comes with a choice between sovereignty and human rights as the proper approach for indigenous advocacy. Professor S. James Anaya’s explanation is worth quoting at length:

The appeal to international law is to its presumptive capacity to exert control over or influence the exercise of power, most significantly the power welded directly by independent states. Indigenous peoples and their advocates have advanced arguments based on what international law is perceived to provide or what it should provide to condition the behavior of states in their relations with indigenous peoples. International law is looked upon as a way of compelling, or at least encouraging, states to act consistently with a catalogue of rights deemed fundamental to the survival of indigenous peoples, including rights over lands and natural resources. Among those who advocate for indigenous rights within the discourse of international law, two, usually complementary, strains of argument emerge.[617]

The argument strains that Professor Anaya identifies are a “state‑centered frame” and a “human rights frame.”[618] The first strain involves positing “indigenous peoples as states, or something like states, within a perceived post-Westphalian world of separate, mutually exclusive political communities.”[619] In other words, the international nation-state approach discussed in Part IV.B.3 of this Article, or a nation-state-like approach of partial recognition of sovereignty.[620] The second strain of argument asserts that indigenous peoples rights are “moral imperatives” supported by “human rights principles that are already part, or becoming part, of international law.”[621] Professor Anaya ends up supporting the second strain of international law approaches by indigenous advocates, arguing in favor of the “pragmatic and ethical” realist use of human rights law in a way that incorporates developing standards.[622] What this argument offers is the possibility that the problematic independence of sovereign states need to be fully incorporated into the way environmental groups relate to Indian nations.

Instead of “historical sovereignty” stopping all discussion about the proper balance between economic development and the environment, “the human rights discourse” allows tribes and environmental organizations alike to escape from formalistic ideas of statehood.[623] Indian tribes have a realist’s appreciation for the fact that the United States will play a significant role in their development. While it is arguably reasonable that the Navajo Nation, given its population and size, might have a greater claim to more attributes of international sovereignty than a small, heavily allotted tribe, being surrounded by the United States and being dependent on U.S. government funding does limit the Navajo Nation’s ability to remove the U.S. role completely.[624] Small, weak nation-states reveal “the myth of sovereign equality” in the international sphere[625] and an internationally-recognized Navajo Nation would still be less powerful than the United States, and the relationship would reflect the power differential. This realization suggests another reason, besides improbability of it actually occurring, why internationalization of tribal sovereignty would not end the need for some tribal accommodation of U.S. interests. But should environmental organizations approach to tribally proposed projects be based upon power alone? Put differently, what legal theory besides federal primacy and plenary power should guide environmental organizations as they deal with Indian nations?

The international legal origin of federal Indian law arguably provides the basis for insisting that international human rights ought to inform domestic treatment of Indians. This is Professor Phil Frickey’s argument in Domesticating Federal Indian Law.[626] U.S. power over Indian tribes was originally based upon international law, but that power was never constitutionalized.[627] Professor Frickey argues that the “backdrop of international law provides the only satisfactory basis for sorting out the existence of an inherent federal power over Indian affairs,” and consequently, international human rights norms regarding indigenous peoples are a necessary backdrop for consideration of U.S. power over Indians.[628] Under this theory, international human rights norms regarding indigenous peoples should be considered by courts because federal Indian law links them “directly to the Constitution,” not because of the independent value of human rights norms.[629] Though Professor Frickey’s article centered on how courts should consider U.S. power over Indians, if courts should take into account the backdrop of international human rights under domestic law, arguably so should environmental organizations.[630]

Although Professor Frickey does not go so far as to say that international human rights norms should be applied regardless of the history of federal Indian law, others do. Tim Coulter, Executive Director of the Indian Law Resource Center, an indigenous rights organization with an international focus, supports the development of “a permanent, irreversible and universal consensus about the rights of Indian nations . . . [as] one of the best ways to assure the continued existence and self-government” of Indian peoples.[631] Professors Robert Williams and James Anaya locate an obligation to apply human rights standards to Indians not in the history of federal Indian law, but in international treaties that the United States has signed and in emerging international law regarding indigenous peoples.[632]

The quintessential form of international human rights law involves the protection of the individual from the state—the recognition of the individual’s human rights even against the majority or the state. For human rights scholars, it may therefore come as a surprise that the most important human right that indigenous peoples have been recognized to enjoy is the right to collective self-determination. The self-determination norm “arise[s] within international law’s modern human rights frame,” and derives from established human rights principles and norms.[633] Article 3 of  the U.N.   Declaration on the Rights of Indigenous Peoples reads, “Indigenous peoples have the right to self-determination. By virtue of that right they freely determine their political status and freely pursue their economic, social and cultural development.”[634]

Indigenous peoples’ collective right to self-determination does not fit neatly into international human rights law’s predominant framework of protection of individuals or discrete minorities. It is worth quoting at length a U.N. summary of indigenous peoples’ right to self-determination:

[I]ndigenous peoples, as collectivities, have distinct and unique cultures and world views, and their current needs and aspirations for the future may differ from those of the mainstream population. Their equal worth and dignity can only be assured through the recognition and protection of not only their individual rights, but also their collective rights as distinct groups. It is when these rights are asserted collectively that they can be realized in a meaningful way.[635]

The summary explains,

The core international human rights instruments protect the rights of the individual and establish obligations by States to guarantee, protect and respect such rights. The rights related to indigenous peoples seek to protect, in addition to individual rights, their collective rights, because recognition of such rights is necessary to ensure the continuing existence, development and well-being of indigenous peoples as distinct collectivities. Past experience has shown that unless the collective rights of indigenous peoples are respected, there is a risk that such cultures may disappear through forced assimilation into the dominant society.[636]

That self-determination is an important aspect of indigenous peoples’ human rights means that not recognizing the collective rights of Indians is a denial of their human rights, even though it would not be for other groups.[637] As the U.S. Supreme Court has acknowledged, the nature of Indian rights is sui generis,[638] and this holds true for how indigenous human rights are understood: Treating indigenous peoples as equivalent to individuals with regard to human rights protection is falsely reductive. Moreover, the collective nature of indigenous peoples’ human rights includes not only self‑determination rights but also land rights. Recognition of indigenous peoples’ ownership, use, and control rights over land has been driven by  a  human rights perspective.[639] As a result of indigenous efforts, “[t]he international legal order has come to recognize indigenous land rights as human rights.”[640] Self-determination and land rights are linked: “For many indigenous peoples, the central focus of the right to self-determination is the right to control access to natural resources.”[641]

Environmental organizations’ reliance on federal primacy fails to respect the collective human rights of indigenous peoples to self‑determination and to control of their land. But why should environmental groups abandon the processes and laws that guide their work nationwide simply because projects are located in Indian Country? Within the Indian law scholarly community there is considerable debate about how much emphasis should be placed on international indigenous rights practice.[642] But the debate within the community is largely about the efficacy of arguments tied to indigenous peoples’ rights before the branches of U.S. government, not about the contents of the rights. Were Indian advocates successful in rewriting the terms of the relationship between Indian nations and the United States in a way that rejected the colonizing aspects of the law as it currently exists, environmental organizations would have no choice but to relate to Indian nations in line with the new rules. But as stated previously,[643] I do not believe that a radical change towards a more pro-Indian relationship with the United States is likely in the foreseeable future. And because this Part invites a misreading, it bears repeating that the topic being discussed here is how environmental organizations relate to Indian nations; quite deliberately this Article is not advocating one way or another on the direction or content of a radical change in U.S.‑Indian relations.[644]

Given the status of the U.S.-Indian relationship, environmental organizations must choose whether to accept the law—federal primacy—as dictated by the U.S. government or relate to Indian nations as prescribed by the (collective) human rights of indigenous peoples. Ultimately environmental organizations have to decide between accepting processes regarding reservation development that derive from the colonial relationship of federal primacy, or give up some authority in the name of indigenous peoples’ human rights. So what decision has been reached? In practice, domestically, environmental organizations make use of federal primacy, but when it comes to projects in other parts of the world indigenous peoples’ rights are embraced.[645] Domestically, non-Indian environmental organizations channel objections through federal permitting processes in the name of tribal dissenters or the environment itself.[646] In contrast with development proposals that implicate indigenous peoples’ interests internationally, environmental organizations insist that states respect the free, prior, and informed consent rights of indigenous communities.

FPIC provides indigenous peoples the opportunity to have a say and   play a role in development that affects their communities.[647] “[P]artially derived from the right to self-determination,” FPIC is the accepted international standard for indigenous involvement in reviewing project proposals.[648] The first three elements of FPIC are summarized below:

For consent to be “free,” it must be given without coercion, duress, fraud, bribery, or any threat or external manipulation.

For consent to be “prior,” it must be given before any significant planning for the proposed activity has been completed, and before each decision-making stage in the proposed activity’s planning and implementation at which additional relevant information is available or revised plans are proposed.

For consent to be “informed,” it must be given only after the affected indigenous people is provided with all relevant information related to proposed activities in appropriate languages and formats, including information regarding indigenous rights under domestic and international law, the likely and possible consequences of the proposed activities, and alternatives to the proposed activities. All information must be provided free from external manipulation and with sufficient time for review and decision-making in accordance with the laws and customs of the affected indigenous people.[649]

FPIC’s fourth element, consent, requires greater elaboration. FPIC requires more than “mere consultation.”[650] The indeterminate nature of consultation contrasts with the active community participation in decision making that consent entails.[651]

Although consent can be summarized as a community’s right to “approve,” and implicitly disapprove,[652] proposals, the question of “how to determine or quantify consent” is important.[653] The case can be made that consent should be determined by community referenda, especially when the affected community is a nonindigenous one.[654] The problem with a referenda process when it comes to Indian nations is that the imposition of such a process assumes the absence of an existing governance structure. Although a referenda process may be appropriate for some indigenous peoples, with perhaps a few exceptions “[t]he consent process should allow communities, indigenous peoples in particular, to participate through their freely chosen representatives and customary or other institutions.”[655] The exceptions might include situations where there is a known break between formally chosen representatives and customary institutions, such as with the Hopi tribe.[656] Otherwise, consent should be determined in a “way agreed upon by the community,” with respect given to “the representative(s) chosen by the community as the only legitimate provider(s) of consent.”[657] Answering the question of “whether consent is sought from a legitimate authority” is something for the particular tribe to decide, and not the work of outsiders.[658] Though FPIC participation can be associated with “inter- and
intra- community issues,” consent does not hinge on universal agreement.[659] This means that the presence of internal disagreement within a particular community regarding the decision of tribal representatives or leaders to approve or disapprove a project does not invalidate the decision.[660]

For all its strengths—FPIC certainly represents an improvement on the earlier international norm of not taking indigenous peoples into account—FPIC’s imagined community is largely passive. The assumption behind FPIC seems to be that project initiation is something indigenous peoples and communities do not do or are not capable of doing. FPIC accords them the right to participate and even to approve or disapprove projects, with the elements of FPIC designed to protect communities from the harmful effects of such projects and perhaps enable them to benefit in some way. But FPIC does not squarely address what rights indigenous peoples have regarding environmentally destructive forms of development that they propose. Sometimes this may be partly a matter of semantics: Is Desert Rock being proposed by the Navajo Nation with the agreement of their partner, Sithe Global, or is it the reverse? The assumption that indigenous communities are recipients rather than doers, environmental victims rather than environmental harm-causers, arguably goes against the applicability of FPIC when indigenous communities, including Indian nations, are project proponents rather than the impacted community. On the other hand, there would seem to be no proposal that better meets the requirements of FPIC than community or Indian nation proposed projects. In such situations the decision is being made freely, prior to project commencement, with full information, and with the “consent” or approval of the tribe or the chosen representatives of the tribe.

FPIC, although an imperfect mechanism from the standpoint of both indigenous peoples and environmentalists, is the emerging international norm for protecting indigenous peoples’ human rights to self-determination and land when it comes to development proposals.[661] The idea that, when it comes to natural resource extraction or other forms of environmentally destructive development, indigenous peoples “may legitimately choose to exercise self-determination and other human rights in ways that are not commensurate with the optimal environmental outcome as perceived by outsiders,” is only partly captured by FPIC.[662] The U.N. Commission on Human Rights final report on Indigenous Peoples’ Permanent Sovereignty over Natural Resources supports a particularly proindigenous peoples’ stance regarding the contents of their land rights.[663] Special Rapporteur Erica-Irene A. Daes writes, “Few if any limitations on indigenous resource rights are appropriate, because the indigenous ownership of the resources is associated with the most important and fundamental of human rights: the rights to life, food, and shelter, the right to self-determination, and the right to exist as a people.”[664] The U.N. report probably overstates the rights indigenous peoples ought to have. Put differently, to the question of whether indigenous people have an absolute right “to allow—as well as prohibit—access to natural resources,” the answer is no, and should be no.[665] But the report’s strong position comes out of the context of states routinely failing to respect basic rights of indigenous peoples’ to self-determination and land.[666] FPIC is similarly a product of the existing limited role indigenous communities play in development decisions.[667]

The human rights of indigenous peoples, especially rights to self‑determination, have attained the level of acceptance and definition that should guide how environmental organizations relate to Indian nations. One only has to think of the right to health or housing to see that human rights concepts can be nebulous and can reflect (utopian) ideals rather than standards to which actors will be held accountable. The tireless work of indigenous peoples and their advocates, however, has succeeded in bringing not only attention to but also concrete ideas regarding implementation of the rights of indigenous peoples.[668] FPIC is not perfect, but it reflects the growing awareness that indigenous communities have a right to more than token participation; generally speaking they have a right to approve or disapprove projects. Human rights law ultimately holds greater promise for guiding how environmental organizations relate to Indian tribes than does federal primacy.

2. Tribal Acceptance and Responsibility

The wisdom and success of the various Indian policies of the United States can somewhat accurately be summarized by looking only at the amount of say Indian nations had in their implementation.[669] When Indians have more say, the results have been better; when policies are imposed, results have been poor.[670] Tribal acceptance of the human rights framework is a necessary prerequisite before tribes should have to relate to outsiders according to the norms of international indigenous rights versus tribal sovereignty in its current form. This raises two sets of questions regarding the relationship between Indians and environmentalists. First, should Indian nations accept the applicability of international human rights law, since at times it will constrain the powers Indian nations would have as nation‑states? How would acceptance be manifest and what would acceptance mean for tribal governance? Second, whether tribes accept or reject the human rights framework, in light of indigenous peoples’ human rights, should the opposition of environmental organizations to tribal projects still be channeled through U.S. regulatory processes? Even though a change to the overarching relationship between tribes and the U.S. government is deliberately being taken off the table here so that the focus can be on the Indian-nation–environmentalist-organization relationship, a  move by tribes or environmental organizations towards a human rights approach could help delegitimize the existing federal framework.[671]

Caution is in order for tribal leaders contemplating acceptance of a human rights approach in their relations with environmental organizations. Given that recognizing indigenous peoples’ human rights entails recognizing self-determination rights, why should tribes hesitate to embrace human rights law and norms? In some circumstances tribes may be more limited under international human rights law than they are currently under federal Indian law. This can be seen in Santa Clara Pueblo v. Martinez,[672] in which the U.S. Supreme Court allowed a form of tribal gender discrimination despite the Indian Civil Rights Act.[673] The plaintiff in the case was a tribal member challenging the tribe’s membership rules on behalf of her child.[674] According to the membership rules, when the father was a tribal member and the mother a non-Indian, the child was considered a tribal member; but, when the mother was a tribal member and the father a non-Indian, the child was not considered a tribal member.[675] Had the Inter-American Court of Human Rights been able to hear the case, would that court have been as deferential as the U.S. Supreme Court to Santa Clara Pueblo’s tribal membership rules? Should the U.N. Special Rapporteur on Indigenous Peoples, a post currently held by Professor Anaya and part of the United Nations’ human rights regime, ignore gender discrimination in the name of self-determination?

Acceptance of human rights norms arguably would undo important aspects of sovereignty relied upon by tribal governments. Although as discussed previously, the collective nature of indigenous peoples’ human rights differs from human rights law’s typical dynamic of individual versus the state,[676] there is a limit on how far this contrast should be extended. Suppose a resident of tribally owned housing was evicted to make way for a relative of a tribal council member. Legal aid attorneys representing such a resident today confront the wall of tribal sovereign immunity, unless it has been waived with regard to tribal housing programs.[677] But under a human rights framework, a tribe would not be able to so easily dismiss the resident’s complaint. The same could be said of tribes that fail to protect due process rights of tribal members or that discriminate, along racial or other lines, against particular member classes. If a tribe accepted the applicability of the human rights approach with regards to the environment, would such acceptance spill over to other aspects of reservation life? Put another way, should acceptance follow the maxim in for a penny, in for a pound? Before tribes accept a human rights framework for their relationship with environmental organizations, the scope and impact of such acceptance must be carefully delineated.

Even if acceptance of a human rights approach could be limited to environmental issues, tribes may lose some of their sovereignty. FPIC, for example, might narrow the sovereignty of the Navajo Nation when it comes to the Navajo government’s support of Desert Rock. If the indigenous community being impacted is redefined not as the tribe as a whole, but as the tribal members located closest to the proposed site, then arguably the community’s rights were violated.[678] Although copies of the draft environmental impact statement were available at local chapter houses, the draft’s complicated format and failure to discuss crucial aspects of the project—especially CO2 emissions—arguably denied tribal members their right to be informed.[679] Additionally, the unwillingness of both parties to make public the contract between Sithe Global and the Navajo Nation is a clear violation of FPIC.[680] Perhaps more troubling from a protribal sovereignty perspective, if the conception of the community impacted were broadened to include those communities where visibility might be impacted by haze from the plant, then arguably the community would not be limited to the tribe. If participation of all impacted by development, not just the immediate, politically-defined community, became an expectation of international human rights, Indian tribes may be required to permit
non-Indians, on and near the reservation, a formal role in tribal decision making and the consent process.[681]

Despite the negative impact that acceptance of international human rights could have on tribal sovereignty, many tribes have in one way or another embraced human rights based efforts. Representatives of Indian tribes and tribal advocates participated in the lengthy effort to finalize the Declaration on the Rights of Indigenous Peoples.[682] At various points they worked to have international human rights bodies censure the United States for violations of the rights of Indian tribes and tribal members.[683] Indigenous peoples have also testified before such bodies on their unique connection to the land.[684] The Navajo Nation is no different. For example, in August 2009, Duane H. Yazzie, Chair of the recently formed Navajo Nation Human Rights Commission (NNHRC), traveled to Geneva to address the Expert Mechanism on the Rights of Indigenous Peoples of the U.N. Human Rights Council regarding the implementation of the Declaration on the Rights of Indigenous Peoples.[685] The Navajo Nation Council’s Intergovernmental Relations Committee had passed a resolution authorizing the NNHRC “to advocate for special recognition status” for the Navajo Nation, and Duane Yazzie’s comments highlighted “Navajo Nation’s successes and difficulties in implementing international standards and laws in the United States.”[686] When  Indian representatives appear before human rights bodies, their position is unidirectional, focusing on U.S. violations of their human rights and not on the possibility of Indian nations being held accountable for violations of tribal members’ human rights by those same bodies.[687]

Indian nations’ embrace of international human rights law and processes should entail more than just denouncements of U.S. policy regarding the injustices experienced by tribes; with the human rights embrace comes responsibility. Professor Angela Riley argues that “indigenous peoples are taking advantage of the ‘human rights culture’ to secure their own place in the global community. A theory of good native governance assumes that corresponding duties come along with indigenous peoples’ exercise of their rights.”[688] Good governance is hard, and for most if not all tribal and non-tribal governments, is a work-in-progress,[689] but drawing upon the international human rights framework implies an obligation on Indian nations to attempt to live up to that same framework. Professor Riley argues convincingly that what counts as good governance for Indian nations does not have to reflect non-Indian ideas of good governance.[690] After acknowledging that the United States has played and continues to play a significant role in undermining Indian nations, Professor Riley argues that nevertheless, “Indian tribes in a contemporary world are in a position to more fully consider their obligations to their citizens.”[691] The Harvard Project on American Indian Economic Development has done lots of work identifying institutional improvements that would improve tribal governance and help tribes become more responsive to tribal members.[692] Other scholars have recognized the need for “effective” tribal governments[693] and the related importance of “effective [environmental] programs.”[694] The challenge when considering changes to improve tribal governance and effectiveness is the tribal specificity involved. So although articles and sample codes have been written for everything from domestic violence to environmental review processes,[695] resolving the obstacles faced by one tribe in effectively serving tribal members may not be what is most needed by another tribe. And what works well for one tribe may not work for others. But for those tribes that use international human rights bodies to air grievances, it would be overly opportunistic to do so without accepting some attendant governance responsibilities to their citizens.

Regardless of the stance of Indian nations regarding the acceptance of the applicability of human rights standards, I believe environmental groups should stop relying upon federal primacy and federal processes to block environmentally destructive forms of development supported by tribal governments. Environmental organizations’ disparate treatment of indigenous peoples, depending on whether they are domestic or foreign, highlights both the singularity of federal primacy and the existence of a better model for the relationship between indigenous peoples and environmental organizations. FPIC provides one mechanism for ensuring community involvement does not take away from indigenous peoples’ ability to select their own representatives and to allow representatives to speak for them. The objection may be made that if Indian tribes do not accept a human rights framework, why should environmentalists? But such an objection reflects a failure to appreciate the denial of Indian rights inherent in federal primacy. Environmental organizations may fear that allowing development in Indian Country could be used as precedent for the rest of the United States; however, just because a particular level of pollution is allowed on a reservation does not mean that a higher standard should not be required elsewhere.[696] Establishing the possibility that on-reservation and off‑reservation standards could differ would allow environmental organizations to decide not to aggressively assert legal rights through federal processes when it comes to tribal projects.[697] To be clear, there is no legal requirement that environmental organizations separate themselves from federal primacy and its problematic assumption of U.S. superiority and related diminishment of Indian sovereignty. But sometimes the right thing to do is to lay down one’s arms.

Recognition of indigenous rights according to international human rights law by environmental organizations would involve a number of changes to the way non-Indian environmental groups interact with Indian nations proposing harmful projects. Such recognition would involve first prioritizing tribal processes of decision making rather than the federal permitting scheme. The next generation of tribal mining legislation notably supports prioritizing tribal processes: Under the Indian Tribal Energy Development and Self-Determination Act of 2005 (ITEDSDA), environmental review would be conducted by tribes, and public comments, including those of environmental groups, “will be reviewed in light of tribal values, priorities, and decisions, rather than filtered through a federal lens.”[698] Fear among environmentalists that tribal oversight would mean lesser environmental protection than would be true under federal oversight should not be enough to justify federal primacy. Such fear mirrors assumptions made by policymakers that federal management of tribal resources is better than tribal control;[699] yet, given the record of U.S. management, tribes probably “would do no worse” than the United States has historically on either resource management or environmental protection.[700] The Navajo uranium experience and even the political flip-flop on Desert Rock’s PSD permit by EPA after President Obama’s election attest to shortcomings in federal oversight. Environmental organizations would likely have less faith in federal permitting if the administration was still Republican. Decolonization of Indian law involves getting rid of the “underlying distrust of tribal governance” in EPA and among environmental organizations.[701]

The Navajo Nation provides avenues for project objections to be raised and it is important that internal dissent not be misused or misrepresented by environmentalists. Nearly every tribal government proposal—just like any U.S. government proposal—will have detractors. But the consequences are particularly acute for tribes, as “the age-old problem of internal disagreement . . . weakens tribal governments and has historically worked against Indian people.”[702] Non-Indian governments have undercut tribes by supporting dissenting factions and either signing agreements with them that purport to bind the entire tribe or using trumped-up tribal disagreement as a pretext for ignoring the will of the tribe.[703] Environmental organizations should not do the same. To be concrete, while the few Diné directly affected by Desert Rock are legitimately upset with the leadership of the Navajo Nation, their complaints should not be bootstrapped by environmental organizations or presented as the views of the Navajo people. The fact that “native peoples have not been of one mind on resource issues” should not provide a pretext for attempting to undercut tribal governments.[704] Exploiting dissent in the Navajo Nation fails to respect the will of the people—as expressed in the same way that it is in the United States, through democracy—and denies the majority the right to establish the balance between development and the environment through the political processes and internal tribal mechanisms.

B. The Big Picture and Desert Rock

Let’s be clear: The world is in the midst of an environmental crisis that will have far-reaching and global impacts. Environmental organizations and indigenous peoples worldwide will both be called upon to deal with the challenges associated with climate change, resource depletion, and sustainable development.[705] And construction of another coal-fired power plant in the Southwest would not symbolize a new start as much as a continuation of the development and consumption practices that are responsible for global warming. The development of alternative energy sources is required, and Indian tribes have an important role to play in how the United States powers itself and consumes resources.[706]

Indigenous peoples, globally and in the United States, are “among the most vulnerable” to the effects of climate change.[707] In 2007, the Natural Resources Law Center at the University of Colorado Law School published a report entitled Native Communities and Climate Change that captures the big picture regarding Indians and their environment.[708] The report goes region by region, exploring how climate change will threaten Indian life ways and in the process covers everything from treaty-based fishing rights to water rights.[709] The report’s focus is outward; that is to say, it is largely about how Indians are affected by climate change. Thus, the report notes that tribes “are among the most vulnerable to impact from climate change caused in large part by conventional fossil-fuel-based energy development.”[710] The outward focus of this report is shared by nearly all writing on indigenous peoples and climate change and is easily justified. As the U.N.  Permanent Forum on Indigenous Issues website states, indigenous peoples have been “among the first to face the direct consequences of climate change.”[711] The meeting report from the 2008 Copenhagen Conference on Indigenous Peoples and Climate Change explains further that “while indigenous peoples bear the brunt of the catastrophe of climate change, they have minimal access to resources to cope with the changes.”[712] The “survival of indigenous communities worldwide” is threatened by climate change, “even though indigenous peoples contribute the least to greenhouse emissions.”[713]

Given these facts, it is no wonder that the Native Communities and Climate Change report looked outward, which is where most of the action is and where most of the blame—for lack of a better word—can be found. Picking off the low-hanging fruit first makes sense, and is likely not going to be controversial among fellow Indian law scholars. Nonindigenous peoples and governments do make for good bad guys. The report however does include brief acknowledgment that “climate change [will require] tribes to . . . consider the long-term sustainability of [natural resource extraction].”[714] Rhetorically and factually an outward looking analysis makes sense, but there is also the need to engage with Indian complicity in what could be described as the current U.S. indifference to both climate change
and intergenerational equity.[715] As Shepard Krech III explains in The Ecological Indian,

[C]ritics who excoriate the larger society as they absolve Indians of all blame sacrifice evidence that in recent years, Indian people have had a mixed relationship to the environment. They victimize Indians when they strip them of all agency in their lives except when their actions fit the image of the Ecological Indian.[716]

The easy cases that seem to call for scholarly analysis and footnoted anger are those that involve sympathetic tribes suffering as a result of non‑Indian actions. The hard cases involve tribes imposing harmful externalities on others. A Native Alaskan village “in imminent danger of falling into the sea” because protective sea ice is melting as a result of global warming that decides to sue ExxonMobil is an easy case.[717] As the complaint makes clear, climate change could well force the villagers into environmental exile even though they “have contributed little or nothing to global warming.”[718] Let there be no mistake, Desert Rock is a hard case. A nineteen year-old, Orion Yazzie, brought the issues raised by the Navajo Nation’s choice to pursue Desert Rock into powerful relief: “Navajo sovereignty is a lot of times brought up during this debate on the power plant . . . but it is a terrible paradox that us Navajo people would be responsible for upsetting numerous other indigenous people’s [lifeways] by contributing to global warming.”[719]

VI. Conclusion

There is no satisfying answer to whether the Navajo Nation should pursue economic development through environmental destruction.[720] But the choice to do so is exactly that—a choice. Given the colonialism of federal Indian law and the determinative role powerful mining interests played in prior natural resource development, choice—not just the appearance of choice—itself is remarkable. Simply saying that Desert Rock is a remnant of a coal past is not responsive enough, partly because the United States continues its coal-fired habit, but mostly because tribal administrative needs and reservation poverty demand more than silence. Unfortunately, that is pretty much all that the Navajo Nation has gotten so far from non-Indians, politicians, and others, regardless of political leanings. Such disinterest in reservation conditions provides excuse, if not full justification, for seeking out coal-fired revenue and employment.[721] It would be great if the U.S. government permitted the Navajo Nation to act according to the will of its elected leadership, and though government policy change is improbable, it should be expected that environmental organizations not ignore Indian sovereignty by making use of federal review processes to block tribes.


* Associate Professor, American University Washington College of Law; Research Affiliate, National Poverty Center, University of Michigan; M.Phil. in Land Economics, Cambridge; J.D. magna cum laude, Harvard Law School; B.A. in Economics and English, Yale University. The assistance of the research librarians at Pence Law Library—particularly Susan Lewis‑Somers, Adeen Postar, and Renée Talley-Cuthbert—and at Diné College is gratefully acknowledged. The comments and suggestions of David Hunter, Benjamin Leff, Alexander Skibine, Bill Snape, Steve Vladeck, and Robert A. Williams, Jr. are gratefully acknowledged. Thanks also to participants at the 2010 Public Interest Environmental Law Conference; a 2009 Securities and Exchange Commission’s lunch workshop in Washington, D.C.; the 2009 Navajo Studies Conference; Alaska Inter-Tribal Council’s Alaska Museum of History and Art 2008 environmental gathering; and Valparaiso’s 2008 Law, Poverty, and Economic Inequality Conference. Finally, love as always to Elvia and now Mateo, who was born while this Article was in the editing process.

[1] As Sam Deloria explains with his characteristic directness,

We must, of course, hold the government to standards of trusteeship and identify instances in which it shirks its responsibility. But if that analytical role slips into one of invariably passing all the blame to the federal government, the economic system, or the society at large, then Indian self-determination becomes a concept of power without responsibility.

Philip S. Deloria, The Era of Indian Self-Determination: An Overview, in Indian Self-Rule: First-Hand Accounts of Indian-White Relations from Roosevelt to Reagan 191, 195 (Kenneth R. Philp ed., 1995) [hereinafter Indian Self-Rule].

[2] See Judith V. Royster, Practical Sovereignty, Political Sovereignty, and the Indian Tribal Energy Development, 12 Lewis & Clark L. Rev. 1065, 1066 (2008) (describing natural resource development as a major source of economic development on many Indian tribes’ reservations).

[3] The affection progressives have for Indians is perhaps a continuation or the next generation’s version of “the fascination of the hippie culture with the red man.” Wilcomb E. Washburn, Red Man’s Land / White Man’s Law: The Past and Present Status of the American Indian 230 (2d ed. 1995). If tribes are successful in pushing their economic development priorities against non-Indian opposition, this may change. Professor Lenora Ledwon argues that “[t]he increasing popularity of all things Indian is in inverse proportion to tribal autonomy.” Lenora Ledwon, Native American Life Stories and “Authorship”: Legal and Ethical Issues, 9 St. Thomas L. Rev. 69, 77 (1996); see also Stephen D. Osborne, Special Feature, Protecting Tribal Stories: The Perils of Propertization, 28 Am. Indian L. Rev. 203, 204–05 (2003) (noting that “Indians are hot” and that many Indians “view the continuing popularity of all things ‘Indian’ with more than a little skepticism”).

[4] Tellingly, the Diné—the language of the Navajo tribe, who call themselves “Diné,” meaning “the people”—word for white people is “Biligaana,” which is a shortened version of biłdà ahiigaani which means “those who we fight.” E-mail from Zelma King to Ezra Rosser, Assoc. Professor, Am. Univ. Wash. College of Law (Aug. 13, 2009, 08:55:29 EST) (on file with author).

[5] Jerry C. Straus, Foreword to Peter H. Eichstaedt, If You Poison Us: Uranium and Native Americans, at ix, ix (1994).

[6] Id.

[7] Id.

[8] See infra Part V.B.

[9] The focus on the Navajo Nation is not entirely coincidental. I grew up in part on the Navajo Nation and my tie to—and understanding of—the Navajo Nation is stronger than to other tribes. The same is true of my personal interests. As Professor Frank Pommersheim notes, “This notion of homeland [tied to the austere beauty of the prairie and the land] is not, of course, unique to Indians alone, and despite the obvious irony, it is valued by many non-Indians, including non-Indian residents of the reservation.” Frank Pommersheim, The Reservation as Place: A South Dakota Essay, 34 S.D. L. Rev. 246, 251 (1989).

[10] The first paragraph of Jerry C. Straus’s foreword to Peter H. Eichstaedt’s If You Poison Us: Uranium and Native Americans attests to the larger pattern of oppression:

The history of our nation’s relations with American Indians is one of ignorance, indifference, exploitation, and broken promises. When land occupied by the Indians was needed by settlers, or for some other public purpose, it was seized and the Indians herded onto apparently barren reservations. Then, when these reservation lands turned out to be rich in minerals and other resources, they were leased to mining companies, ranchers, and others, with little or no regard for the rights of the native inhabitants, their livelihood, or the long-term effects on the land. Often, only token payments were made for these extractive uses and sometimes none at all because the secretary of the interior, the designated federal trustee, failed to ensure payment.

Straus, supra note 5, at ix.

[11] Timothy Benally, Sr., Navajo Uranium Miners Fight for Compensation, In Motion Mag., Sept. 20, 1999, http://www.inmotionmagazine.com/miners.html (last visited Apr. 18, 2010). A  study conducted long after the mines closed found “excess mortality for lung cancer, pneumoconioses and other respiratory diseases, and tuberculosis for Navajo uranium miners.” Robert J. Roscoe et al., Mortality Among Navajo Uranium Miners, 85 Am. J. Pub. Health 535, 539 (1995). For example, lung cancer or various forms of fibrosis killed 133 of the 150 Navajo uranium miners who worked at Kerr-McGee’s Shiprock uranium mine until 1970. Saleem H. Ali, Mining, the Environment, and Indigenous Development Conflicts, at xx (2003); see also Jessica Barkas Threet, Testing the Bomb: Disparate Impacts on Indigenous Peoples in the American West, the Marshall Islands, and in Kazakhstan, 13 U. Balt. J. Envtl. L. 29, 32 (2005) (“Driven by poverty, and ignorant of the risks to their health, tribal members made up the majority of the miner population. They have been stricken with lung cancer and other ailments from working in the midst of uranium dust and radon gas, often with little or no filtration systems.” (footnote omitted)).

[12] Memories Come to Us in the Rain and the Wind: Oral Histories and Photographs of Navajo Uranium Miners & Their Families 8 (3d ed. 2000) (quoting Floyd Frank of Oakspring, Arizona). A suit by former miners alleging that the United States negligently regulated uranium mining given its awareness of the health risks was dismissed because of the national security imperative associated with such uranium mining. Begay v. United States, 591 F. Supp. 991, 1011–13 (D. Ariz. 1984) (providing a history of the health studies conducted). The United States Supreme Court later held that given the national interests at stake, the tribal court exhaustion rule did not apply in a suit against a uranium mining company by Navajos living near an open pit mine who used polluted waters for a number of things, including drinking. El Paso Natural Gas Co. v. Neztsosie, 526 U.S. 473, 477, 486–88 (1999).

[13] Keith Schneider, A Valley of Death for the Navajo Uranium Miners, N.Y. Times, May 3, 1993, at A1 (“The Government promised good wages but, Federal records show, did nothing to warn the men of the excessive levels of radiation in the uranium mines.”). For a brief overview of uranium mining and its consequences for Navajo miners, see Doug Brugge & Rob Goble, A Documentary History of Uranium Mining and the Navajo People, in The Navajo People and Uranium Mining 25 (Doug Brugge et al. eds., 2006). For a more complete account, see Eichstaedt, supra note 5.

[14] Doug Brugge et al., “So A Lot of the Navajo Ladies Became Widows, in The Navajo People and Uranium Mining, supra note 13, at xv, xv (noting additionally that there the Navajo Nation had four uranium mills).

[15] Judy Pasternak, Blighted Homeland: A Peril that Dwelt Among the Navajos, L.A. Times, Nov. 19, 2006, at 1, available at 2006 WLNR 20073872 (providing the first in a four-part series published by the Los Angeles Times looking at the effects of uranium mining on the Navajo reservation). A photo of a hogan, the traditional Navajo house, with a contaminated foundation is included in the most recent Navajo Nation five-year contamination plan as an example of the legacy of uranium mining. U.S. Envtl. Prot. Agency, Health and Environmental Impacts of Uranium Contamination in the Navajo Nation: Five-Year Plan 2 (2008), available at http://www.epa.gov/region09/superfund/navajo-nation/pdf/NN-5-Year-Plan-June-12.pdf; see also James M. Grijalva, Closing the Circle: Environmental Justice in Indian Country 62–69 (2008) (describing the problem of leaking uranium tailings near Church Rock, New Mexico, and subsequent proposals to further develop mining in the area); Bill Donovan, Navajos Lack Cash to Study Tainted Homes, Ariz. Republic, Apr. 26, 1985, at B1 (reporting on the lack of funding to evaluate homes “that may have been built out of abandoned uranium-mill tailings,” and on a United States Department of Housing and Urban Development decision to reverse, once the problem’s large extent was known, a decision to provide emergency funding to relocate people whose homes were radioactive).

[16] Diné Natural Resources Protection Act of 2005, Navajo Nation Code Ann. tit. 18, §§ 1301–1303 (West 2005).

[17] Navajo Nation Council Res. CAP-18-05 (2005), available at http://www.navajocourts.org/ Resolutions/CAP-18-05.pdf; see also Navajo Nation Code Ann. tit. 18, § 1303 (West 2005).

[18] Navajo Nation Council Res. CAP-18-05 § 1301. “Diné Bi Beenahaz’áanii — the Foundation of the Diné, Diné Law, and Diné Government” became law on November 13, 2002. See Navajo Nation Council Res. CN-69-02 (2002), available at http://www.navajocourts.org/Resolutions/ CN‑69-02Dine.pdf (codified at Navajo Nation Code Ann. tit. 1, §§ 201–206 (West 2005)). The codification of Navajo customary law into Navajo Fundamental Law is analyzed in Kenneth Bobroff, Diné Bi Beenahaz’áanii: Codifying Indigenous Consuetudinary Law in the 21st Century, Tribal L.J., 2004–2005, http://tlj.unm.edu/tribal-law-journal/articles/volume_5/_dine_ bi_beenahazaanii__codifying_indigenous_consuetudinary_law_in_the_21st_century/index.php (last visited Apr. 18, 2010).

[19] Navajo Nation Council Res. CAP-18-05 § 3.

[20] For more on the history of uranium mining on the reservation and the relationship between the ban and the Bush Administration’s energy policies, see Bradford D. Cooley, Note, The Navajo Uranium Ban: Tribal Sovereignty v. National Energy Demands, 26 J. Land Resources & Envtl. L. 393, 393–97 (2006).

[21] In 2006, the United States Nuclear Regulatory Commission denied a petition to reconsider the final environmental impact statement approving Hydro Resources Inc.’s proposed uranium mines bordering the reservation at Church Rock and Crownpoint in light of the Diné Natural Resources Protection Act. Hydro Resources, Inc., 64 N.R.C. 417 (2006); see also Cindy Yurth, New Life for the Yellow Ore?, Navajo Times (Window Rock, Ariz.), Mar. 19, 2009, http://navajotimes.com/news/2009/0309/031909uranium.php (last visited Apr. 18, 2010) (discussing the uranium claims that surround the Navajo Nation).

[22] Judy Pasternak, Blighted Homeland: Mining Firms Again Eyeing Navajo Land, L.A. Times, Nov. 22, 2006, http://articles.latimes.com/2006/nov/22/nation/na-navajo22 (last visited Apr. 18, 2010) (internal quotation marks omitted) (quoting Mark Pelizza, Vice President of Uranium Resources Inc.).

[23] See Press Release, U.S. Envtl. Prot. Agency, EPA Issues Air Permit for Desert Rock Energy Facility (July 31, 2008), http://yosemite.epa.gov/opa/admpress.nsf/d0cf6618525a9efb852 57359003fb69d/8331e0972492f17c85257497005a37fb!OpenDocument (last visited Apr. 18, 2010).

[24] For overviews of the Desert Rock proposal, see id. (describing the project); San  Juan  Citizens Alliance, Desert Rock Power Plant, http://www.sanjuancitizens.org/air/ desertrock.shtml (last visited Apr. 18, 2010) (same); Sithe Global, Desert Rock Energy Project, http://www.sitheglobal.com/projects/desertrock.cfm (last visited Apr. 18, 2010) (same).

Given the costs of transporting coal, “[m]ine-mouth conversions to electricity or ‘clean’ synthetic fuels appear to be practical means of employing [western coal] as their low energy‑to‑weight ratios usually prohibit long-distance transportation.” Donald W. Clements, Recent Trends in the Geography of Coal, 67 Annals Ass’n Am. Geographers 109, 119 (1977).

[25] The Blackstone Group purchased its 80% ownership stake in Sithe Global in 2005, after the Desert Rock proposal had begun. Press Release, Sithe Global, Blackstone Capital Partners, Together with Bruce Wrobel and Management, Acquires a Majority Interest in Sithe Global Power, a Leading Power Development Company (Oct. 5, 2005), available at http://www.sithe
global.com/press/BlackstonePressRelease.pdf. Blackstone is owned by Stephen A. Schwarzman, number 53 on the Forbes list of the 400 richest people in America in 2008. Stephen A. Schwarzman Profile, Forbes, http://people.forbes.com/profile/stephen-a-schwarzman/78312 (last visited Apr. 18, 2010). His total compensation in 2008 was over $1.3 billion. Id.; see also Blackstone’s Chief Received $350 Million in Pay in 2007, N.Y. Times, Mar. 13, 2008, at C2 (noting that amount does not include $4.77 billion in stock received when Blackstone went public, $1.2 billion of which immediately vested).

[26] Desert Rock Energy Co., Navajo Nation, http://www.desertrockenergyproject.com/navajo_
nation.htm (last visited Apr. 18, 2010).

[27] The Navajo Nation would have the option of obtaining an ownership stake of “25% outright, up to an aggregate of 49% depending on extent of other equity investment.” Letter from Joe Shirley, Jr., President, Navajo Nation, to Stephen L. Johnson, Adm’r, U.S. Envtl. Prot. Agency 2 (Sept. 20, 2007), available at http://navajo-nsn.gov/News%20Releases/George%20
Hardeen/July08/State%20of%20the%20Navajo%20Nation%20Address%20%20July%2021%202008.pdf.

[28] Joe Shirley, Jr., President, Navajo Nation, State of the Navajo Nation Address at the 21st Navajo Nation Council 5 (July 21, 2008), available at http://opvp.org/cms/kunde/rts/opvporg/ docs/817209846-07-25-2008-17-00-46.pdf.

[29] See infra notes 372–75 and accompanying text.

[30] Webcast: Conference on Indian Nations and Institution Building, held by the American University Washington College of Law (Feb. 16, 2009), available at http://media.wcl.american.edu/
Mediasite/Viewer/?peid=2fa4f3dacd5948d585262246a90504bb (quoting Joe Shirley, Jr., President, Navajo Nation, from minutes 45:45–47:20 in the webcast). For a representative example of President Shirley’s support of Desert Rock, see Letter from Joe Shirley, Jr., President, Navajo Nation, to Gerardo C. Rios, Chief, Air Permits Office, U.S. Envtl. Prot. Agency (Sept. 10, 2004) (on file with author) (“The Office of the President and Vice President of the Navajo Nation fully support the Desert Rock project.”).

[31] Navajo opposition to uranium seems to be based primarily on the health effects experienced by miners and not on ideological opposition to nuclear power. See infra notes 430–45 and accompanying text.

[32] See Eichstaedt, supra note 5, at 14.

[33] Treaty Between the United States of America and the Navajo Tribe of Indians, U.S.‑Navajo, June 1, 1868, 15 Stat. 667 [hereinafter 1868 Treaty].

[34] Office of Gen. Counsel, U.S. Comm’n on Civil Rights, Demographic and Socio‑Economic Characteristics of the Navajo 4 (1973).

[35] The importance of place to the Diné comes across from the Gary Witherspoon’s description:

Navajoland is the Holy Land of the Navajo people. It is circumscribed by sacred mountains, and is described as being beautiful. Essential parts, as well as the land itself, are called mother. For a Navajo, there is no safer, more secure, and more wonderful place to be than close to Earth Mother within the boundaries of the sacred mountains, which represent parts of her body. . . .

Some non-Navajo have seen Navajoland as a bleak, lonely, and forbidding place. On the contrary, Navajoland is thought by its people to be as sacred and secure as motherhood itself.

Gary Witherspoon, Navajo Kinship and Marriage 68 (1975); see also Office of Gen. Counsel, supra note 34, at 4 (noting the relationship between the Diné creation story and “[t]he land between these four mountains [that] is the area the Navajo calls home”).

[36] Office of Gen. Counsel, supra note 34, at 8, 10.

[37] The land base of the Navajo Nation consists not only of land included in the 1868 treaty but also land subsequently added by various acts of Congress, judicial opinions, and a long series of executive orders. J. Lee Correll & Alfred Dehiya, Anatomy of the Navajo Indian Reservation: How It Grew (rev. ed. 1978). The need for Navajos to have more land in order to survive was colorfully described in an 1879 letter written by John C. Pyle, an Indian agent:

The Navajo would not exchange his desert home for the most favored spot elsewhere and if the Reservation is found to be too limited for his necessities, why not give him more desert? But I suppose it would be worse than folly to ask for more territory for any tribe, however deserving, from a Government that does not secure to the Indian the peaceful possession of lands already guaranteed to him by solemn treaty stipulation.

Dane Coolidge & Mary Roberts Coolidge, The Navajo Indians 247 (1930) (quoting from John C. Pyle’s 1879 letter to the Bureau of Indian Affairs at Washington).

The Navajo Nation has also used primarily mining revenues to purchase additional land. See Office of General Counsel, supra note 34, at 10. One particular tribal purchase, that of Big Boquillas Ranch, would ultimately lead then-Tribal Chairman (the title was subsequently changed to Navajo Nation President) Peter MacDonald to be thrown out of office and imprisoned for accepting bribes connected to the land deal. See United States v. Brown, 763 F. Supp. 1518, 1520–24 (D. Ariz. 1991) (containing a brief overview of the nature of the bribery), aff’d, 979 F.2d 1380 (9th Cir. 1992); Navajo Nation v. MacDonald, 885 P.2d 1104, 1109, 1113 (1994) (affirming liability in a civil suit following the criminal conviction of defendants on 14 counts). For Peter MacDonald’s side of the story, see Peter MacDonald, The Last Warrior: Peter MacDonald and The Navajo Nation 278–341 (1993). The Navajo Nation recently announced plans to build a $200 million, 85-megawatt wind farm on the Big Boquillas Ranch. Cyndy Cole, Navajo Wind Farm Set, Ariz. Daily Sun, Dec. 28, 2009, http://azdailysun.com/ news/local/article_0a9abe65-e473-50dc-aa78-464f4b6b9210.html (last visited Apr. 18, 2010).

[38] Richard White, The Roots of Dependency: Subsistence, Environment, and Social Change Among the Choctaws, Pawnees, and Navajos 225 (1983) (describing the reservation); Div. of Econ. Dev., Navajo Nation, An Overview of the Navajo Nation—Demographics, http://www.navajobusiness.com/fastFacts/demographics.htm (last visited Apr. 18, 2010) (providing population figures).

[39] Navajo Nation, History Page, http://www.navajo.org/history.htm (last visited Apr. 18, 2010) (proudly proclaiming that “Navajo government has evolved into the largest and most sophisticated form of American Indian government”); see also Robert H. Keller & Michael F. Turek, American Indians & National Parks 186 (1998) (“The continued vitality of the Navajo language, survival of traditional culture, and rich legends combine with a sense of place to produce a tribal sovereignty beyond rhetoric. Navajos own and control their homeland.” (emphasis added)).

[40] Harrison Lapahie, Jr., Window Rock, http://www.lapahie.com/Window_Rock_Capitol.cfm (last visited Apr. 18, 2010); Navajo Nation Office of the President & Vice President, President of the Navajo Nation, http://www.opvp.org/content.asp?CustComKey=33998&CategoryKey=33999 &pn=Page&DomName=opvp.org (last visited Apr. 18, 2010).

[41] Treaty Between the United States of America and the Navajo Tribe of Indians, U.S.‑Navajo, Sept. 9, 1849, 9 Stat. 974 [hereinafter 1849 Treaty]; 1868 Treaty, supra note 33.

[42] For more on the Navajo Long Walk, see generally L.R. Bailey, The Long Walk: A History of the Navajo Wars, 1846–68 (1964); The Diné of the E. Region of the Navajo Reservation, Oral History Stories of the Long Walk: Hwéeldi Baa Hané (1991).

Some Diné, including members of my step-mother’s family, avoided capture by hiding in the mountains and canyons in northern parts of Diné territory. Though they could only come out of hiding and reunite with those at Fort Sumner following the treaty signing, those who avoided the long walk played an important role in revitalizing the tribe’s economy after 1868. Peter Iverson, Diné: A History of the Navajos 57 (2002).

[43] Of the more than eight thousand Navajos “detained at Bosque Redondo” in 1864, two thousand died by 1868. Office of General Counsel, supra note 34, at 7–8.

[44] 1868 Treaty, supra note 33, arts. II, XXIII, 15 Stat. at 668, 671. Author’s note: Navajo is usually spelled with a j, but sometimes is spelled with an h; both spellings refer to the same tribe.

[45] The U.S. Congress formally ended the practice of making Indian treaties in 1871, though this attempt by Congress to limit the government’s Indian treaty-making powers is arguably unconstitutional. See David P. Currie, Indian Treaties, 10 Green Bag 2d 445, 445, 449–51 (2007).

[46] Grijalva, supra note 15, at 77 (describing the detrimental approach to natural resource extraction experienced by tribes generally).

[47] According to Professor James M. Grijalva, whose work on environmental justice informs much of this Article, business and governmental interests jointly sought Indian natural resources:

The federal government also induced non-Indian natural resource development companies to locate in Indian country in the mid-1900s. As trustee, the federal government was legally obligated to manage tribal resources for the benefit of the tribes, but on occasion its zeal for revenue and the political connections of non-Indian companies led to below market lease and royalty payments. Prospects for increased profit margins, possible insulation from state taxation, and comparatively weak federal regulation helped spur strip and pit mines, clear-cut timber harvests, and power plants.

Id.

[48] As Robert H. Keller and Michael F. Turek explain, “Anglo-Americans once considered the Southwest the most inhospitable and uninhabitable quadrant of the United States, a perception that perhaps explains the large size of the Navajo Reservation.” Keller & Turek, supra note 39, at 188; see also J.W. Hoover, Navajo Land Problems, 13 Econ. Geography 281, 284 (1937) (“From the standpoint of utilization, the Navajo country is marginal land.”).

In particular, the Navajo Nation did not suffer from allotment the way other tribes did, even though it was contemplated in the 1868 treaty. See 1868 Treaty, supra note 33, art. V,
15 Stat. at 668. Devised as a strategy to turn reservation Indians into yeoman farmers and to turn over surplus land to non-Indians, allotment lasted from 1881 to 1934 and resulted in tribal land loss without noticeable economic gains. See Judith V. Royster, The Legacy of Allotment, 27 Ariz. St. L.J. 1, 6 (1995). The leading article on the lasting effects of allotment is Royster, supra.

The limited agricultural utility of the reservation means that the on-reservation Diné population vastly exceeds the number of people—estimated at 35,000—who could be supported at a subsistence level through agriculture. Kent Gilbreath, Red Capitalism: An Analysis of the Navajo Economy 4 (1973).

[49] The Treaty of September 9, 1849, authorized trading posts among the Navajo. 1849 Treaty, supra note 41, art. VIII, 9 Stat. at 975. Trading posts were and are an important part of reservation life:

The Reservation trading post became one of the most necessary and influential institutions of the Reservation system. The Navaho Reservation was so vast and so isolated that until the early [1930s], government officials had very little contact with the Indians, leaving the trader as the most important, often the only white man in the native community.

Jesse L. Nusbaum, Introduction to Elizabeth Compton Hegemann, Navaho Trading Days, at vii, ix (1963) (providing a first-person account of trading post life); see also Frances Gillmor & Louisa Wade Wetherill, Traders to the Navajos: The Story of the Wetherills of Kayenta (1934) (providing a narrative of a trader family on the reservation). In 1968, Southwestern Indian Development, Inc., under the leadership of future Navajo President Peterson Zah, published a highly critical report on trading post operators, their pricing policies, and the Bureau of Indian Affair’s lack of oversight:

The institution of the trading post, admittedly, has played an essential part in the development of modern Indian society in its role as mediator between the Navajo and Anglo world, yet this does not give them the unquestioned “right” to exploit and dominate to the fullest extent those very people who provided their livelihood.

Sw. Indian Dev., Inc., Traders on the Navajo Reservation: Draft Report 26 (1970) (on file with Rogers College of Law Library, University of Arizona).

The land upon which their trading posts or other businesses sit, as well as the land held by many religious organizations, is often an island of fee land surrounded by trust land. These islands of non-Indian fee land create special problems for tribes seeking to regulate conduct within their reservation, and the Supreme Court has blocked various assertions of tribal sovereignty over these businesses. See Atkinson Trading Co. v. Shirley, 532 U.S. 645 (2001) (preventing the Navajo Nation from assessing a hotel occupancy tax on a non-Indian hotel located on the Navajo Nation despite significant ties between the business and the tribe).

[50] Keller & Turek, supra note 39, at 186 (“Once considered marginal terrain, Navajo land contains coal, oil, and gas, plus 500,000 acres of timber.”). What is true for the Navajo Nation also holds for Indian landholdings in general. Russel Lawrence Barsh, Indian Resources and the National Economy: Business Cycles and Policy Cycles, in Native Americans and Public Policy 193, 215 (Fremont J. Lyden & Lyman H. Legters eds., 1992) (noting the relative richness of Indian-held oil, coal, and uranium natural resources); see also Carol A. Markstrom & Perry H. Charley, Psychological Effects of Technological/Human-Caused Environmental Disasters: Examination of the Navajo People and Uranium, in The Navajo People And Uranium Mining, supra note 13, at 89, 103 (referring to natural resource extraction as a form of colonialism and noting that “[t]he irony is that these lands were not known to be resource-rich at the time reservation lands were allotted to tribes. Indeed, in many cases, seemingly the least inhabitable lands were designated for reservations” (emphasis added)).

[51] M.R. Campbell & H.E. Gregory, The Black Mesa Coal Field, Arizona, in Contributions to Economic Geology (Short Papers and Preliminary Reports): Part II.—Mineral Fuels 229, 229 (U.S. Geological Survey, Bulletin 431, 1909).

[52] Id.

[53] Id. at 236.

[54] Mark Schoepfle et al., Navajo Attitudes Toward Development and Change: A Unified Ethnographic and Survey Approach to an Understanding of Their Future, 86 Am. Anthropologist 885, 885 (1984).

[55] Known as the 1882 Executive Order Area or Joint Use Area, the conflict over which tribe and whose tribal members were entitled to live in the area evolved into the multigenerational Navajo-Hopi land dispute. For an overview of the history and legal cases involved in the dispute, see Eric Cheyfitz, Theory and Practice: The Case of the Navajo-Hopi Land Dispute, 10 Am. U. J. Gender Soc. Pol’y & L. 619, 623–30 (2002); see also David M. Brugge, The Navajo-Hopi Land Dispute: An American Tragedy 2, 3, 47, 55, 62–63 (1994) (providing a history of the dispute).

[56] Brian Jackson Morton, Coal Leasing in the Fourth World: Hopi and Navajo Coal Leasing, 1954–1977, at 1 (May 17, 1985) (unpublished Ph.D. dissertation, University of California, Berkeley) (on file with Boise State University Library) (citing U.S. Dep’t of the Interior, Southwest Energy Study: Report of the Coal Resources Work Group app. J (1972)).

[57] Colleen O’Neill, Working the Navajo Way: Labor and Culture in the Twentieth Century 30–54 (2005) (describing the development and characteristics of truck mines of the 1930s).

[58] Morton, supra note 56, at 7–9. This is not to say that coal exploitation only began in the last century. Philip Reno, Mother Earth, Father Sky, and Economic Development: Navajo Resources and Their Use 106 (1981) (“Remains of ancient campsites indicate that coal was burned one thousand years ago by Indian people . . . .”). Between 1300 and 1600 A.D., Black Mesa “production may have totaled 100,000 tons.” Donald L. Baars, Navajo Country: A Geology and Natural History of the Four Corners Region 171 (1995).

[59] Morton, supra note 56, at 8.

[60] See id. at 9–10.

[61] Id. at 56.

[62] Winona LaDuke, Recovering the Sacred: The Power of Naming and Claiming 35 (2005).

[63] Black Mesa Def. Fund et al., “. . . . . Like Ripping Apart St. Peter’s, In Order to Sell the Marble., N.Y. Times, May 20, 1971, at 31 (paid advertisement).

[64] Id.

[65] Id. In 1974, Reid Chambers and Monroe Price wrote of the “considerable controversy” surrounding “the development of immense fossil-fuel power plants and the strip mining of coal for these plants . . . . designed to meet the needs of Tucson, Phoenix, Los Angeles, Albuquerque, and other southwestern metropolises.” Reid Peyton Chambers & Monroe E. Price, Regulating Sovereignty: Secretarial Discretion and the Leasing of Indian Lands, 26 Stan. L. Rev. 1061, 1066 (1974); see also Floyd Harvey Dove, Groundwater in the Navajo Sandstone: A Subset of “Simulation of the Effects of Coal-Fired Power Developments in the Four Corners Region” 1 (Nov. 21, 1973) (unpublished Ph.D dissertation, University of Arizona) (on file with Pence Law Library, American University) (“Economic progress may cause change in the immediate environment but may also accelerate environmental change in areas remote from the central core of economic activity. Such is the case . . . in the Southwest portion of the United States.”).

[66] Black Mesa Def. Fund et al., supra note 63.

[67] Carol J. McCabe & Hester Lewis, U.S. Comm’n on Civil Rights, The Navajo Nation: An American Colony 17 (1975); Reno, supra note 58, at 123 (noting that oil was first found near Hogback in 1922).

[68] See infra notes 123–24 and accompanying text.

[69] Kathleen P. Chamberlain, Under Sacred Ground: A History of Navajo Oil 1922–1982, at 29 (2000).

[70] Id. at 29–30. The approval of the leases came only after two similarly purposed prior Bureau of Indian Affairs–directed gatherings of Navajo men voted to reject the lease; the first such group voted 75 to zero against the proposed mining lease. Jerry Mander, In the Absence of the Sacred: The Failure of Technology and the Survival of the Indian Nations 278 (1991).

[71] Witherspoon, supra note 35, at 69; see also McCabe & Lewis, supra note 67, at 17 (noting that the tribal council was “created in part so that oil companies would have some legitimate representatives of the Navajos through whom they could lease reservation lands on which oil had been discovered”). “[T]he urge to establish a puppet government as a medium for control of the Tribe” had been around since internment at Fort Sumner, but that first attempt failed. Robert W. Young, A Political History of the Navajo Tribe 36 (1978). The Washington Office of the Bureau of Indian Affairs in 1915, upon hearing word from an agent based on the reservation that a council might be forming (the agent ended up being proven wrong), wrote the agent that “so long as the council can be used and controlled . . . it should be of great benefit to the Indians.” Lawrence C. Kelly, The Navajo Indians and Federal Indian Policy: 1900–1935,
at 49 (1968) (internal quotation marks omitted). The effort to form a new council in 1923 was sparked by the decision of Navajos called to a March 1922 gathering to not approve new leases. See id. at 52.

What was true of the formation of the Navajo Tribal Council holds for other tribes as well: During the New Deal, “tribal councils were organized largely to ‘rubberstamp’ the [Bureau of Indian Affair’s] approval of mineral leasing on the reservation.” Rebecca Tsosie, Tribal Environmental Policy in an Era of Self-Determination: The Role of Ethics, Economics, and Traditional Ecological Knowledge, 21 Vt. L. Rev. 225, 301 (1996).

[72] Ward Churchill, American Indian Self-Governance: Fact, Fantasy, and Prospects for the Future, in American Indian Policy: Self-Governance and Economic Development 37, 41 (Lyman H. Legters & Fremont J. Lyden eds., 1994) [hereinafter American Indian Policy]. Given that the University of Colorado fired Ward Churchill on what the university claims are academic misconduct grounds, in citing his work it is perhaps important to also include the citations tied to that controversy. See Report of the Investigative Committee of the Standing Committee on Research Misconduct at the University of Colorado at Boulder Concerning Allegations of Academic Misconduct Against Professor Ward Churchill 3, 94 (2006), available at http://www.colorado.edu/news/reports/churchill/download/WardChurchillReport.pdf; Ward Churchill, Summary of the Fallacies in the University of Colorado Investigative Committee Report of May 9, 2006 (2006), available at http://wardchurchill.net/files/ churchill052006.doc; Eric Cheyfitz, Framing Ward Churchill: The Political Construction of Research Misconduct, Works & Days, 2008–09, at 231 (providing a strong defense of Churchill and a critique of the committee’s report); see also John P. LaVelle, The General Allotment Act “Eligibility” Hoax: Distortions of Law, Policy, and History in Derogation of Indian Tribes, Wicazo Sa Rev., Spring 1999, at 251, 251–52 (1999) (providing a critique of Churchill’s scholarship that pre-dated the Investigative Committee’s report and was used by the committee); Scott Jaschik, Ward Churchill Fired, Inside Higher Ed, July 25, 2007, http://www.insidehighered.com/news/2007/07/25/churchill (last visited Apr. 18, 2010) (providing an overview of the allegations and events).

[73] George A. Boyce, When Navajos Had Too Many Sheep: The 1940s, at 89 (1974) (quoting Jake Morgan).

[74] See generally Chamberlain, supra note 69.

[75] Id. at 30.

[76] Id. (internal quotation marks omitted).

[77] Id. at 32.

[78] Id. at 36. Chamberlain subsequently describes this as a “far-sighted choice.” Id. at 84. The ability of tribes to make per capita payments of funds held in trust by the Secretary of the Interior was reaffirmed by Congress in 1983. Pub. L. No 98-64, 97 Stat. 365 (1983). As early as a 1968, a Harvard Law Review note highlighted distribution of tribal resources to individuals as “a particularly divisive issue.” Warren H. Cohen & Philip J. Mause, Note, The Indian: The Forgotten American, 81 Harv. L. Rev. 1818, 1827 (1968). More recently, gaming has exacerbated the challenges inherent in per capita payments, and membership issues come to the fore when per capita distributions become as significant as they can be with a successful casino. Kathryn R.L. Rand & Steven A. Light, Virtue or Vice? How IGRA Shapes the Politics of Native American Gaming, Sovereignty, and Identity, 4 Va. J. Soc. Pol’y & L. 381, 422 (1997) (“Tribal membership often becomes an issue. Not surprisingly, everyone wants a part of the jackpot of Indian gaming.”). Such payments have inspired some to call for limits on tribal sovereignty. E.g., Eric Reitman, Note, An Argument for the Partial Abrogation of Federally Recognized Indian Tribes’ Sovereign Power Over Membership, 92 Va. L. Rev. 793, 801–30 (2006) (arguing that tribal authority over membership should be limited to protect tribal members from being wronged by tribal disenrollment decisions often driven by per capita payments). Contra Carole Goldberg, American Indians and “Preferential” Treatment, 49 UCLA L. Rev. 943, 958–66 (2002) (defending tribal sovereign authority over membership).

[79] Chamberlain, supra note 69, at 36.

[80] Morton, supra note 56, at 272 (basing amounts on figures from 1958 and noting that the peak in oil revenues to the tribe occurred in 1957). The actual royalty amount may be higher. See Robert S. McPherson & David A. Wolff, Poverty, Politics, and Petroleum: The Utah Navajo and the Aneth Oil Field, 21 Am. Indian Q. 451, 454 (1997) (giving a figure of $34.5 million in royalties from the Aneth oil field alone in 1956).

[81] Chamberlain, supra note 69, at 93 (stating Navajos established a college scholarship program and provided money for the needy, irrigation and soil conservation projects, and renovation of chapter houses).

[82] Reno, supra note 58, at 124.

[83] Baars, supra note 58, at 162.

[84] McPherson & Wolff, supra note 80, at 454.

[85] Barsh, supra note 50, at 211 (providing a percentage based on the period from 1880–1970). Oil companies argued that they should not have to pay more for the higher quality of Hogback and Rattlesnake crude because, they claimed, “the high quality was a curse, not a blessing” because “high gas content made the petroleum more volatile.” Chamberlain, supra note 69, at 54; see also Michael Joseph Francisconi, Kinship, Capitalism, Change: The Informal Economy of the Navajo, 1868–1995, at 70 (1998) (reporting that for the over $2 billion exported from the Navajo Nation by 1978, the tribe had received only $300 million).

[86] In 1933 Congress expanded the reservation, adding the Aneth strip/extension to the existing reservation and providing for the 37.5% dedication of royalties. Act of Mar. 1, 1933, 72 Pub. L. No. 403-160, 47 Stat. 1418 (1933). Because the dedication requirement of the 1933 Act was not actually leading to money reaching area Navajos, Congress confirmed the requirement in a 1968 amendment to the Act. Act of May 17, 1968, 90 Pub. L. No. 306, 82 Stat. 121 (1968).

[87] Richard J. Ansson, Jr., Comment, Protecting Profits Derived from Tribal Resources: Why the State of Utah Should Not Have the Power to Tax Non-Indian Oil and Gas Lessees on the Navajo Nation’s Aneth Extension: Texaco, Exxon, and Union Oil v. San Juan County School District—A Case Study, 21 Am. Indian L. Rev. 329, 345 (1997) (noting that an audit in 1992 found that of $61 million that should have been in a royalty-based trust fund from payments from 1960–1990, only $9.5 million could be properly accounted for and “the state confessed that it had recklessly squandered $51.5 million”); McPherson & Wolff, supra note 80, at 460–61.

[88] Chamberlain, supra note 69, at 111.

[89] Id.; McPherson & Wolff, supra note 80, at 458–60 (discussing the first moments of the occupation).

[90] McPherson & Wolff, supra note 80, at 463.

[91] Id. at 460 (internal quotation marks omitted).

[92] Id. at 464. Prior to the occupation, the Navajo Times had reported similar rock throwing by residents. Chamberlain, supra note 69, at 112.

[93] Reno, supra note 58, at 126 (internal quotation marks omitted) (describing this as the complaint of Aneth occupiers).

[94] Chamberlain, supra note 69, at 65 (stating the resolution failed to have effect because the council’s ability to cancel such leases depended on the companies being in breach of contract).

[95] The council may have been dissatisfied that one of the promises made in return for approving the leases—that they “would receive government aid in securing new lands”—had not been kept. Kelly, supra note 71, at 69. Despite its democratic and institutional failings, the tribal council “was not simply a ‘yes-man’s’ organization.” Id. at 194.

[96] Writing of reorganization-era mineral leasing, Professor Judith Royster explains, “[T]ribes had more authority over resource development on paper than in practice.” Judith V. Royster, Practical Sovereignty, Political Sovereignty, and the Indian Tribal Energy Development and Self‑Determination Act, 12 Lewis & Clark L. Rev. 1065, 1074 (2008).

[97] Chamberlain, supra note 69, at 113.

[98] See Francisconi, supra note 85, at 69 (“Oil had a history similar to coal.”).

[99] Charles F. Wilkinson, Home Dance, the Hopi, and Black Mesa Coal: Conquest and Endurance in the American Southwest, 1996 BYU L. Rev. 449, 467–69 (1996).

[100] Indian Reorganization Act, ch. 576, 48 Stat. 984 (codified as amended at 25 U.S.C. §§ 461–479 (2006)).

[101] See, e.g., Robert N. Clinton, Redressing the Legacy of Conquest: A Vision Quest for a Decolonized Federal Indian Law, 46 Ark. L. Rev. 77, 104 (1993) (listing features of the Indian Reorganization Act).

[102] See id.

[103] See Wilkinson, supra note 99, at 457–58.

[104] Id. at 458.

[105] Id. (“The 1936 election was a watershed event. The creation of a Tribal Council eliminated the impediments to mineral leasing that had previously flowed from village autonomy and a lack of any written governmental structure. Most basically, there was now one official body to sign a lease.”). Mining companies were the beneficiaries of this change. See Suzanne Gordon, Black Mesa: The Angel of Death 22 (1973) (reporting that, after being asked how the company could ignore the true Hopi leadership, a Peabody public relations vice president, William L. Stockton, “commented that it would be too difficult for Peabody to go to every village chief and get his permission to lease the land. Peabody needed a quick, easy way of securing leases, and the Tribal Council, created by the Department of the Interior, was a convenient solution”).

[106] Wilkinson, supra note 99, at 459 (internal quotation marks omitted).

[107] Pat Sekaquaptewa, Dir., Native Nations Law & Policy Inst., Univ. of Cal.–L.A., Statement at the Meeting of the National Congress of American Indians (Nov. 17, 2006), in Conference Transcript: The New Realism: The Next Generation of Scholarship in Federal Indian Law, 32 Am. Indian L. Rev. 1, 121 (2007).

[108] See, e.g., Gordon, supra note 105, at 17 (“Hopi leaders and a great majority of the tribe have boycotted the Tribal Council, which has brought not democracy, but rather great divisions in the tribe between ‘Progressives,’ who favor the white man’s ways, and the ‘Traditionals,’ who prefer the old ways.”).

[109] Healing v. Jones, 210 F. Supp. 125, 134 (D. Ariz. 1962) (dividing the mineral rights to the contested portions of the 1882 Executive Order area equally between the Hopi and Navajo tribes). For more on the maneuverings of the Navajo and Hopi attorneys that led up to Healing v. Jones, see John Redhouse, Geopolitics of the Navajo Hopi ‘Land Dispute’ (1985), http://www.angelfire.com/art/hoganview/Geopol.htm (last visited Apr. 18, 2010).

[110] Wilkinson, supra note 99, at 459–67, 469–72.

[111] Lomayaktewa v. Hathaway, 520 F.2d 1324, 1327 (9th Cir. 1975).

[112] Lomayaktewa, 520 F.2d at 1326. The court took the position of energy companies who explained Hopi opposition as “dissidents spurred on by outside agitators.” Gordon, supra note 105, at 19 (quoting David Fogarty, Vice President of Southern California Edison, as saying “in any organized society there is always one sector that’s unhappy with the leadership, elected or appointed, or however they got there” (internal quotation marks omitted)).

[113] Wilkinson, supra note 99, at 471.

[114] Id. at 471, 480.

[115] Katosha Belvin Nakai, When Kachinas and Coal Collide: Can Cultural Resources Law Rescue the Hopi at Black Mesa?, 35 Ariz. St. L.J. 1283, 1290 (2003) (giving water usage amounts); Wilkinson, supra note 99, at 480 (comparing the water usage rates under the original lease, $1.67 per acre-foot, and the second lease, $300 per acre-foot). The coal slurry “is approximately 275 miles in extent” and moves “at a velocity of about 5 miles per hour.” Dove, supra note 65, at 43 (citing Bureau of Reclamation, U.S. Dep’t of the Interior, Environmental Statement, Navajo Project 87 (1972)). The slurry is “the only one of its kind in the United States.” Ali, supra note 11, at 106. In order to supply the necessary water, six Peabody wells ranging from 3535 to 3737 feet deep pump Black Mesa groundwater. Dove, supra note 65, at 44. The annual water use stands at “1.3 billion gallons of pristine water.” LaDuke, supra note 62, at 38. As Philip Reno describes, “the water as well as the coal is being mined and shipped away.” Reno, supra note 58, at 59; see also Nancy Greig, Secondary Business and Job Development Related to the Coal Gasification Plants and the Navajo Indian Irrigation Project 101 (1974) (on file with U.C. Berkeley Library) (noting that water used by coal companies ends up polluting other waterways). The coal slurry was supplemented in 1974 by a dedicated train line running from Black Mesa to another power plant, Navajo Generating Station, near Page, Arizona. Reno, supra note 58, at 108.

[116] Brian Jackson Morton argues that resolving the power struggle in their favor and consolidating authority explains the tribal council’s decision to approve the lease more so than the council’s desire to respond to reservation poverty. Morton, supra note 56, at 283.

[117] See Gordon, supra note 105, at 14.

[118] Id.

[119] Redhouse, supra note 109.

[120] Gordon, supra note 105, at 72 (internal quotation marks omitted).

[121] Id. Navajos in the areas affected by mining had to be relocated, an effort that, according to one study, required “the conceptual gap between Navajo perceptions and conventional economic development formulations” to be bridged. Schoepfle et al., supra note 54, at 888.

[122] David F. Aberle, Education, Work, Gender, and Residence: Black Mesa Navajos in the 1960s, 45 J. Anthropological Res. 405, 426 (1989). Robert Begay, writing in 2001, reported that 700 Navajos were employed by Peabody on Black Mesa. Robert Begay, Doo Dilzin Da: Abuse of the Natural World, 25 Am. Indian Q. 21, 22 (2001).

[123] This is not to imply that there were not many of the same problems of a “heavy hand of government oppression” in pushing the leases on the Navajo Nation. Redhouse, supra note 109 (noting that the then-attorney for the tribe complained in 1965 to the press of “a not-too-subtle implied threat on the Navajo Tribe that they had better do what [Secretary of the Interior] Udall wishes” (internal quotation marks omitted)).

[124] Though the nature of the tribal council’s formation might suggest otherwise, “it would be inaccurate to say that the current Navajo Nation government is simply a rubber stamp for the federal government or other outsiders bent on access to Navajo resources. The council is an integral and highly active part of public life on the Navajo Nation.” John W. Sherry, Land, Wind, and Hard Words: A Story of Navajo Activism 22 (2002); see also Mander, supra note 70, at 279 (crediting Peter MacDonald’s tenure as Tribal Chairman with making the Council cease to be a “rubber stamp for the BIA”).

The nature and extent of the Navajo Nation’s sovereign powers reflect the Supreme Court’s Indian law jurisprudence, a jurisprudence that recently has harmed the tribe in numerous ways by severely limiting tribal authority over non-Indians. Sarah Krakoff, A  Narrative of Sovereignty: Illuminating the Paradox of the Domestic Dependent Nation, 83 Or. L. Rev. 1109, 1195 (2005) (“The Supreme Court’s decisions that divest tribes of categories of jurisdiction over non‑members are doing the most mischief.”). Professor Sarah Krakoff has written an excellent article exploring the role of the Supreme Court decisions on Navajo sovereignty; she singles out for special condemnation the Court’s limitations on tribal jurisdiction. See id.

[125] Redhouse, supra note 109. Navajo society was traditionally organized as a matriarchy, with women controlling land and property and in which it was not uncommon for a woman to  have multiple husbands. See Ruth M. Underhill, The Navajos 8, 43, 48 (1967); Witherspoon, supra note 35, at 42–43, 74–75. The Anglo influence and assumption that tribes should have male leadership has broken down parts of this matriarchy, with men assuming the political leadership roles. Dine Policy Inst., Navajo Nation Constitutional Feasibility and Government Reform Project 56 (2008).

[126] Chamberlain, supra note 69, at 76 (“On June 15, 1935, Navajos rejected IRA by 7,679 to 8,197, a very close vote.”).

[127] The Navajo Nation Local Governance Act, Navajo Nation Code Ann. tit. 26, §§ 1–3, 101–103, 1001–1004, 2001–2005 (West 2005), aimed “to recognize governance at the local level.” Id. § 1(B)(1). The Navajo Nation Council wanted to allow “chapters greater autonomy in governmental decision-making.” Eric Lemont, Developing Effective Processes of American Indian Constitutional and Governmental Reform: Lessons from the Cherokee Nation of Oklahoma, Hualapai Nation, Navajo Nation, and Northern Cheyenne Tribe, 26 Am. Indian L. Rev. 147, 163 (2002). Yet, more than 10 years after the Local Governance Act was passed, only 10 chapters had completed the steps necessary to be certified to take on Local Governance Act authority. Div. of Cmty. Dev., Navajo Nation, Certified Chapters, http://www.nndcd.org/ content.asp?CustComKey=292717&CategoryKey=295197&pn=Page&DomName=nndcd.org (last visited Apr. 18, 2010).

[128] See Duane Champagne, Social Change and Cultural Continuity Among Native Nations 335 (2007) (“Native political arrangements are decentralized, egalitarian, and negotiated, while colonial tribal governments and Western political forms are hierarchical, centralize power and decision making, and are geared for greater political competitiveness.”).

[129] Lomayaktewa, 520 F.2d 1324, 1325, 1327 (9th Cir. 1975).

[130] Nancy B. Collins & Andrea Hall, Nuclear Waste in Indian Country: A Paradoxical Trade, 12 Law & Ineq. 267, 325 (1994) (“Second, American culture tends to essentialize vastly diverse Native American cultures, treating them all as uniformly ‘Indian.’”). Professor Saikrishna Prakash argues convincingly that the Court ought to recognize tribal differences rather than treat all tribes as synonymous with one another. Saikrishna Prakash, Against Tribal Fungibility, 89 Cornell L. Rev. 1069, 1070–72 (2004). Greater contextualism, according to Professor Robert Clinton, may also prevent larger tribes from seeing their rights diminished by the workings of “unrealistic claims by tribes on heavily allotted reservations” and federal Indian law’s universalist logic. Robert N. Clinton, Reservation Specificity and Indian Adjudication: An Essay on the Importance of Limited Contextualism in Indian Law, 8 Hamline L. Rev. 543, 596–97 (1985); see also Ezra Rosser, Ambiguity and the Academic: The Dangerous Attraction of  Pan‑Indian Legal Analysis, 119 Harv. L. Rev. F. 141, 141 (2006), available at http://www.harvardlawreview.org/media/pdf/rosser.pdf (arguing that this same phenomenon of wrongly ignoring tribal differences extends to Indian law academics).

[131] As Director of the Smithsonian’s National Museum of the American Indian, and former Assistant Secretary for Indian Affairs in the U.S. Department of the Interior, Kevin Gover notes,

At some point, the Montana tribes or the Alaska tribes may choose to pursue their own interests without regard to whether the tribes of other states receive the same consideration. Indian policy-making necessarily becomes more complex at that point, but it also becomes more sensible when it is customized to meet the particular circumstances of each tribe.

Kevin Gover, Federal Indian Policy in the Twenty-First Century, in American Indian Nations: Yesterday, Today, and Tomorrow 187, 206 (George Horse Capture et al. eds., 2007) [hereinafter American Indian Nations].

[132] See, e.g., Wilkinson, supra note 99, at 458.

[133] Lomayaktewa, 520 F.2d at 1327.

[134] Id.

[135] Navajo Nation, History Page, http://www.navajo.org/history.htm (last visited Apr. 18, 2010). The chapter system was created in 1928 to deal with “internal or local issues,” with the Council left to address “matters raised by the dominant society.” Chamberlain, supra note 69, at 75–76.

[136] The relationship between Washington’s control over the tribe and a single Navajo leader is highlighted in a 1920 letter noting the need for Washington approval of the form of Navajo governance. Atsidi Nez argued, “All the Navahos in every direction want to have but one boss,” but he prefaced his position by saying that a gathering of Navahos would have to “write to Washington, and then Washington can decide whether we can have one boss for all the Navahos or not.” Letter from Atsidi Nez to Father Anselm Weber (Dec. 31, 1920), in “For Our Navajo People”: Diné Letters, Speeches & Petitions, 1900–1960, at 160, 161–62 (Peter Iverson ed., 2002).

[137] See David E. Wilkins, The Navajo Political Experience 164–65 (rev. ed. 2003).

[138] But see Redhouse, supra note 109 (calling the Navajo Tribal Council of 1968 “the puppet council[]”). Perhaps part of the explanation for the difference in Hopi and Navajo reactions can be attributed to geography: Window Rock is several hours away from Black Mesa and governs a more extensive territory than do the Hopis, for whom Black Mesa plays a larger relative role. See Wilkinson, supra note 99, at 463. An anthropological article on Navajo attitudes regarding development notes, for example, that attitudes are likely to vary across regions and “be formed partly as a result of personal experience . . . . This should be especially true of such disruptive social changes as strip mining.” Schoepfle et al., supra note 54, at 895.

[139] McCabe & Lewis, supra note 67, at 30.

[140] Id. (quoting Testimony: Hearing Before the U.S. Comm’n on Civil Rights 27 (Oct. 22–24, 1973) (testimony of Peter MacDonald, Chairman, Navajo Tribal Council)).

[141] Id. at 7.

[142] See Chamberlain, supra note 69, at 97 (“Thanks to federal attorneys, who were either incompetent or unconcerned, Navajos did not receive adequate recompense.”); Donald L. Fixico, The Invasion of Indian Country in the Twentieth Century: American Capitalism and Tribal Natural Resources 147 (1998) (“Tribes endowed with energy resources are also angered by the lack of proper supervision by [BIA] in protecting Indian interests and by [BIA’s] urging of tribes to accept inadequate leases.”); Francisconi, supra note 85, at 70 (faulting the federal government); Wilkins, supra note 137, at 164 (arguing that the discoveries of additional natural resources led mining interests to negotiate “with the tribe, or more accurately, with the BIA” which then lobbied the Tribal Council to act without deliberation in approving the leases).

[143] See Reno, supra note 58, at 113.

[144] Id. As Professor Michael Joseph Francisconi explains, “The federal government was not in business to make a profit, and therefore leased lands below market prices.” Francisconi, supra note 85, at 68 (identifying this as the most important way in which the U.S. government controlled “[t]he supply side of Diné resources”). Russel Lawrence Barsh argues that with companies getting the same effective discount rate until the 1970s for Indian lands as public lands for the sake of national development, the lease discounting served as “a confiscatory transfer from the poorest few to the many.” Barsh, supra note 50, at 213.

[145] See Morton, supra note 56, at 118–19.

[146] Id. But see Ali, supra note 11, at 82 (arguing that the leases “gave unprecedented concessions to the coal company,” with coal royalty rates 20% of the federal royalty rate at the time and “‘laughable’” water use rates (quoting Wilkinson, supra note 99, at 471)).

[147] Morton, supra note 56, at 115.

[148] Id. at 294.

[149] Id. at 198–99; Reno, supra note 58, at 114 (“[I]n 1975 the rate of profit for coal mining was the highest of any industry in the United States—running at 20 percent of equity in 1974.”).

[150] Morton, supra note 56, at 255 (describing, but not arguing in favor of, this perspective).

[151] McCabe & Lewis, supra note 67, at 25.

[152] Deloria, supra note 1, at 195.

[153] Morton, supra note 56, at 256–57.

[154] Grijalva, supra note 15, at 25 (“[F]ederal policies for reservation economic development in the 1950s and 1960s relied almost exclusively on non-Indian exploitation of tribal lands and natural resources.”); Morton, supra note 56, at 101, 246–47.

[155] Reno, supra note 58, at 116.

[156] United States v. Navajo Nation (Navajo Nation I), 537 U.S. 488, 495 (2003).

[157] Francisconi, supra note 85, at 67.

[158] Navajo Nation I, 537 U.S. at 493.

[159] See id. at 496–98 (explaining the allegations that Peabody Coal forced the tribe back to the bargaining table under “severe economic pressure” by delaying the Secretary of the Interior’s adjustment of the royalty rate by meeting with him in secret (internal quotation marks omitted) (quoting Navajo Nation v. United States, 263 F.3d 1325, 1328 (Fed. Cir. 2001))).

[160] The requirement of a final sign-off by the Secretary of the Interior “traces back to the Nonintercourse Act, first enacted by the first Congress in 1790, and unchanged since 1834. The Nonintercourse Act provides that no lease or other encumbrance of Indian land is valid under United States law without the consent of the federal government.” Royster, supra note 96, at 1077.

[161] Navajo Nation I, 537 U.S. at 496–97.

[162] Id. at 520 (Souter, J., dissenting); Ezra Rosser, The Trade-Off Between Self-Determination and the Trust Doctrine: Tribal Government and the Possibility of Failure, 58 Ark. L. Rev. 291, 311–12 (2005) (explaining the details of Stanley Hulett’s meeting with Secretary Hodel).

[163] United States v. Navajo Nation (Navajo Nation II), 129 S. Ct. 1547, 1553 (2009). For more on the facts surrounding the royalty rates and the origins of the litigation, see Bill Donovan, Case Closed: U.S. Supreme Court Kills Bid to Hold Interior Accountable for Coal Royalty Deceit, Navajo Times (Window Rock, Ariz.), Apr. 9, 2009, http://navajotimes.com/news/2009/ 0409/040909coal.php (last visited Apr. 18, 2010).

[164] 25 U.S.C. §§ 396a–396g (2006).

[165] 28 U.S.C. § 1505 (2006); Navajo Nation I, 537 U.S. at 511, 514.

[166] Navajo Nation v. United States, 501 F.3d 1327, 1348–49 (Fed. Cir. 2007), rev’d, 129 S. Ct. 1547 (2009).

[167] Navajo Nation II, 129 S. Ct. at 1551. During oral argument, Justice Ginsburg was particularly quick to indicate that she felt Navajo Nation I was determinative. Adam Liptak, On Return, Ginsburg Is Quick to Question, N.Y. Times, Feb. 24, 2009, at A12; see also Posting of Matthew L.M. Fletcher to Turtle Talk, Commentary on the Navajo Nation Oral Argument, http://turtletalk.wordpress.com/2009/02/24/commentary-on-the-navajo-nation-oral-argument (Feb. 24, 2009, 09:40) (last visited Apr. 18, 2010) (noting that the oral arguments “did not go very well” for the tribe).

[168] Navajo Nation II, 129 S. Ct. at 1551.

[169] Id. at 1558.

[170] Id. at 1558 (Souter, J., concurring).

[171] Navajo Nation I, 537 U.S. 488, 520 (2003) (Souter, J., dissenting).

[172] Royster, supra note 96, at 1085; Navajo Nation II, 129 S. Ct. at 1551.

[173] See Brief for Respondent at 12, Navajo Nation II, 129 S. Ct. 1547 (No. 07-1410), available at http://www.narf.org/sct/usvnavajonation/brief_for_respondent.pdf (presenting the conclusions of Dr. Rai who, based in part on Bureau of Mines’s studies, “rejected the notion that the customary 12½% rate for federal coal should be adopted” because the contract did not include a bonus to reflect the “extraordinary value of the tribal coal”).

[174] The Secretary of the Interior can take a more protective and paternalistic approach: In 1976, the Secretary refused to approve the Burnham mine lease until the original agreement was renegotiated with improved terms for the Navajo Nation. Ali, supra note 11, at 65.

[175] Francisconi, supra note 85, at 67–69 (describing the history of coal extraction on Navajo land); Reno, supra note 58, at 113.

[176] Grijalva, supra note 15, at 112 (arguing that emissions limitations and “new strip mining technologies” under the Clean Air Act, 42 U.S.C. §§ 7401–7671q (2006), together contributed to making the mining industry focus its attention on Indian coal around 1976); see Clements, supra note 24, at 114.

[177] Jeff Radford, Stripmining Arid Navajo Lands in the US: Threats to Health and Heritage, 11 Ambio 9, 10 (1982).

[178] Fixico, supra note 142, at 150 (“In the West, draglines can strip-mine 100 tons of coal per man-day of labor, more than eight times the rate from the deep Appalachian shaft mines.”).

[179] See infra Part III; see, e.g., W. Roger Buffalohead, Self-Rule in the Past and Future: An Overview, in Indian Self-Rule, supra note 1, at 265, 272–73 (“It was not Collier but later commissioners of Indian affairs and reservation Indian leaders looking for a quick fix to economic poverty who brought uranium mines and polluting coal development and many other economic enterprises to Indian reservations.”); Morton, supra note 56, at 269 (“Enduring poverty formed the context of the tribe’s coal leasing in general.”).

[180] Francisconi, supra note 85, at 67–69. The tribe employs the majority of the wage earners on the reservation. Id. at 68.

[181] Id. at 74.

[182] Fixico, supra note 142, at 151 (“The Department of the Interior could persuade tribal officials to lease land to companies, thereby easing the exploitation of Indian lands.”).

[183] Peter MacDonald, An Indian View of Minerals Development on Indian Lands, in Inst. on Indian Land Dev., Oil, Gas, Coal and Other Minerals 1-1, 1-3 (1976), quoted in Morton, supra note 56, at 189. In his autobiography, MacDonald was more direct, describing the mid-70s leases as forms of environmental and financial “rape,” and linking these leases to the formation of the Council of Energy Resource Tribes. MacDonald, supra note 37, at 229.

[184] Greig, supra note 115, at 5. The Supreme Court acknowledged, but did not find dispositive with regard to damages for breach of trust, the pervasive federal control over Navajo coal in Navajo Nation II. 129 S. Ct. 1547, 1557–58 (2009).

[185] Grijalva, supra note 15, at 19–20;  see also Pollution: Keep America Beautiful—Canoe (Ad Council 1971), http://www.aef.com/misc_video/adcouncil/indian_in_canoe_60.mpg. The Keep America Beautiful and Ad Council advertisement won multiple awards, and Iron Eyes Cody, the actor, eventually was honored with a Hollywood Walk of Fame star. Ad Council, Pollution Prevention: Keep America Beautiful—Iron Eyes Cody (1961–1983) (2003), http://www.aef.com/exhibits/social_responsibility/ad_council/2278 (last visited Apr. 18, 2010). The ad “appeared widely in print and on television” and was so successful because it “cleverly manipulated ideas deeply engrained in the national consciousness.” Shepard Krech III, The Ecological Indian: Myth and History 15 (1999). Robert Yazzie, former Chief Justice of the Navajo Nation, criticizes the ad as “totally false because it is based on the stereotyping of Indians as being ‘stoic’ and without emotions.” Robert Yazzie, Air, Light/Fire, Water and Earth/Pollen: Sacred Elements that Sustain Life, 18 J. Envtl. L. & Litig. 191, 191 (2003).

[186] Armstrong Wiggins, Indian Rights and the Environment, 18 Yale J. Int’l L. 345, 354 (1993) (“Although Indian communities, like all others, have difficult decisions to make about their development, there is good reason to believe that if Indians are permitted to chart their own future they will continue to serve not only themselves, but also the global environment.”).

[187] Robert H. Keller and Michael F. Turek note the dangers of the generalizing nature
of stereotypes:

[T]he “Indian as Environmentalist” evokes powerful reactions. Like most stereotypes, its shard of truth can cause more harm than good. Indians who ride motorcycles instead of ponies, who fish with nylon gillnets instead of wooden weirs, who clear-cut tribal forests rather than seek visions . . . find that non-Indians, including environmentalists, can react with dismay, anger, and disbelief. The ecological mandate freezes Indians as an idea and artifact, a static and quaint people who have few economic needs.

Keller & Turek, supra note 39, at 178.

[188] Pommersheim, supra note 9, at 246.

[189] Id. at 350.

[190] Id. at 368.

[191] Wiggins, supra note 186, at 348.

[192] Robert Laurence, A Memorandum to the Class, in Which the Teacher Is Finally Pinned Down and Forced to Divulge His Thoughts on What Indian Law Should Be, 46 Ark. L. Rev. 1, 2 (1993).

[193] Grijalva, supra note 15, at 19; see also Reno, supra note 58, at 3 (“Indians have . . . been called the first American ecologists . . . .”); Jace Weaver, Introduction: Notes from a Miner’s  Canary, in Defending Mother Earth: Native American Perspectives on Environmental Justice 1, 4 (Jace Weaver ed., 1996) (noting that “worshipful Whites” saw Indians as “the first environmentalists”).

[194] Mark David Spence, Dispossessing the Wilderness: Indian Removal and the Making of the National Parks 11–12 (1999) (internal quotation marks omitted).

[195] Keller & Turek, supra note 39, at 177. They add that the thought behind such a stereotype is that “unless people heed the Indian, Western civilization may destroy the planet.” Id. at 178.

[196] See, e.g., Collins & Hall, supra note 130, at 326 (“Many environmentalists homogenize and romanticize all Native Americans as environmentalists who desire to keep their land free of all economic development.”); Wiggins, supra note 186, at 354 (“Although Indian communities, like all others, have difficult decisions to make about their development, there is good reason to believe that if Indians are permitted to chart their own future they will continue to serve not only themselves, but also the global environment.”); Carl H. Johnson, Note, Balancing Species Protection with Tribal Sovereignty: What Does the Tribal Rights–Endangered Species Order Accomplish?, 83 Minn. L. Rev. 523, 558 (1998) (arguing that because of their values, “tribes are more motivated to protect habitat” than non-Indians).

[197] Fixico, supra note 142, at 145. This holds true for traditional Navajos. Begay, supra note 122, at 24.

[198] Valerie L. Kuletz, The Tainted Desert: Environmental Ruin in the American West 97 (1998) (discussing the U.S. Nuclear Negotiator and U.S. environmental policy).

[199] Rebecca Tsosie, How the Land Was Taken: The Legacy of the Lewis and Clark Expedition for Native Nations, in American Indian Nations, supra note 131, at 246; see also Sarah Krakoff, American Indians, Climate Change and Ethics for a Warming World, 85 Denv. U. L. Rev. 865, 868 (2008) (“American Indian people are not hard-wired to be any closer to nature or more environmentally sensitive than non-Indian people. But their traditional religious and cultural systems of meaning revolve around the earth and its values, and these long-held beliefs have influenced how American Indians view and interact with the land and the natural world.”).

[200] John P. LaVelle, Rescuing Paha Sapa: Achieving Environmental Justice by Restoring the Great Grasslands and Returning the Sacred Black Hills to the Great Sioux Nation, 5 Great Plains Nat. Resources J. 40, 96 (2001) (“Many commentators have noted the high solicitude for conservational values and ecological balance manifested in traditional American Indian tribal societies.”). For more on traditional Indian environmental beliefs and relations with the land, see Tsosie, supra note 71, at 272–87.

[201] Keller & Turek, supra note 39, at 240; see also LaVelle, supra note 200, at 96, 98 (arguing that “one should avoid endorsing conventional stereotypes about Indians and the environment” but also “recognize that environmental stewardship and reverence for nature are central, pervasive, and normal attributes of tribal societies”).

[202] Conceits that rely upon “ahistorical” ideas of Indians as people who live in an eden-esque state of nature are not limited to the area of Indians and the environment. See Kenneth H. Bobroff, Retelling Allotment: Indian Property Rights and the Myth of Common Ownership, 54 Vand. L. Rev. 1559, 1620–21 (2001) (disproving the idea underlying allotment that Indian societies did not recognize property rights in individuals).

[203] Terry L. Anderson, Sovereign Nations or Reservations? An Economic History of American Indians, at xiv (1995) (“American Indian institutions were far from static but evolved in response to environmental and market conditions. . . . Indians readily adapted their institutions to meet changing economic and environmental conditions even before contact with Europeans.”).

[204] Krech, supra note 185, at 26–27.

[205] Jana L. Walker et al., A Closer Look at Environmental Injustice in Indian Country, 1 Seattle J. Soc. Just. 379, 379–80 (2002) (focusing on conceptions of environmentalists).

[206] Robert D. Cooter & Wolfgang Fikentscher, American Indian Law Codes: Pragmatic Law and Tribal Identity, 56 Am. J. Comp. L. 29, 47 (2008).

[207] For an extended discussion of Indians as environmentalists, see Fixico, supra note 142, at 205–18.

[208] Collins & Hall, supra note 130, at 326.

[209] Id. at 325.

[210] Dean Suagee, Panel I: Tribal People and Environmentalists: Friends of Foes?, 7 Great Plains Nat. Resources J. 3, 4 (2002) (“[T]he easy case is dealing with environmental issues that arise outside of the reservation boundaries.”); see also Grijalva, supra note 15, at 160 (noting that a proposal by non-Indians to build a landfill over a tribe’s objections makes environmental justice issues “more obvious” than when a tribe proposes a landfill).

[211] A. Cassidy Sehgal, Note, Indian Tribal Sovereignty and Waste Disposal Regulation, 5 Fordham Envtl. L.J. 431, 454 (1994).

[212] Deloria, supra note 1, at 206; see also Keller & Turek, supra note 39, at 239–40 (arguing that it is “an unjust demand” that Indians not adapt to modern culture without risking the forfeiture of their rights).

[213] For a brief history of the environmental justice movement, see Grijalva, supra note 15, at 4–8. Additionally, EPA’s environmental justice history webpage provides a brief, agency-specific history of the implementation of environmental justice efforts. U.S. Envtl. Prot. Agency, Environmental Justice: Basic Information, http://www.epa.gov/oecaerth/basics/ejbackground.html (last visited Apr. 18, 2010).

[214] See, e.g., U.S. Gen. Accounting Office, Siting of Hazardous Waste Landfills and Their Correlation with Racial and Economic Status of Surrounding Communities (1983); Comm’n for Racial Justice, United Church of Christ, Toxic Wastes and Race in the United States: A National Report on the Racial and Socio-Economic Characteristics of Communities with Hazardous Waste Sites (1987).

[215] Jeffrey R. Cluett, Two Sides of the Same Coin: Hazardous Waste Siting on Indian Reservations and in Minority Communities, 5 Hastings W.-Nw. J. Envtl. L. & Pol’y 191, 192 (1999) (reciting findings of Comm’n for Racial Justice, supra note 214).

[216] Grijalva, supra note 15, at 5.

[217] Id.

[218] Exec. Order No. 12,898, 3 C.F.R. 859 (1995), reprinted in 42 U.S.C. § 4321 (2006).

[219] Rachel D. Godsil, Note, Remedying Environmental Racism, 90 Mich. L. Rev. 394, 396 (1991). How much is being shouldered is contextual. A sewage treatment plant in a poor neighborhood that serves an entire city is a localized form of environmental injustice; a community bearing “the burden of an environmental problem that belongs to the entire nation” is a more national form. See Collins & Hall, supra note 130, at 269 (discussing the storing of nuclear waste on Indian reservations).

[220] After discussing the challenges of finding deliberate environmental racism, Rachel Godsil ends her section on the definition by simply concluding, “[B]ecause hazardous waste sites must go somewhere, they are frequently placed in poor, minority communities.” Godsil, supra note 219, at 400.

[221] Id. at 396.

[222] Joshua Glasgow, Not in Anybody’s Backyard?: The Non-Distributive Problem with Environmental Justice, 13 Buff. Envtl. L.J. 69, 89–97 (2005) (arguing that political, educational, and informational limits among poor communities prevent them from imposing not-in-my-backyard-type costs upon developers pursuing environmentally harmful activities, making such communities more attractive to those developers). Media indifference to environmental problems in minority communities is arguably another contributing factor. Cluett, supra note 215, at 196.

[223] See Collins & Hall, supra note 130, at 304.

[224] Alice Kaswan, Distributive Justice and the Environment, 81 N.C. L. Rev. 1031, 1044 (2003) (describing the distributive environmental justice claim). Professor Kaswan’s thesis is that “distributional injustice is a matter of concern regardless of its cause.” Id. at 1050.

[225] Fixico, supra note 142, at xvi.

[226] See supra notes 63–66 and accompanying text; Cluett, supra note 215, at 197–98.

[227] Most articles focus on environmental justice theory and not on providing examples—so they should not necessarily be faulted for not discussing Indian environmental justice issues—yet the absence of Indian examples is striking. See, e.g., Kaswan, supra note 224 (containing a 118-page article without any discussion of Indian environmental justice issues).

[228] See Cluett, supra note 215, at 197 (“American Indians are rarely treated as a separate group for the purposes of examining environmental racism.”).

[229] Wiggins, supra note 186, at 349.

[230] A notable counter-example is Professor James Grijalva’s 2008 book, Closing the Circle: Environmental Justice in Indian Country. Grijalva, supra note 15.

[231] Robert A. Williams, Jr., Large Binocular Telescopes, Red Squirrel Piñatas, and Apache Sacred Mountains: Decolonizing Environmental Law in a Multicultural World, 96 W. Va. L. Rev. 1133, 1153 (1994).

[232] See Cluett, supra note 215, at 201–02 (describing the paternalistic position of Eleanor Metzger).

[233] Members of Congress share the idea that industry might need to be controlled because of the possibility “that tribal communities are being exploited by an unprincipled industry that takes advantage of poor communities.” Jana L. Walker & Kevin Gover, Commercial Solid and Hazardous Waste Disposal Projects on Indian Lands, 10 Yale J. on Reg. 229, 260 (1993). Tribes that decide to pursue harm-causing projects “face economic paternalism from those who believe . . . that Tribes are simply incapable of making proper and intelligent decisions.” Walker et al., supra note 205, at 390.

[234] Pommersheim, supra note 9, at 364.

[235] Fixico, supra note 142, at 190.

[236] The paternalism of the original quote comes across when seen alongside the practice of tribes to “seek . . . out” hazardous waste sites, even though such siting “generally seem[s] forced upon communities.” Cluett, supra note 215, at 201.

[237] “Indians” here refers to the collective rights of Indians as peoples, not Indians as individuals. The United States and other countries oppose the term “peoples” in relation to indigenous peoples and have sought “to delete the letter ‘s’ from the term ‘indigenous peoples.’” Dean B. Suagee, Recent Development, Human Rights of Indigenous Peoples: Will the United States Rise to the Occasion?, 21 Am. Indian L. Rev. 365, 376 (1997). Oren Lyons, a traditional chief of the Onondaga Nation, Iroquois Confederacy, explains, “When you say peoples, then we have to be recognized as separate nations and sovereigns. Consequently, they still refuse to add s to people.” Oren Lyons, Law, Principle, and Reality, 20 N.Y.U. Rev. L. & Soc. Change 209, 210 (1993). The issue took center stage at the 1993 United Nations World Conference on Human Rights and was dubbed “the battle of the ‘s’” by the Canadian press. Russel Lawrence Barsh, Indigenous Peoples in the 1990s: From Object to Subject of International Law, 7 Harv. Hum. Rts. J. 33, 51 (1994) (internal quotation marks omitted) (quoting Canadian Press, Battle of the ‘s, Montreal Gazette, June 23, 1993, at A12). For more on collective group rights of indigenous peoples and how these rights relate to U.S. history and political structure, see generally Robert N. Clinton, The Rights of Indigenous Peoples as Collective Group Rights, 32 Ariz. L. Rev. 739 (1990).

[238] See Williams, supra note 231, at 1154.

[239] Grijalva, supra note 15, at 9 (describing the EPA position); see also Collins & Hall, supra note 130, at 313 (“In order to understand the position of Native Americans in environmental law, the twin issues of racism and sovereignty must be understood.”); Walker et al., supra note 205, at 395 (“If Tribes are to achieve environmental justice within Indian country . . . it is absolutely imperative that environmental justice issues affecting Tribes be viewed against the backdrop of tribal sovereignty . . . .”).

[240] Grijalva, supra note 15, at 4 (making this claim based on tribal sovereignty and the close connections of Indians with the natural environment); Catherine A. O’Neill, Environmental Justice in the Tribal Context: A Madness to EPA’s Method, 38 Envtl. L. 495, 508 (2008) (arguing that Indians cannot be treated as any other “subpopulation” for environmental justice purposes because of tribal sovereignty and their government-to-government relationship with the United States (internal quotation marks omitted)).

[241] See, e.g., Oren Lyons et al., Traditionalism and the Reassertion of Indianness, in Indian Self-Rule, supra note 1, at 243, 244 (“We will determine what our culture is. It has been pointed out that culture constantly changes. It is not the same today as it was a hundred years ago. We are still a vital, active Indian society. We are not going to be put in a museum or accept your interpretations of our culture.”).

[242] For more on what environmental law stands to gain from Indian perspectives, see Grijalva, supra note 15, at x–xi (“Tribes . . . bring a measure of human humility and respect for the natural world modern American environmental law seemingly lacks but, I think, desperately needs.”); id. at 11 (“[W]estern environmental law as implemented by federal and state agencies is generally unable to account for Indian visions of environmental justice that include the physical, social and spiritual relations affected by various land development uses.”).

[243] Id. at xi.

[244] Charles F. Wilkinson & John M. Volkman, Judicial Review of Indian Treaty Abrogation: “As Long as Water Flows, or Grass Grows Upon the Earth”—How Long a Time Is That?, 63 Cal. L. Rev. 601, 617–18 (1975).

[245] Philip P. Frickey, Marshalling Past and Present: Colonialism, Constitutionalism, and Interpretation in Federal Indian Law, 107 Harv. L. Rev. 381, 401 (1993). Professor Frickey goes on to highlight the limitations of a contract of adhesion approach as compared to a sovereignty approach when interpreting Marshall’s opinion in Worcester v. Georgia, 31 U.S. (6 Pet.) 515 (1832). Frickey, supra, at 406–07 (focusing on timing of the Worcester decision, which predates the development of the adhesion contract approach in contract law).

[246] For more on the development of the Indian canons of construction, see Kristen A. Carpenter, Interpretive Sovereignty: A Research Agenda, 33 Am. Indian L. Rev. 111, 117–20 (2008).

[247] See id. at 120. Courts have resolved treaties between Indians and non-Indian governments “‘as the Indians would have understood them.’” See id. at 117 (quoting United States v. Shoshone Tribe of Indians, 304 U.S. 111, 116 (1938)).

[248] Congress, in 1871, passed legislation providing “[t]hat hereafter no Indian nation or tribe within the territory of the United States shall be acknowledged or recognized as an independent nation, tribe, or power with whom the United States may contract by treaty.” Act of Mar. 3, 1871, ch. 120, 16 Stat. 544, 566 (codified as amended at 25 U.S.C. § 71 (2006)). The Act reflected anger in the House of Representatives about not being involved in the treaty process; therefore, “abandonment of treatymaking was a matter of internal congressional politics.” Philip P. Frickey, (Native) American Exceptionalism in Federal Public Law, 119 Harv. L. Rev. 431, 441 (2005). Negotiated agreements approved by Congress and signed by the President replaced treaties. Id.

[249] The photograph was taken by William Chaplis on May 20, 1948, and can be seen  at  http://www.newberry.org/lewisandclark/newnation/ranchers/flooding.asp. See also Paul VanDevelder, Savages and Scoundrels: The Untold Story of America’s Road to Empire Through Indian Territory 113 (2009) (reprinting, on the preceding, unnumbered page, the photograph, and describing tribal chairman George Gillette as being “[o]vercome by grief” as “the formal takings act that allowed Congress to ‘condemn’ 156,000 acres of the tribes’ ancestral homelands” was signed).

[250] Bethany R. Berger, Williams v. Lee and the Debate over Indian Equality 12 (2010) (unpublished manuscript, on file with author) (emphasis added). Thanks to Professor Berger for locating the photo and for providing the history of the photo.

[251] Mandan, Hidatsa & Arikara Nation, History: Other History, http://www.mhanation.com/ main/history/history_garrison_dam.html (last visited Apr. 18, 2010).

[252] Fixico, supra note 142, at ix–x.

[253] Collins & Hall, supra note 130, at 314 (emphasis added).

[254] Id. at 320.

[255] Robert D. Bullard et al., United Church of Christ, Toxic Wastes and Race at Twenty: 1987–2007: Grassroots Struggles to Dismantle Environmental Racism in the United States 155 (2007), available at http://www.ucc.org/assets/pdfs/toxic20.pdf. A series of influential environmental justice articles by Professor Vicki Been uses the term “locally undesirable land uses” (LULUs for short); much of the thinking about environmental justice is framed in terms of LULUs. See Vicki Been, Locally Undesirable Land Uses in Minority Neighborhoods: Disproportionate Siting or Market Dynamics?, 103 Yale L.J. 1383, 1384 (1994) (discussing studies that demonstrate links between LULUs and socioeconomic characteristics); Vicki Been, What’s Fairness Got to Do With It? Environmental Justice and the Siting of Locally Undesirable Land Uses, 78 Cornell L. Rev. 1001, 1001–03 (1993) (discussing the siting of LULUs in poor or minority neighborhoods). However, here the choice to describe this in terms of “undesirable characteristics” instead of LULUs is deliberate; some harmful activities may have little local effects while still being undesirable, and will only be accepted with compensation. See, e.g., Howard A. Latin, Environmental Deregulation and Consumer Decisionmaking Under Uncertainty, 6 Harv. Envtl. L. Rev. 187, 197–98 (1982) (discussing environmental consequences that “occur at times and places far removed from the locus of consumer choice” (footnotes omitted)).

[256] The success of the ex parte communications between a Peabody lobbyist and Secretary Hodel attests to both the private-public linkages and the failure of the government to live up to the trust relationship. See supra notes 158–63 and accompanying text.

[257] Cluett, supra note 215, at 203 (“[R]esidents of minority and economically crippled communities, presented with promises of money and jobs, unwillingly receive hazardous waste facilities.”).

[258] See Morton, supra note 56, at 104 (citing Lorraine Turner Ruffing, The Navajo Nation: A History of Dependence and Underdevelopment, Rev. Radical Pol. Econ., Summer 1979, at 25, 31–32, for the proposition that the Navajo Nation’s dependence upon royalty payments is one reason for the “relatively low . . . bargaining power” of the tribe); see also Barsh, supra note 50, at 217 (“Even if Indian tribes were guaranteed absolute freedom of choice in land development, their dependence on government aid and capital would continue to influence planning.”).

It is beyond the scope of this Article to define or defend an accounting of what counts as U.S. government aid to tribes. For the purposes of this Article, it is enough to say that if the United States ceased providing tribes with funding, government services would suffer markedly for many tribes. Some U.S. government funding goes directly to tribal administrative agencies that have taken over work previously performed by BIA (similar to federal block grants to states), some funding is used to meet obligations that the United States agreed to through treaty, and some funding flows directly to individual tribal members as part of the government’s welfare obligations to all citizens, regardless of Indian or non-Indian status. See generally Deloria, supra note 1, at 194–200 (discussing reservation welfare programs); Virginia Davis, A Discovery of Sorts: Reexamining the Origins of the Federal Indian Housing Obligation,
18 Harv. BlackLetter L.J. 211, 211–12 (2002) (arguing that the U.S. government has treaty‑based obligations to provide reservation housing).

[259] Radford, supra note 177, at 12.

[260] See Williams, supra note 231, at 1153–54 (arguing that given high unemployment rates Indians will consider siting a hazardous waste dump on an unused area, but would not even think about such a dump if it were placed “where important spiritual, social, or physical values of the tribe are implicated”).

[261] Declaration of Joe Shirley, President of the Navajo Nation, at 3, Navajo Nation v. U.S. Forest Serv., 408 F. Supp. 2d 866 (D. Ariz. 2006) (Nos. CV 05-1824-PCT-PCR, CV 05-1914-PCT-EHC, CV 05-1949-PCT-NVW, CV 05-1966-PCT-JAT).

[262] Ezra Rosser, This Land Is My Land, This Land Is Your Land: Markets and Institutions for Economic Development on Native American Land, 47 Ariz. L. Rev. 245, 265–66 (2005) (looking at the causes and solutions to reservation poverty from the perspectives of neoclassical economics and new institutional economics).

[263] The dual—United States and tribal—control over trust land protects the integrity of the tribal land base, a goal that almost everyone working on behalf of tribes supports and that reflects the failure of allotment. See id. at 262–65. The problem comes when U.S. and tribal governments, together or independently, manage the trust land poorly and in ways that reduce the value of the land. Even those less supportive of tribal trust land who have done studies indicating that the trust status of reservation land reduces land output acknowledge that such cost “does not necessarily imply that trust constraints should be lifted.” Terry L. Anderson & Dean Lueck, Land Tenure and Agricultural Productivity on Indian Reservations, 35 J.L. & Econ. 427, 449 (1992).

[264] Joe De La Cruz et al., What Indians Should Want: Advice to the President, in Indian Self‑Rule, supra note 1, at 311, 319 (including, according to Philip S. Deloria, “the relationship of Indians to the economy” as part of the true conflict).

[265] Barsh, supra note 50, at 195.

[266] Id. at 195–98, 217.

[267] Robert L. Bee, Riding the Paper Tiger, in State and Reservation: New Perspectives on Federal Indian Policy 139, 140 (George Pierre Castile & Robert L. Bee eds., 1992).

[268] Grijalva, supra note 15, at 175; see McCabe & Lewis, supra note 67, at 22–24 (comparing the status of the Navajo reservation to an underdeveloped nation in the grip of a colonial system). The Canadian government shares in this, promoting “industry and enterprises center[ed] on natural resource extraction” as the means of generating jobs and government revenue on indigenous land. Taiaiake Alfred, Sovereignty, in Sovereignty Matters: Locations of Contestation and Possibility in Indigenous Struggles for Self-Determination 33, 45 (Joanne Barker ed., 2005).

[269] For up-to-date information on the dispute as well as a collection of the documents related to the case, see Save the Peaks Coal., Protect and Respect the Mountain and Our Children!, http://www.savethepeaks.org (last visited Apr. 18, 2010).

[270] Petition for a Writ of Certiorari at 3–6, Navajo Nation v. U.S. Forest Serv., 129 S. Ct. 2763 (2009) (No. 08-846); see also Jonathan Knapp, Note, Making Snow in the Desert: Defining a Substantial Burden under RFRA, 36 Ecology L.Q. 259, 295–96 (2009) (describing the importance of the Peaks in the beliefs of Navajos and Hopis).

[271] Petition for a Writ of Certiorari, supra note 270, at 3.

[272] Id.

[273] Id.

[274] Navajo Nation v. U.S. Forest Serv., 535 F.3d 1058, 1065 (9th Cir. 2008).

[275] Id. (internal quotation marks omitted) (quoting Navajo Nation v. U.S. Forest Serv., 208 F. Supp. 2d 866, 907 (D. Ariz. 2006)).

[276] Id. Though the toilet wastewater complaint is straightforward, it might appear to require a little creativity to connect sewage with dead bodies; but according to the Navajo Nation President, the connection is a significant one:

Practitioners of the Navajo religion are not concerned with what the scientists say about the quality of reclaimed wastewater. Some of this water has come into contact with death and sickness at, for example, hospitals and mortuaries. It does not matter what kind of treatment is provided, this water will compromise and contaminate the sacred Mountain that was established by the Holy People.

Declaration of Joe Shirley, President of the Navajo Nation, supra note 261, at 2. The dissent seemed to agree, quoting Larry Foster, a Diné training to be a medicine man, at length for a description of the harm associated with sewage water, with Foster twice referring to “mortuaries or hospitals.” Navajo Nation, 535 F.3d at 1103 (Fletcher, J., dissenting) (internal quotation marks omitted).

[277] 42 U.S.C. §§ 2000bb to -4 (2006); Navajo Nation, 535 F.3d at 1067.

[278] Navajo Nation, 535 F.3d at 1070.

[279] Id. (discussing amount of land impacted); id. at 1089 (Fletcher, J., dissenting) (criticizing the majority’s “restrictive definition of ‘substantial burden’”); Brief of Amici Curiae Religious  Liberty Law Scholars in Support of Petition for a Writ of Certiorari at 4–7, Navajo Nation v. U.S. Forest Serv., 129 S. Ct. 2763 (2009) (No. 08-846).

[280] Navajo Nation, 535 F.3d at 1065.

[281] Based on a personal experience of the author playing seventh-grade soccer on fields irrigated with such water in Kayenta, Arizona.

[282] Navajo Nation, 535 F.3d at 1111 (Fletcher, J., dissenting).

[283] Id. at 1082.

[284] Id. at 1113 (quoting id. at 1063 (majority opinion)). Professor Kristen A. Carpenter, who has done a series of articles on the religious rights of non-Indian owners, tellingly begins one article on sacred site jurisprudence by calling attention to the fact that “through varied means of acquisition, non-Indian governments, entities, and individuals have come to own Indian sacred sites.” Kristen A. Carpenter, Old Ground and New Directions at Sacred Sites on the Western Landscape, 83 Denv. U. L. Rev. 981, 983 (2006); see also Kristen A. Carpenter, A Property Rights Approach to Sacred Sites Cases: Asserting a Place for Indians as Nonowners, 52 UCLA L. Rev. 1061, 1063 (2005) (discussing the special problem American Indians face in practicing religious and cultural activities on land owned by the federal government); Kristen A. Carpenter, Sonia K. Katval & Angela R. Riley, In Defense of Property, 118 Yale L.J. 1022, 1024–25 (2009) (focusing on protecting indigenous cultural rights through property interests).

[285] But see Knapp, supra note 270, at 306–11 (offering a critique of Justice Fletcher’s approach to the case).

[286] Navajo Nation v. U.S. Forest Serv., 129 S. Ct. 2763 (2009); see also Grijalva, supra note 15, at 172 (“[T]he Court’s modern role is not to seek justice delayed for Indian people, but rather to ensure those who benefit from a nation built on land and natural resources acquired from Tribes by force, threats, artifice and fraud continue to do so.”).

[287] The amicus certiorari petition brief submitted by the National Congress of American Indians draws parallels between how Indians view the San Francisco Peaks and the importance for non-Indians of sacred sites around the world, and asks, “If Mount Calvary, the Holy Mosque in Mecca, or the Wailing Wall were located on public lands in the United States, would they be denied protection under RFRA in the same manner as the San Francisco Peaks?” Brief of Amici Curiae National Congress of American Indians et al. in Support of Petitioners at 17, Navajo Nation v. U.S. Forest Serv., 129 S. Ct. 2763 (No. 08-846).

[288] See Marsha Weisiger, Dreaming of Sheep in Navajo Country 18 (2009).

[289] Gary Witherspoon, Sheep in Navajo Culture and Social Organization, 75 Am. Anthropologist 1441, 1443 (1973).

[290] Filmmaker Billy Luther, himself the son of the 1966 winner, followed Crystal Frazier as she prepared for and competed in the pageant; the butchering scene in the resulting documentary vividly captures the importance of sheep for the Diné. The author strongly recommends readers interested in the Navajo Nation see, literally see, Miss Navajo (World of Wonder Productions 2007). More information is available at World of Wonder Prods., Miss Navajo: A Documentary by Billy Luther, http://www.missnavajomovie.com (last visited Apr. 18, 2010).

[291] See World of Wonder Prods., supra note 290.

[292] Coolidge & Coolidge, supra note 37, at 63.

[293] Morton, supra note 56, at 265.

[294] Eric Henderson, Navajo Livestock Wealth and the Effects of the Stock Reduction Program of the 1930s, 45 J. Anthropological Res. 379, 380–81 (1989).

[295] Id. at 380 (citing an 1892 account of a Gallup school superintendent).

[296] Although containing some statements that are offensive by today’s standards—Navajos are described as “superior physically and in other respects” and “[the] sex morals are on a higher plane than with most tribes”—an article entitled Navajo Land Problems published in 1937 provides a great window into the thinking at the time as to the origins of, and solutions for, Navajo overgrazing. See J.W. Hoover, Navajo Land Problems, 13 Econ. Geography 281, 283, 297–98 (1937).

[297] Professor Colleen O’Neill explains,

[T]he advent of a new, reformist administration offered a unique opportunity . . . . The soil experts, climatologists, agricultural economists, and sociologists who descended onto the reservation in the 1930s to preserve Navajo rangelands enjoyed unprecedented political support in Washington and unwavering faith that science would offer an acceptable solution.

These scientists examined all aspects of the Navajos’ problem. They tested the soils, studied the climate, and inspected the livestock. They assessed the carrying capacity of reservation land and divided it into eighteen land management districts and calculated how many sheep, goats, and horses each could support.

O’Neill, supra note 57, at 23 (citation omitted).

[298] David Wilkins, Governance Within the Navajo Nation: Have Democratic Traditions Taken Hold?, Wicazo Sa Rev., Spring 2002, at 91, 105 (2002). The same basic promise—that if the Navajos cooperated they would get more land—had been made to induce the tribal council to approve oil leases in the 1920s. See supra note 95.

[299] Gary D. Libecap & Ronald N. Johnson, The Navajo and Too Many Sheep: Overgrazing on the Reservation, in Bureaucracy vs. Environment: The Environmental Costs of Bureaucratic Governance 87, 89 (John Baden & Richard L. Stroup eds., 1981). For an overview of the development of the Navajo sheep economy as well as the range conditions related to Navajo livestock, see Reno, supra note 58, at 15–16, 26–45.

[300] The government paid families $1 per goat and $2 per sheep; between 1933 and 1934, according to one study, the market price for sheep rose from $2.30 to $3.35. Libecap & Johnson, supra note 299, at 89–90.

[301] Chamberlain, supra note 69, at 73 (discussing the goat reductions of 1934).

[302] Kelly, supra note 71, at 162.

[303] Robert S. McPherson, Navajo Livestock Reduction in Southeastern Utah, 193346: History Repeats Itself, 22 Am. Indian Q. 1, 7 (1998). Moreover, “[a]s stock reduction became increasingly forced, more violence and longer jail sentences resulted.” Id. at 12.

[304] Kelly, supra note 71, at 114.

[305] Francisconi, supra note 85, at 50. In a 1934 article written by the Department of the Interior’s Director of the Soil Erosion Service that uses reservation erosion as an example of a generalized problem, readers are walked through the scientific process of dealing with erosion across the country on a farm-by-farm basis and told that “work is carried out on a strictly cooperative basis with the farmers.” H.H. Bennett, Soil Erosion—A National Menace, 39 Sci. Monthly 385, 400 (1934). Such consideration was not extended on the Navajo reservation, where Navajos were “caught in a catastrophe, largely because they were a colonial appendage of American society.” White, supra note 38, at 248.

[306] Young, supra note 71, at 88.

[307] For more on the equity goals of stock reduction and how the program changed over time, see White, supra note 38, at 265–68 (noting that the goat reduction portion of the program disproportionately affected the poor, and highlighting opposition to early inequities); Henderson, supra note 294, at 393–400 (discussing the leveling of wealth); Libecap & Johnson, supra note 299, at 89–95 (highlighting Collier’s role in pushing an equity as part of the program and the consequent limits on herd size).

[308] Chamberlain, supra note 69, at 73 (“Many Navajos lost their livelihood altogether and were forced to accept government subsidies for the first time.”); Francisconi, supra note 85, at 58 (noting that stock reduction made supplemental wages and welfare income a necessity for many families); McPherson, supra note 303, at 2 (including the “crippling of the relatively self‑sufficient Navajo economy” among the effects of stock reduction).

[309] Wilkins, supra note 298, at 104.

[310] Chamberlain, supra note 69, at 83.

[311] McPherson, supra note 303, at 1.

[312] Stock reduction’s “economic hardships” were supposed to be offset in part through wage work on New Deal conservation projects, in line with Collier’s pledge “to triple Navajo income.” Weisiger, supra note 288, at 165. The end result, however, was “the expropriation and absolute impoverishment of many Navajo families.” Lawrence David Weiss, The Development of Capitalism in the Navajo Nation: A Political-Economic History 98 (1984). For an excellent way to better understand the effects and experience of the livestock reduction policy, see Navajo Livestock Reduction: A National Disgrace (1974), a collection of first-hand accounts of Diné herders and politicians looking back on livestock reduction published by the Navajo Community Press.

[313] For more on the plenary power over Indians, see Nell Jessup Newton’s leading article on the topic. Nell Jessup Newton, Federal Power over Indians: Its Sources, Scope, and Limitations, 132 U. Pa. L. Rev. 195 (1984). The summary of plenary power is captured by Professor Phil Frickey: “By virtue of its plenary power, Congress has run rough-shod over tribal interests.” Philip P. Frickey, Domesticating Federal Indian Law, 81 Minn. L. Rev. 31, 45 (1996).

[314] Young, supra note 71, at 152.

[315] Id.

[316] Id.

[317] Morton, supra note 56, at 297.

[318] Collins & Hall, supra note 130, at 270 (arguing that such alternatives are required if tribes are to properly engage in cost-benefit analysis regarding nuclear waste storage).

[319] Cluett, supra note 215, at 199–200.

[320] Backcountry Against Dumps v. U.S. Envtl. Prot. Agency, 100 F.3d 147, 149 (D.C. Cir. 1996).

[321] Id. at 149–50.

[322] Id. at 147; Smithsonian Institution, Senior Staff Biography: Kevin Gover, Director, National Museum of the American Indian, http://newsdesk.si.edu/admin/bios/gover.htm (last visited Apr. 18, 2010).

[323] The authors’ footnote acknowledges that the authors were the attorneys for the Campo Band. Walker & Gover, supra note 233, at 229.

[324] Id. at 231–32.

[325] This despite the fact that waste companies are attracted to Indian communities in part because of “the prospect of relaxed regulation in Indian Country.” Mary Christina Wood, Indian Land and the Promise of Native Sovereignty: The Trust Doctrine Revisited, 1994 Utah L. Rev. 1471, 1484 (1994). Walker and Gover’s position rejecting a non-Indian role with regard to tribal environmental matters is shared by others. After identifying sources of law, including some available to non-Indians, Dean B. Saugee’s and John P. Lowndes’s article on public participation in tribal environmental programs concludes by arguing that tribal courts and tribal officials bear the responsibility for establishing the right procedures and protections, thus implicitly favoring the resolution of all concerns through the tribal system. Dean B. Saugee & John P. Lowndes, Due Process and Public Participation in Tribal Environmental Programs, 13 Tul. Envtl. L.J. 1, 43 (1999).

[326] Walker & Gover, supra note 233, at 231.

[327] See Cluett, supra note 215, at 200.

[328] Walker & Gover, supra note 233, at 258.

[329] Fortunately for the Campo Band, they were able to resolve disputes with the state of California in 1997, and the Golden Acorn Casino opened in 2001. Campo Kumeyaay Nation, Campo Kumeyaay Nation History, http://www.campo-nsn.gov/modernera.html (last visited Apr. 18, 2010).

[330] For more on the controversy, see Dan McGovern, The Campo Indian Landfill War: The Fight for Gold in California’s Garbage (1995).

[331] Walker & Gover, supra note 233, at 262.

[332] Collins & Hall, supra note 130, at 270 (focusing on tribal-U.S. relations and nuclear waste siting).

[333] Anderson, supra note 203, at 1; see also Walker et al., supra note 205, at 384 (“The economic condition and public health status of [American Indians and Alaska Natives] are among the lowest of any ethnic or minority group in the United States.”).

[334] Joseph P. Kalt & Stephen Cornell, The Redefinition of Property Rights in American Indian Reservations: A Comparative Analysis of Native American Economic Development, in American Indian Policy, supra note 72, at 121, 126. Backlash against gaming tribes impacts the cultural perception non-Indians have of Indian tribes seeking federal recognition. Renee  Ann Cramer, The Common Sense of Anti-Indian Racism: Reactions to Mashantucket Pequot Success in Gaming and Acknowledgment, 31 Law & Soc. Inquiry 313, 314 (2006). Professor Bethany Berger argues that protests arise when tribes violate the “racially fixed image” of Indians as “poor, traditional, and close to the earth.” Bethany R. Berger, Red: Racism and the American Indian, 56 UCLA L. Rev. 591, 651 (2009). For a detailed account of the anti‑Indian, anti-casino backlash focused on Connecticut, home of Foxwoods and the Mohegan Sun, see Jeffrey R. Dudas, The Cultivation of Resentment: Treaty Rights and the New Right 95–136 (2008).

[335] Aberle, supra note 122, at 414.

[336] For more on the causes of reservation poverty, see Walker et al., supra note 205, at 387. Walker et al. explain,

These reasons include, but are not limited to, lack of money for new projects on Indian lands, as tribal and Indian trust land cannot generally be mortgaged or put up for collateral; the remoteness of most reservations which makes many projects not economically feasible; lack of infrastructure—electricity, communication systems, water, roads, and buildings—conducive to business; lack of skilled laborers and professionals; and the applicability of many federal, as well as tribal, laws to activities in Indian country that may make businesses reluctant to locate there.

Id. Vine Deloria, Jr., writing about allotment, argued, “Indian poverty was deliberately planned and as predictable as the seasons.” Vine Deloria, Jr., Reserving to Themselves: Treaties and the Powers of Indian Tribes, 38 Ariz. L. Rev. 963, 978 (1996).

[337] Buffalohead, supra note 179, at 273.

[338] Joe De La Cruz et al., What Indians Should Want: Advice to the President, in Indian Self‑Rule, supra note 1, at 311, 321.

[339] See Cluett, supra note 215, at 201 (“As host to a uranium mine, Laguna Pueblo has become one of the best-educated tribes, having produced poets, doctors, writers, lawyers and academics.”).

[340] R. David Edmunds et al., Tribal Sovereignty: Roots, Expectations, and Limits, in Indian Self-Rule, supra note 1, at 289, 290.

[341] Collins & Hall, supra note 130, at 275.

[342] Fixico, supra note 142, at 189.

[343] Professor Fixico’s treatment of this issue illustrates the difficulties of recognizing agency when tribes are also part of a larger system: “[C]apitalistic greed” is described as inconsistent with Indian values regarding the environment at one point. Id. at 189. On the other hand, when describing Indian motivations in more detail, Professor Fixico notes, “The Indians’ reaction to the demand for their energy resources is twofold: reluctance to allow the mining operations to continue, on one hand, and a progressive attitude toward increased mining to help develop tribal programs on the other.” Id. at 144.

[344] Deloria, supra note 1, at 200.

[345] Professor Hertzberg calls economics a “neglected subject,” and notes, “We talk about Indian poverty, but there has not been enough analysis of the economic conditions on reservations.” Suzan Shown Harjo, Russell Jim, Hazel W. Hertzberg, Joe De La Cruz & Oren Lyons, Federal Indian Policy Yesterday and Tomorrow, in Indian Self-Rule, supra note 1, at 278, 283.

[346] Reno, supra note 58, at 2 (arguing that because of proximity, Indian tribes share the resource problems, though not the affluence). Though it sounds good to speak in terms of the “need to preserve our ecosystems from contamination so indigenous people can utilize those natural resources,” the irony is that surrounding community contamination is what provides the market for on-reservation waste siting. Harjo et al., supra note 345, at 281.

[347] See supra notes 252–60 and accompanying text; see also Walker et al., supra note 205,
at 390 (“Tribes seeking to free themselves from federal dependence and poverty often must consider less desirable forms of economic development that may include potentially polluting industries and locally unwanted land uses (‘LULUs’).”).

[348] Professors Joseph Kalt and Stephen Cornell of the Harvard Project on Indian Economic Development explain,

[S]ome American Indian tribes have enjoyed more extensive, complete, and secure property titles than private companies. That is, in a number of important respects, reservations are more “deregulated”—at least with respect to nontribal governments—than the vast bulk of the rest of the economy. This creates niches in the market that present American Indian tribes with classic opportunities for the exercise of comparative advantage. The question, of course, is how, and how well, tribes can respond to these opportunities.

Kalt & Cornell, supra note 334, at 126.

[349] Gilbreath, supra note 48, at 55.

[350] Al Henderson, Introduction: What Economic Development Means to the Navajo, in Reno, supra note 58, at xii, xv.

[351] Id. at xii.

[352] Trib Choudhary, Div. of Econ. Dev., Navajo Nation, Comprehensive Economic Development Strategy of the Navajo Nation 2005–2006, at T 49 tbl.21 (2006).

[353] Press Release, Office of the President & Vice President, Navajo Nation, Fluor Corp. Signs Agreement to Build Desert Rock Energy Project, Navajo President Joe Shirley, Jr., Calls It Step to Independence (Sept. 7, 2007), available at http://www.navajo.org/News%20Releases/George%20
Hardeen/Sept07/Fluor%20Corporation%20selected%20to%20build%20Desert%20Rock%20plant%20for%20Sept.pdf. Fifty-two million dollars annually is the project’s revenue benefit to the tribe according to Desert Rock Energy Co., Our Commitment: Environment, http://www.desertrock
energyproject.com/commitment.htm (last visited Apr. 18, 2010).

The power plant may employ some non-Indians with special training or qualifications, but, given the plant’s location on a remote part of the reservation and the Navajo Preference in Employment Act (NPEA), Navajo Nation Code Ann. tit. 15, §§ 601–619 (West 2005), a sizable percentage of employees are likely to be Navajo. Sithe Global acknowledges the NPEA would apply and assumes “that 65 to 80 percent of the workforce, or 130 to 160 workers, would be American Indian. Most of them would be Navajo.” Sithe Global Power LLC, Application for Prevention of Significant Deterioration Permit for the Desert Rock Energy Facility Additional Impacts: Environmental Justice Analysis 30 (2006). Though the NPEA might be vulnerable to legal challenge, a suit by the Equal Employment Opportunity Commission (EEOC) against Peabody Coal for the company’s practice of Navajo hiring and promotion preferences on Black Mesa was dismissed by the United States District Court of Arizona in 2006. Equal Employment Opportunity Comm’n v. Peabody W. Coal Co., No. CV 01-01050-PHX-MHM, 2006 WL 2816603, at *17–18 (D. Ariz. Sept. 30, 2006); see also Ann E. Tweedy, Connecting the Dots Between the Constitution, the Marshall Trilogy, and United States v. Lara: Notes Toward a Blueprint for the Next Legislative Restoration of Tribal Sovereignty, 42 U. Mich. J.L. Reform 651, 687–88 (2009) (noting the “perceived vulnerability” of the NPEA); Brendan O’Dell, Special Feature, Judicial Rewriting of Indian Employment Preferences—A Case Comment: E.E.O.C. v. Peabody Western Coal Company, 400 F.3d 774 (9th Cir. 2005), 31 Am. Indian L. Rev. 187, 204–05 (2006) (discussing the treatment by the Ninth Circuit of EEOC’s suit prior to final remand).

The Navajo Nation is not the only tribe with laws affording preference for tribal members; for more on Indian preference, see Jerry D. Stubben, Indian Preference: Racial Discrimination or a Political Right?, in American Indian Policy, supra note 72, at 103.

[354] Indian Energy Development: Hearing Before the S. Comm. on Indian Affairs, 110th Cong. 21 (May 1, 2008) (statement of Steven C. Begay, General Manager, Diné Power Authority, Navajo Nation) [hereinafter Indian Energy Development Hearing].

[355] Press Release, Office of the President & Vice President, Navajo Nation, supra note 353.

[356] Desert Rock Energy Co., Jobs and Taxes: Construction Jobs, http://www.desertrock energyproject.com/jobs_and_taxes.htm (last visited Apr. 18, 2010) (stating that the average salary is projected to be $60,000).

[357] For more on Sithe Global, see supra notes 24–25 and accompanying text.

[358] Off-road mining trucks will bring the coal from an open pit mine to the Desert Rock power plant. Steag Power, LLC, Application for Prevention of Significant Deterioration Permit for the Desert Rock Energy Facility 6-35 (2004); see also supra note 115 and accompanying text (discussing Black Mesa’s coal slurry and dedicated train that connect power plants with Black Mesa).

[359] Indian Energy Development Hearing, supra note 354, at 23 (prepared statement of Steven C. Begay, General Manager, Diné Power Authority, Navajo Nation).

[360] Desert Rock Energy Co., supra note 356.

[361] The plant will be primarily debt financed, allowing the tribe an option to purchase a 25% equity stake for $250 million. Christopher Helman, Beyond Casinos, Forbes, Mar. 16, 2009, at 88, 89. A 49% equity stake costs $400 million. Kathy Helms, DPA Request Denied: Power Authority Sought $2M for Desert Rock, Transmissions Projects, Gallup Indep. (Gallup, N.M.), Oct. 3, 2005, http://www.gallupindependent.com/2005/oct/100305dpa.html (last visited Apr. 18, 2010). Had the Navajo Nation won its $600 million breach of trust case, United States v. Navajo Nation, 129 S. Ct. 1547 (2009), against the United States, President Shirley’s plan was “to use some of the money to buy an equity stake in Desert Rock.” Helman, supra, at 89. Tellingly, in a press release, the Office of Navajo Nation President & Vice President highlighted the “opportunity for the Navajo Nation to acquire an ownership stake in the project.” Press Release, Office of the President & Vice President, Navajo Nation, supra note 353.

[362] See Steag Power LLC, supra note 358, at 6-35.

[363] Chamberlain, supra note 69, at 92.

[364] McCabe & Lewis, supra note 67, at 122–23 (focusing on oil and gas development).

[365] See Edmunds et al., supra note 340, at 292.

[366] Helman, supra note 361, at 88.

[367] Theresa Julnes, Economic Development as the Foundation for Self-Determination, in American Indian Policy, supra note 72, at 151, 155. Professor Gavin Clarkson’s articles focusing on improving tribal access to capital highlight both the legal barriers to, and possibilities of, improving tribal finance. See Gavin Clarkson, Accredited Indians: Increasing the Flow of Private Equity into Indian Country as a Domestic Emerging Market, 80 U. Colo. L. Rev. 285, 287–92, 325–26 (2009); Gavin Clarkson, Tribal Bonds: Statutory Shackles and Regulatory Restraints on Tribal Economic Development, 85 N.C. L. Rev. 1009, 1082–84 (2007); Gavin Clarkson,
Wall Street Indians: Information Asymmetry and Barriers to Tribal Capital Market Access,
12 Lewis & Clark L. Rev. 943, 952–58 (2008).

[368] Helman, supra note 361, at 88.

[369] As Philip Reno argued in 1981, “Resources still in Navajo hands, primarily coal, should be developed by the Tribe itself whenever possible.” Reno, supra note 58, at 151 (emphasis added).

[370] See Kerr-McGee Corp. v. Navajo Tribe of Indians, 471 U.S. 195 (1985); Merrion v. Jicarilla Apache Tribe, 455 U.S. 130 (1982). The ability of tribes to impose such severance or excise taxes despite an earlier tribal-corporate agreement regarding the royalty rate was affirmed by the Supreme Court in Merrion. Id. at 133–44. The case involved an Indian Reorganization Act–constituted tribal government whose decision was subject to review by the Secretary of the Interior. Three years later, Kerr-McGee extended the Merrion decision when the Court affirmed a similar tax by the Navajo Nation, a tribe without the secretarial approval requirement. Kerr‑McGee Corp., 471 U.S. at 196–201.

[371] According to Philip S. Deloria, the two hats that tribal governments have—that of the regulator and that of the landowner or entrepreneur—make resource development “more complex” on-reservation than off-reservation. Deloria, supra note 1, at 196.

[372] See Letter from Diné Citizens Against Ruining Our Env’t et al. to Harrilene Yazzie, NEPA  Coordinator, Bureau of Indian Affairs, Navajo Regional Office (Aug. 17, 2007), available at http://www.sanjuancitizens.org/air/FINAL%20DREF&20DEIS%20commentletter081707-1.pdf; Ctr.for Biological Diversity, Group Files Appeal on Permit for Desert Rock Plant, http://www.biologicaldiversity.org/news/center/articles/2008/kold-09-02-2008.html (last visited Apr. 18, 2010). More on these groups can be found on their websites. Ctr. for Biological Diversity, Center for Biological Diversity, http://www.biologicaldiversity.org (last visited Apr. 18, 2010); Envtl. Def. Fund, Environmental Defense Fund—Finding the Ways That Work, http://www.edf.org/home.cfm (last visited Apr. 18, 2010); Nat’l Parks Conservation Ass’n, National Parks Conservation Association: Protecting Our National Parks for Future Generations, http://www.npca.org (last visited Apr. 18, 2010); Natural Res. Def. Council, Natural Resources Defense Council: The Earth’s Best Defense, http://www.nrdc.org (last visited Apr. 18, 2010); Sierra Club, Sierra Club Home Page: Explore, Enjoy and Protect the Planet, http://www.sierraclub.org (last visited Apr. 18, 2010).

[373] More on the groups and their opposition to the project can be found on their websites. Grand Canyon Trust, Plateau-Wide Issues: Air Quality: Our Work with the Western  Clean Energy Coalition to Oppose the Desert Rock and Cemex Facilities, http://www.grandcanyontrust.org/plateau/air_actions.php (last visited Apr. 18, 2010); Conservation Voters N.M., CVNM Accomplishments, http://www.cvnm.org/About/Accomplishments.html (last  visited Apr. 18, 2010); N.M. Conference of Churches, The Environment, http://www.nmchurches.org/node/6 (last visited Apr. 18, 2010); San Juan Citizens Alliance, San   Juan Citizens Alliance, Air: Global Warming: Desert Rock Power Plant, http://www.sanjuancitizens.org/air/desertrock.shtml (last visited Apr. 18, 2010); W. Res. Advocates, New Mexico Coal Plants, http://www.westernresourceadvocates.org/energy/coal/newmexico.php (last visited Apr. 18, 2010).

[374] More on these groups can be found on their websites. Diné CARE, Welcome to Diné CARE, http://www.creativegeckos.com/dinecare/ (last visited Apr. 18, 2010); Doodá Desert Rock!, Stop the Desert Rock Energy Project, http://www.doodadesertrock.com/ (last visited Apr. 18, 2010). For a detailed account of the struggles of grassroots efforts to protect the environment among Diné civil society, focused on the foundation of Diné CARE and their work to protect against excessive logging on the reservation, see Sherry, supra note 124.

[375] See Dooda (No) Desert Rock, Hall of Fame: Dooda (No) Desert Rock: Causes.com, http://www.causes.com/causes/75652/hall_of_fame (last visited Apr. 18, 2010).

[376] Bureau of Indian Affairs, U.S. Dep’t of the Interior, Desert Rock Energy Project:  Draft Environmental Impact Statement, at ES-20 to -21 (2007), available at http://www.desertrockenergyeis.com/documents/presentations/Executive%20Summary.pdf.

[377] BIA takes the lead role preparing environmental impact statements (EISs) for projects with a significant impact on the environment, though other agencies and the governing tribe or tribes can become “cooperating agencies” for the purposes of the EIS. Judith V. Royster, Equivocal Obligations: The Federal-Tribal Trust Relationship and Conflicts of Interest in the Development of Mineral Resources, 71 N.D. L. Rev. 327, 338–39 (1995).

[378] Neither the DEIS nor an executive summary of the DEIS was available in Diné, the Navajo language, limiting the participation of those without command of English. Letter from Diné Citizens Against Ruining Our Env’t et al. to Harrilene Yazzie, supra note 372, at 28. The response to the DEIS authored by Diné CARE and other environmental groups notes, “[T]he DEIS—at two-volumes and 1,600 page[s]—is very much inaccessible to most Navajo community members.” Id. For the list of the meetings with the public and area officials that preceded publication of the DEIS, see Bureau of Indian Affairs, supra note 376, app. L, available at http://www.desertrockenergyeis.com/documents/presentations/Appendix%20L.pdf.

[379] Bureau of Indian Affairs, supra note 376, app.K, at K-37.

[380] Letter from Mike Eisenfeld, N.M. Staff Organizer, San Juan Citizens Alliance, to Harrilene Yazzie, NEPA Coordinator, Burea of Indian Affairs, Navajo Regional Office 12 (Oct. 4, 2007), available at http://www.sanjuancitizens.org/air/DESERT%20ROCK%20DEIS%20Comments%20 SJCA%2010-8-2007%20FINAL.pdf; see also Letter from Vickie Patton, Deputy Gen. Counsel, Envtl. Defense Fund, to Joseph Lapka, Air Permitting Program, U.S. Envtl. Prot. Agency (July 31, 2008) (on file with author) (arguing CO2 is subject to EPA regulation when considering Prevention of Significant Deterioration permit applications). The figure given by the plant’s developers is 10.9 million tons per year. Desert Rock Energy Co., Desert Rock Energy Project: Carbon Dioxide Facts, http://www.desertrockenergyproject.com/carbon_facts.htm (last visited Apr. 18, 2010). To give some context to these amounts, consider that Yale University was responsible for more than 300,000 tons per year of CO2 equivalent emissions from 2003 to 2008. Yale Office of Sustainability, Yale University Greenhouse Gas Emissions Inventory: Update 2003–2008, at 3 (2009), available at http://sustainability.yale.edu/sites/default/ files/GHG2008.pdf.

Note: The Environmental Defense Fund Supplemental Comments were contained in an online database, the Initial Prevention of Significant Deterioration Permit for the Desert Rock Energy Facility Docket folder on Regulations.gov, Docket ID: EPA-R09-OAR-2007-1110, http://www.regulations.gov/search/Regs/home.html#docketDetail?R=EPA-R09-OAR-2007-1110 (last visited Apr. 18, 2010). But given the challenges of subsequent researchers finding particular letters from this database, citations are to copies of the letter on file with author.

[381] Bureau of Indian Affairs, supra note 376, at 5-12, available at http://www.desertrockenergyeis.com/documents/presentations/Chapter%205%20-%20Cumulative%
20Impacts,%20Unavoidable%20Adverse%20Effects,%20and%20Irreversible%20and%20Irretrievable%20Commitment%20of%20Resources.pdf.

[382] Id. at 5-11.

[383] See id. at 1-1, available at http://www.desertrockenergyeis.com/documents/presentations/ Chapter%201%20-%20Introduction.pdf.

[384] Id. at 2-2 tbl.2-1, available at http://www.desertrockenergyeis.com/documents/ presentations/Chapter%202%20-%20Alternatives.pdf.

[385] See id. (providing acreage requirements for transmission lines, water wells, the main plant access road, and a coal preparation area); see also id. at 2-3 fig.2-1 (providing a planning map with anticipated land use acreage and sites).

[386] See id. at 2-7 to -8. The DEIS also includes water use figures in acre-feet per year (af/yr) rather than gpm; 4950 af/yr is equivalent to the 3070 gpm planned amount. This does not include the additional 600 af/yr “associated with the expansion of the surface mining operations at the Navajo Mine required to supply coal to the Desert Rock Energy Project.” Id. at 2-9.

[387] Id. at 2-15.

[388] Id. app. D, at D-1, available at http://www.desertrockenergyeis.com/documents/
presentations/Appendix%20D.pdf.

[389] Id. (giving the coal consumption figures); id. at 2-18, available at http://www.desertrock
energyeis.com/documents/presentations/Chapter%202%20-%20Alternatives.pdf (giving the plant’s design life).

[390] See id. app. D, at D-11 to -15, available at http://www.desertrockenergyeis.com/
documents/presentations/Appendix%20D.pdf.

[391] The tribe’s experience with Black Mesa reclamation attests to the limits of reclamation. According to Rebecca Reppert, the reclaimed area on Black Mesa had growing grass, “but not much else could be done with that area.” Letter from Rebecca Reppert, English Teacher, Red Mesa High Sch., to Robert T. Baker, U.S. Envtl. Prot. Agency (Oct. 24, 2006) (on file with author); see also Karyn I. Wendelowski, Comment, A Matter of Trust: Federal Environmental Responsibilities to Native Americans Under Customary International Law, 20 Am. Indian L. Rev. 423, 426 (1995) (arguing that Black Mesa reclamation efforts have been unsuccessful and that Peabody Coal has not taken “its reclamation obligations seriously”). For more on the challenges of reclamation and reclamation funding, see A. Brooke Rubenstein & David Winkowski, Comment, A Mine Is a Terrible Thing to Waste: Past, Present and Future Reclamation Efforts to Correct the Environmentally Damaging Effects of Coal Mines, 13 Vill. Envtl. L.J. 189, 199–204 (2002).

[392] See Leslie Linthicum, Proposed Coal-Fueled Plant on Navajo Land Worries Some Nearby Residents, Albuquerque J., June 26, 2005, at A1, available at 2005 WLNR 10133288 (“The desert floor fans out here like a dinner plate—flat, hot and empty. . . . Even by Navajo reservation standards, this place is empty and remote. A perfect place, some might imagine, to tuck away a new power plant to serve the energy-thirsty Southwest.”).

[393] Bureau of Indian Affairs, supra note 376, at 3-76, available at http://www.desertrock
energyeis.com/documents/presentations/Chapter%203%20-%20Affected%20Environment.pdf.

[394] In City of Sherrill, New York v. Oneida Indian Nation of New York (City of Sherrill), 544 U.S. 197 (2005), the Supreme Court held that the Oneida Indian Nation could not unify fee and Indian title within their original reservation through open market purchases. Id. at 202–03. The decision was based in part on a development bias: “[T]he properties here involved have greatly increased in value since the Oneidas sold them 200 years ago. Notably, it was not until lately that the Oneidas sought to regain ancient sovereignty over land converted from wilderness to become part of cities like Sherrill.” Id. at 215.

City of Sherrill is but the newest version of a Supreme Court bias that has been around since Chief Justice John Marshall’s opinion in Johnson v. M’Intosh, 21 U.S. (8 Wheat.) 543 (1823). According to Chief Justice Marshall, “[T]he tribes of Indians inhabiting this country were fierce savages . . . . To leave them in possession of their country, was to leave the country a wilderness; to govern them as a distinct people, was impossible.” Id. at 590.

[395] Bureau of Indian Affairs, supra note 376, at 3-85, available at http://www.desertrock
energyeis.com/documents/presentations/Chapter%203%20-%20Affected%20Environment.pdf.

[396] Id. at 2-7 fig.2-3, available at http://www.desertrockenergyeis.com/documents/ presentations/Chapter%202%20-%20Alternatives.pdf.

[397] See id. at 3-79 to -85, available at http://www.desertrockenergyeis.com/documents/ presentations/Chapter%203%20-%20Affected%20Environment.pdf.

[398] Steag Power LLC, supra note 358, at 6-25 to -32.

[399] Chuck Slothower, Officials Tout N.M.’s Desert Rock: Environmental Impact Minimal from Plant, They Say, Durango Herald (Durango, Colo.), Sept. 15, 2006, http://archive.durango
herald.com/asp-bin/article_generation.asp?article_type=news&article_path=/news/06/news0609
15_2.htm (last visited Apr. 18, 2010). The Four Corners Air Quality Task Force felt that the statement “epitomizes our perception of the sensitivity of [EPA] Region 9 personnel to the issues in the Four Corners region.” Four Corners Air Quality Task Force, Report of Mitigation Options 228 (2007), available at http://www.nmenv.state.nm.us/aqb/4C/Docs/
4CAQTF_Report_FINAL.pdf.

Public comments on Desert Rock highlighted the current pollution and haze problems associated with the existing plants. See, e.g., Proposed Clean Air Act Permit for Prevention of Significant Detioration of the Desert Rock Power Plant: Hearing Before the U.S. Envtl. Prot. Agency 26 (Oct. 4, 2006, afternoon session) (statement of Anthony Lee) (on file with author) [hereinafter EPA Hearing I] (“There’s too much smoke in the air, and it looks ugly.”); Letter from Rebecca Reppert to Robert T. Baker, supra note 391 (“I have seen the band of haze that crosses the desert near the Four Corners. I am against the construction of another coal‑fired plant . . . .”); Letter from Dorothy Barber-Redhorse, Resident, Little Water, to Robert T. Baker, U.S. Envtl. Prot. Agency Region 9 (Nov. 13, 2006) (on file with author). Dorothy Barber‑Redhorse urged,

[T]he aesthetic value should be kept as a factor as we see yellow to brown haze across the horizon every day. There are days when the haze is so bad that visibility is probably no more than thirty miles. The day when Four Corners Power Plant went down, the visibility was great.

Id.; see also Desert Rock Energy Facility Public Comments: Hearing Before the U.S. Envtl. Prot. Agency 17 (Oct. 3, 2006) (statement of Margie Connolly) (on file with author) [hereinafter EPA Hearing II] (“[O]n many days there’s this thick, ugly, yellow-brownish haze or smog that comes from the two existing power plants in the San Juan River Valley. Any additional deterioration from a coal-fired power plant is significant and should not be permitted.”); Letter from Loretta Annala to Robert Baker, U.S. Envtl. Prot. Agency Region 9 (Nov. 2, 2006) (on file with author) (“Since I moved to this area in 1966, I have observed the thick yellow clouds of pollution from the existing plants cut visibility to a fraction of what it should be.”); Letter from Jamie Stephens to Robert Baker, U.S. Envtl. Prot. Agency Region 9 (Sept. 23, 2006) (on file with author) (“Over the last few years, the air quality here has worsened dramatically. At times the mountains we used to see are almost obliterated by a yellow/brown haze . . . . This haze (smog) is a result of the coal-fired power plants we already have in our area.”).

Tellingly, haze from Arizona plants burning Black Mesa coal “cut sunlight by 15 percent downwind in Flagstaff, Arizona.” Krech, supra note 185, at 215.

[400] 5 U.S.C. § 552 (2006).

[401] Complaint, Dine Citizens Against Ruining Our Env’t v. Bradley, No. 08-CV-350 (D.N.M.  Apr. 2, 2008), available at http://www.sanjuancitizens.org/air/Filed%20Version%20FOIA %20Complaint%20Doc%201.pdf.

[402] Id. at 11, 12.

[403] Letter from Mike Eisenfeld to Harrilene Yazzie, supra note 380, at 35.

[404] Id. at 31.

[405] EPA Region 9’s Motion for Voluntary Remand at 1, In re Desert Rock Energy Co., PSD Permit No. AZP 04-01, (Envtl. Appeals Board, U.S. Envtl. Prot. Agency 2009), 2009 WL 3126170, available at http://www.epa.gov/region09/air/permit/desert-rock/docs/Desert-Rock-EAB-EPA-Motion-for-Voluntary-Remand.pdf [hereinafter EPA’s Motion for Remand]. This Motion for Voluntary Remand to the Environmental Appeals Board is the current form of the Obama Administration’s course reversal, though the Desert Rock litigation, appeals, and lobbying will no doubt continue, and therefore, the fate of the proposal is not yet finalized. See, e.g., Desert Rock Energy’s Response to EPA Region 9’s Motion for Voluntary Remand, In re Desert Rock Energy Co., PSD Permit No. AZP 04-01, (Envtl. Appeals Board, U.S. Envtl. Prot. Agency 2009), 2009 WL 3126170, available at http://yosemite.epa.gov/OA/EAB_WEB_Docket.nsf/Filings%20
By%20Appeal%20Number/915881434C6257B5852575D30059CEC0/$File/Motion%20for%20Remand%20…183.pdf.

[406] U.S. Envtl. Prot. Agency, Prevention of Significant Deterioration Permit, PSD  Permit No. AZP 04-01 (2008), available at http://www.desertrockenergyproject.com/ Final%20permit.pdf.

[407] Long Awaited Final Air Permit from the US EPA Issued, Desert Rock Energy Project (Desert Rock Energy Co., Houston, Tex.), Sept. 2008, at 1, available at http://www.desertrockenergyproject.com/Desert%20Rock%20Newsletter%200808%2015%20final.pdf.

[408] See Original Complaint, Desert Rock Energy Co., LLC v. EPA, No. H-08-872, 2009 WL 3247312 (S.D. Tex. Sept. 29, 2008), available at http://www.sanjuancitizens.org/ air/complaint.pdf. Suit was brought in the name of secondary institutions: Diné Power Authority, an organ of the Navajo Nation government, and Desert Rock Energy Company, a Sithe Global subsidiary. EPA’s Unopposed Motion to Lodge Consent Decree, Desert Rock Energy Co., LLC, 2009 WL 3247312 (S.D. Tex. Sept. 29, 2008), available at http://www.sanjuancitizens.org/air/Desert%20Rock%20consent%20decree.pdf.

[409] Press Release, U.S. Envtl. Prot. Agency Region 9, EPA Issues Air Permit for Desert Rock Energy Facility (July 31, 2008), http://yosemite.epa.gov/opa/admpress.nsf/2dd7f669225439b7852 5735 900400c31/8331e0972492f17c85257497005a37fb!OpenDocument (last visited Apr. 18, 2010) (internal quotation marks omitted).

[410] EPA Move Chagrins Desert Rock Developers, Coal Trader, Apr. 29, 2009, at 4, available at 2009 WLNR 9095762.

[411] Robin Bravender, EPA Wants to Review Permits for Navajo Nation Power Plant, N.Y. Times, Apr. 28, 2009, http://www.nytimes.com/gwire/2009/04/28/28greenwire-epa-wants-to-review-permits-for-navajo-nation-10707.html (last visited Apr. 18, 2010)

[412] See EPA’s Motion for Remand, supra note 405; Press Release, Joe Shirley, Jr., President, Navajo Nation, President’s Statement on Sovereignty Day (Apr. 27, 2009), available
at
http://www.navajo.org/News%20Releases/George%20Hardeen/Apr09/090427pres_President%20
Shirley’s%20statement%20on%20Sovereignty%20Day.pdf.

[413] Press Release, U.S. Envtl. Prot. Agency Region 9, supra note 409.

[414] Letter from Joe Shirley to Gerardo C. Rios, supra note 30.

[415] Letter from Joe Shirley, Jr., President, Navajo Nation, to Wayne Nastri, Reg’l Adm’r, U.S. Envtl. Prot. Agency Region 9, at 1 (May 28, 2005) (on file with author).

[416] Id. at 2.

[417] Id. (“According to the Navajo Division of Community Development, the stagnation of economic development in Navajo country has forced Navajo families to move to far away cities to find their livelihoods. . . . [W]ithout reducing outmigration, by 2012 more than half of the Navajo people may leave the Navajo reservation.”). In his State of the Navajo Nation address, President Shirley has argued that Desert Rock “will allow Navajos to remain in their homeland rather than seek economic opportunity beyond their own borders.” Joe Shirley, State of the Navajo Nation Address, supra note 28, at 5; see also Joe Shirley, Jr., President, Navajo Nation, State of the Navajo Nation Address at the 21st Navajo Nation Council 2 (Apr. 20, 2009), available at http://www.navajo.org/News%20Releases/George%20Hardeen/Apr09/090420pres_STATE%20OF
%20NAVAJO%20NATION%20ADDRESS,%20APRIL%2020%202009.pdf (“Desert Rock will bring hundreds of Navajos home to work on the project, and keep hundreds more from leaving to seek employment elsewhere.”).

The fear that half the population may have to leave the reservation by 2012 is not a new fear: In the 1940s, with some Navajos reported starving, “it was thought that half of the people must find a living elsewhere.” Underhill, supra note 125, at 259. But the oil development of the 1960s helped allow Navajos to stay on the reservation and led to a near doubling of the population. Id.

[418] Letter from Joe Shirley to Stephen L. Johnson, supra note 27, at 2.

[419] Id. at 3 (internal quotation marks omitted).

[420] As the general manager of Diné Power Authority noted in his prepared statement to the Senate Committee on Indian Affairs, “[D]elay costs the Navajo Nation approximately $5 million of desperately needed dollars every month.” Indian Energy Development Hearing, supra note 354, at 23 (prepared statement of Steven C. Begay, General Manager, Diné Power Authority, Navajo Nation).

[421] Letter from Joe Shirley, Jr., President, Navajo Nation, et al. to Stephen L. Johnson, Adm’r, U.S. Envtl. Prot. Agency 1 (Jan. 17, 2008) (on file with author).

[422] Id. at 1–2.

[423] See id. at 1.

[424] Id. at 2.

[425] Id. The margin in favor has remained fairly constant: In February 2009, “the council voted 71-to-8 to approve right-of-way legislation for the Desert Rock Energy Project.” Press Release, Office of the President & Vice President, Navajo Nation, Navajo President Joe Shirley, Jr., Pleased by Council Vote to Approve Desert Rock Energy Project Right-of-Way Permit (Feb. 28, 2009), available at http://www.navajo.org/News%20Releases/George%20Hardeen/Feb09/
090228presNavajo%20President%20pleased%20by%20approval%20of%20Desert%20Rock%20permit.pdf.

[426] Press Release, Bill Richardson, Governor, N.M., Governor Richardson Issues Statement  on Proposed Desert Rock Energy Facility 1 (July 27, 2007), available at http://www.sanjuancitizens.org/air/Richardson_pressrelease.pdf. Richardson’s public statement preceded—arguably something it should not have—his formal request regarding Desert Rock for government-to-government consultation, a process the state and the tribe had previously agreed to in order to resolve disputes. See Letter from Bill Richardson, Governor, New Mexico, to Joe Shirley, Jr., President, Navajo Nation 1 (Aug. 20, 2007) (on file with author).

[427] Press Release, Bill Richardson, supra note 426, at 2.

[428] Letter from Bill Richardson, Governor, N.M., & Gary K. King, Attorney Gen., N.M., to Stephen L. Johnson, Adm’r, U.S. Envtl. Prot. Agency, & Wayne Nastri, Reg’l Adm’r, U.S. Envtl. Prot. Agency Region 9, at 3 (June 19, 2008) (on file with author).

[429] See, e.g., Letter from Helen Kalin Klanderud, Mayor, City of Aspen, Colo., to Robert Baker, U.S. Envtl. Prot. Agency 1 (Mar. 20, 2007) (on file with author) (noting that the Aspen City Council was unanimously concerned with the effects of the Desert Rock on Aspen); Letter from Joelle Riddle, Chair, La Plata County Bd. of County Comm’rs, to Deborah Jordan, Dir., Air Div., U.S. Envtl. Prot. Agency Region 9 (July 16, 2008) (on file with author).

[430] Although describing resistance to Appalachian, and not Western, reservation strip-mining, an account of the creative work of local opposition groups and lawyers can be found in Dean Hill Rivkin et al., Strip Mining and Grassroot Resistance in Appalachia: Community Lawyering for Environmental Justice, 1 L.A. J. Pub. Int. (forthcoming 2010) (manuscript at 14–26), available at http://papers.ssrn.com/sol3/papers.cfm?abstract_id=1478549 (follow the “One-Click Download” hyperlink).

[431] Elouise Brown, Doodá Desert Rock!, Earth First! J., Mar.–Apr. 2007, at 14, 14.

[432] Dooda (No) Desert Rock Power Plant (2005) (on file with author) (petition signed by 1500 Four Corners residents).

[433] Letter from Lucy Willie, Member, Doodá Desert Rock Power Plant Comm., et al. to Steven Begay, Gen. Manager, Diné Power Auth., & Bill Skeet, BHP Billiton/BHP Navajo Coal Co. 1 (July 28, 2006) (on file with author). One member even signed the letter and a separate individualized response with a thumbprint. Letter from Louise Benally to Robert Baker, U.S. Envtl. Prot. Agency Region 9 (Oct. 24, 2006) (on file with author).

[434] See Shannon Shaw, Documenting Desert Rock, Santa Fe New Mexican, July 19, 2006, at C4, available at 2006 WLNR 12809289 (describing the origins of the photo exhibit). For the photos of those impacted, a protest in Window Rock, and the resistance camp, see Carlan Tapp, Question of Power, http://www.questionofpower.org/Pages/stories.html (follow the “click to view story” hyperlinks) (last visited Apr. 18, 2010).

[435] Lisa Meerts, Desert Rock Officials Get Court Order to Access Site, Daily Times (Farmington, N.M.), Dec. 21, 2006, available at LEXIS; Lisa Meerts, Protestors Stop Work on Power Plant, Daily Times (Farmington, N.M.), Dec. 13, 2006, available at LEXIS.

[436] Lisa Meerts, Desert Rock Protesters Reach Agreement, Daily Times (Farmington, N.M.), Jan. 3, 2007, available at LEXIS.

[437] For resistance camp construction photographs, see Carlan Tapp, Desert Rock Resistance Camp, http://www.questionofpower.org/qp3/index.html (last visited Apr. 18, 2010).

[438] Moises Velasquez-Manoff, Before Regulation Hits, a Battle Over How to Build New Coal Plants, Christian Sci. Monitor, Feb. 22, 2007, at 13.

[439] Leslie Linthicum, A Question of Power: Coal-Fired Plant on Navajo Land Called a Cleaner Energy Source, But Critics Say Land, People Will Pay the Price, Albuquerque J., July 15, 2007, at B1, available at 2007 WLNR 13533062.

[440] See Cornelia de Bruin, Breaking News: EPA Issues Desert Rock Air Permit, Daily Times (Farmington, N.M.), July 31, 2008, available at LEXIS (noting intent of both Doodá Desert Rock and Diné CARE to challenge the permit in court).

[441] Elouise Brown, Letter to the Editor, What’s Next for Desert Rock?, Daily Times (Farmington, N.M.), Feb. 11, 2009, available at LEXIS.

[442] Proposed Clean Air Act Permit for Prevention of Significant Deterioration of the Desert Rock Power Plant: Hearing Before the U.S. Envtl. Prot. Agency 8 (Oct. 4, 2006, evening session) (statement of Albert Shirley, Office of the Majority Leader, New Mexico House of Representatives) (on file with author) [hereinafter EPA Hearing III] (“[Y]ou can’t really believe Desert Rock when it tells you that there is no opposition to this project. You can’t believe the media when they tell you that all the Navajo people are in opposition to this proposal.”).

[443] Leslie Linthicum, Power Struggle, Albuquerque J., June 26, 2005, at A1, available at 2005 WLNR 10133288.

[444] Impacts on grazing rights or hogans might be more likely to raise the objections of educated Navajos “willing to participate in development, but [who] are not happy about an outcome in which the traditional way of life for their parents is sacrificed.” Schoepfle et al., supra note 54, at 901.

Locals who benefit from the project may strongly support Desert Rock. Clayton Benally, a union engineer from Shiprock, New Mexico, told a Desert Rock panel, “This project would mean that these people would come back home to work here at home, to be part of their families, to watch their children grow, to enjoy all that a family unit has to enjoy. Like I said, I support this project.” EPA Hearing III, supra note 442, at 26 (statement of Clayton Benally); see also Facsimile from Lyla Ransdell, Field Representative, Mountain W. Reg’l Council of Carpenters, to Robert Baker, U.S. Envtl. Prot. Agency (Oct. 3, 2006) (on file with author) (letter from a local carpenter’s union expressing support for Desert Rock).

[445] Letter from Steven C. Begay, Gen. Manager, Diné Power Auth., to Robert Baker, U.S. Envtl. Prot. Agency Region 9, at 2 (Nov. 13, 2006) (on file with author).

[446] Linda Kruger & Graciela Etchart, Forest-Based Economic Development in Native American Lands: Two Case Studies, in American Indian Policy, supra note 72, at 191, 193.

[447] Keller & Turek, supra note 39, at 186.

[448] Navajo Nation v. U.S. Forest Serv., 535 F.3d 1058, 1101 (9th Cir. 2008).

[449] Kruger & Etchart, supra note 446, at 193.

[450] Public comments on Desert Rock make a similar point about the Washington, D.C.–Four Corners separation, an accusation rejected by EPA: “We disagree that EPA’s PSD permit treats the Four Corners area as a ‘sacrifice’ zone.” U.S. Envtl. Prot. Agency Region 9, EPA Responses to Public Comments on the Proposed Prevention of Significant Deterioration Permit for the Desert Rock Energy Facility 152 (2008); see also Kuletz, supra note 198, at 13 (describing the southwest areas used for nuclear weapon development as “a landscape of national sacrifice, an expendable landscape”).

[451] Natasha Kaye Johnson, Shirley, Shelly Prevail: Incumbent First to Win Back‑Back Elections Since 1982, Gallup Indep. (Gallup, N.M.), Nov. 8, 2006, http://www.gallup
independent.com/2006/nov/110806nkj_shrlyshlly.html (last visited Apr. 18, 2010).

[452] Joe Shirley, Jr., Native America and the Rule of Law, 42 U. Rich. L. Rev. 59, 60 (2007).

[453] EPA Hearing I, supra note 399, at 89 (statement of Arnold Clifford).

[454] EPA Hearing II, supra note 399, at 72–73 (statement of Steve Cone) (continuing by calling Desert Rock “a classic land grab”).

[455] See Ariz. Pub. Serv. Co. v. EPA, 562 F.3d 1116, 1119 (9th Cir. 2009) (explaining EPA oversight of facilities on tribal lands under the Clean Air Act).

[456] See, e.g., Press Release, Office of the President & Vice President, Navajo Nation, Navajo Nation President Joe Shirley, Jr., Stands with Hopi Tribe in Opposition to Environmental Groups’ Interference in Sovereignty 2 (Sept. 30, 2009), available at http://www.navajo.org/News
%20Releases/George%20Hardeen/Sept09/090930presvajo%20president%20stands%20with%20Hopi%20Tribe%20in%20opposition%20to%20environmental%20groups%20interference%20in%20sovereignty.pdf (opining that, despite “overwhelming support” for the Desert Rock project, the Navajo Nation Council’s “greatest opposition comes from environmentalists . . . . [M]any of these people don’t know about Navajos, sovereignty or self-determination”).

[457] See, e.g., Letter from Sanjay Narayan, Staff Attorney, Sierra Club Envtl. Law Program, to Robert Baker, U.S. Envtl. Prot. Agency Region 9 (Nov. 10, 2006) (on file with author) (discussing the permit’s failure to meet the best available control technology standard and enforceability issues).

[458] This idea is more fully developed in Part V.A, supra.

[459] E-mail from Julie Lee to U.S. Envtl. Prot. Agency (Jan. 5, 2007) (on file with author).

[460] U.S. Envtl. Prot. Agency Region 9, supra note 450, at 193.

[461] EPA Hearing III, supra note 442, at 20 (statement of Gloria Emerson) (on file with author).

[462] EPA Hearing I, supra note 399, at 40 (statement of Nelson Lee Simms) (focusing on the EPA in particular).

[463] See, e.g., Joe Hanel, EPA to Reconsider Power Plant Permit, Durango Herald (Durango, Colo.), Sept. 26, 2009, http://durangoherald.com/sections/News/2009/09/26/EPA_to_ reconsider_ power_plant_permit/ (last visited Apr. 18, 2010) (discussing EPA’s reconsideration of the permit for the Desert Rock facility, and the responses to EPA’s decision to reconsider by both coal power opponents and Navajo leaders).

[464] See Walker et al., supra note 205, at 382, 392–93.

[465] See Michael C. Blumm, Public Choice Theory and the Public Lands: Why “Multiple Use” Failed, 18 Harv. Envtl. L. Rev. 405, 406 (1994) (stating that early public land laws that gave “private property rights in water and mineral resources . . . are a major cause of the enormous amount of environmental destruction in the West”).

[466] Wiggins, supra note 186, at 345 (beginning the article by asking how environmentalists should respond to such proposals).

[467] Judith V. Royster & Michael C. Blumm, Native American Natural Resources Law: Cases and Materials 217 (2002) (emphasis added).

[468] Professor Richard Monette explains that for “tribes, being treated as states meant at least being treated fairly.” Richard A. Monette, Treating Tribes as States Under Federal Statutes in the Environmental Arena: Where Laws of Nature and Natural Law Collide, 21 Vt. L. Rev. 111, 114 (1996).

[469] Id. (“[B]eing treated as states meant at least being treated fairly.”).

[470] Or, as Professor Royster argues, “Tribal control of federal programs is thus better than federal control, but a clear second-best to tribal choices of what programs and development opportunities to pursue.” Royster, supra note 96, at 1070.

[471] Indian Tribal Energy Development and Self-Determination Act of 2005, Pub. L. No. 109-58, §§ 501–06, 119 Stat. 594, 763–79 (codified in scattered sections of U.S.C.).

[472] Royster, supra note 96, at 1082, 1090.

[473] United States v. Kagama, 118 U.S. 375, 384 (1886).

[474] Trade and Intercourse Act of 1790, ch. 33, 1 Stat. 137 (1790) (current version at 25 U.S.C. § 177 (2006)); see also Non-Intercourse Act of 1809, ch. 24, 2 Stat. 528 (repealed 1815). The risks of a diminished federal role are further explored in Forced Federalism: Contemporary Challenges to Indigenous Nationhood by Professor Jeff Corntassel and Richard C. Witmer, which focuses on how, “given the devolution of federal powers to states, indigenous nations have become more vulnerable to the jurisdictional claims of local governing bodies, such as state and municipal policymakers.” Jeff Corntassel & Richard C. Witmer, Forced Federalism: Contemporary Challenges to Indigenous Nationhood 5 (2008).

[475] 31 U.S. (6 Pet.) 515 (1832).

[476] Id.

[477] Id. at 519.

[478] William C. Canby, Jr., The Status of Indian Tribes in American Law Today, 62 Wash. L. Rev. 1, 6 (1987).

[479] Robert N. Clinton, There Is No Federal Supremacy Clause for Indian Tribes, 34 Ariz. St. L.J. 113, 133 (2002).

[480] Id. at 162–235 (detailing the history of the Supreme Court’s approval of congressional, colonialist-driven plenary power and creation of judicial plenary power); see also Robert N. Clinton, The Dormant Indian Commerce Clause, 27 Conn. L. Rev. 1055, 1058 (1995) (“The thesis of this article is that the Supreme Court’s rejection in Cotton Petroleum of any viable Indian Commerce Clause limitations on state authority represents an historically untenable interpretation of the clause, and therefore, constitutes an exercise of contra-constitutional interpretation.”).

[481] Frank Pommersheim, Braid of Feathers: American Indian Law and Contemporary Tribal Life 39 (1995). Given the diminishment of sovereignty at the hands of Congress and the judiciary, Professor Pommersheim has suggested that it is time “to more fully consider the necessity for an amendment to the United States Constitution that expressly recognizes tribal sovereignty.” Frank Pommersheim, Is There a (Little or Not So Little) Constitutional Crisis Developing in Indian Law?: A Brief Essay, 5 U. Pa. J. Const. L. 271, 285 (2003); see also Frank Pommersheim, Broken Landscape: Indians, Indian Tribes, and the Constitution 295–312 (2009) [hereinafter Pommersheim, Broken Landscape] (discussing the political feasibility of such an amendment).  Likewise, Professor Robert Laurence would like “to ratchet the sovereignty doctrine higher now, and then lock it in place by declaring it to be a constitutional doctrine.” Laurence, supra note 192, at 6.

[482] It has been argued that “[m]any federal environmental statutes . . . grant Indian tribes a great deal of sovereignty and in so doing preempt states from applying their laws to Indian tribes.” Cluett, supra note 215, at 198. But what this description misses—besides the characterization as a “grant” rather than a “recognition” of sovereignty—is that it is sovereignty “coupled with the federal plenary power over Indian affairs [that] explains why state regulatory laws generally never apply to tribes and tribal lands.” Walker et al., supra note 205, at 383.

[483] Peter D. Lepsch, A Wolf in Sheep’s Clothing: Is New York State’s Move to Cleanup the Akewsasne Reservation an Endeavor to Assert Authority over Indian Tribes?, 8 Alb. L. Envtl. Outlook J. 65, 69 (2002).

[484] Id. at 70.

[485] Id. at 107.

[486] Id.

[487] E-mail from Alaska Inter-Tribal Council to Ezra Rosser (July 31, 2009, 20:53) (on file with author); Derek C. Haskew, Federal Consultation with Indian Tribes: The Foundation of Enlightened Policy Decisions, or Another Badge of Shame?, 24 Am. Indian L. Rev. 21, 21–23 (1999) (exploring the requirement that the federal government consult with tribes on matters affecting them); see also Letter from Clarence Alexander, Executive Bd. Chair, Yukon River Inter-Tribal Watershed Council, to Nina Kocourek, Office of Water & Watersheds, U.S. Envtl. Prot. Agency 2 (Aug. 18, 2008) (on file with author) (“The state of Alaska has taken a ‘hands off’ approach to government consultation with the Tribes of Alaska.”). One of the fears tribes might have is that a state empowered to implement federal environmental regulatory authority that contained protribal elements—such as a consultation requirement—might deliberately undermine federal objectives the state was tasked with putting into effect. See generally Jessica Bulman-Pozen & Heather K. Gerken, Uncooperative Federalism, 118 Yale L.J. 1256 (2009) (exploring state use of federally delegated authority in ways opposed to federal goals).

[488] As Professor Grijalva notes, “Opponents of tribal sovereignty sometimes . . . perceive the only appropriate resolution of state objections is forcing differing tribal values to yield.” Grijalva, supra note 15, at 115.

[489] The tension between space and control explains one author stating that “[t]he decision to build waste disposal facilities should be left entirely to the tribes themselves,” and then continuing in the same paragraph by writing, “Still, the decision to enter the waste management business requires assurance that compliance with environmental laws will be stringent.” Sehgal, supra note 211, at 433–34.

[490] Nance v. EPA, 645 F.2d 701, 704–05 (9th Cir. 1981).

[491] Id. at 714.

[492] James M. Grijalva, The Origins of EPA’s Indian Program, 15 Kan. J.L. & Pub. Pol’y 191, 214 (2006).

[493] Carol Tebben, An American Trifederalism Based upon the Constitutional Status of Indian Nations, 5 U. Pa. J. Const. L. 318, 318 (2003). Professor Tebben’s thesis is that tribes are part of the constitutional structure of the United States, id., something this Article moves away from in Part III. But regardless of how tribes are classified, they should not be simply ignored.

[494] William H. Rodgers, Jr., Treatment as Tribe, Treatment as State: The Penobscot Indians and the Clean Water Act, 55 Ala. L. Rev. 815, 816 (2004).

[495] William D. Ruckelshaus, U.S. Envtl. Prot. Agency, EPA Policy for the Administration of Environmental Programs on Indian Reservations 1 (1984), available at http://www.epa.gov/tribalportal/pdf/indian-policy-84.pdf.

[496] Id. at 2. The Policy provided for encouraging tribal assumption of regulatory and program management, but with EPA retaining responsibility until tribes were interested in and capable of taking on such a role. Id.; see also President’s Special Message to the Congress on Indian Affairs, 1970 Pub. Papers 564, 568 (July 8, 1970) (arguing that, under the self-determination initiatives Nixon introduced with the speech, “Indian control of Indian programs would always be a wholly voluntary matter”). For more on the 1984 EPA Policy, see Dean B. Suagee, The Supreme Court’s “Whack-A-Mole” Game Theory in Federal Indian Law, a Theory That Has No Place in the Realm of Environmental Law, Great Plains Nat. Resources J., Fall 2002, at 90, 124–25.

[497] City of Albuquerque v. Browner, 97 F.3d 415, 423 (10th Cir. 1996). For more on the case and the issue of tribal water quality standards, see Janet K. Baker, Tribal Water Quality Standards: Are There Any Limits?, 7 Duke Envtl. L. & Pol’y F. 367 (1997).

[498] Lincoln L. Davies, Skull Valley Crossroads: Reconciling Native Sovereignty and the Federal Trust, 68 Md. L. Rev. 290, 365 (2009).

[499] Id. at 334.

[500] Ali, supra note 11, at 36.

[501] Davies, supra note 498, at 339–40.

[502] Id. at 343; see also David Rich Lewis, Skull Valley Goshutes and the Politics of Nuclear Waste: Environment, Identity, and Sovereignty, in Native Americans and the Environment: Perspectives on the Ecological Indian 304, 304 (Michael E. Harkin & David Rich Lewis eds., 2007) (highlighting Utah governor Michael Leavitt’s vocal opposition to the Goshute plan).

[503] Davies, supra note 498, at 346 (quoting Press Release, Office of U.S. Senator Orrin G. Hatch, Utahns Deliver Killing Blow to Skull Valley Nuke Waste Plan (Sept. 7, 2006), http://hatch.senate.gov/public/index.cfm?FuseAction=PressReleases.View&PressRelease_id=6bf6bbe-b834-4ebb-a950-19e629e35706 (quoting Senator Hatch)).

[504] Id. at 374–76. Under this proposal, tribes would decide whether or not to switch to such a position, just as they had decided whether to opt into IRA during the New Deal. A key difference is that under Professor Davies’s model, opting in would also protect tribes from Congressional and judicial diminishment of tribal sovereignty. Id. at 367.

[505] Id. at 371.

[506] Id. at 370.

[507] Professor Richard Monette explains that Republican Party objections to federal bureaucracy and preference for local regulation led to the current form of federal primacy with state administration: “The federal government assumed primacy over environmental regulation, but its programs ‘devolved’ to the states to administer. It is a mistake to believe, however, that the EPA has delegated such programs to the states.” Richard Monette, Environmental Justice and Indian Tribes: The Double-Edged Tomahawk of Applying Civil Rights Laws in Indian Country, 76 U. Det. Mercy L. Rev. 721, 735 (1999).

[508] Davies, supra note 498, at 371–72 (“[S]ome tribes might see that kind of moderation as a dilution of their historical sovereignty—particularly when that sovereignty is couched in terms of the full nation-like sovereignty tribes theoretically enjoy, or even in terms of sovereignty exercised in a way that seeks to minimize federal contact—and therefore might choose not to partake in the tradeoff. Others, of course, may adopt a more practical view . . . .”).

[509] Professor Judith Royster argues that when it comes to mineral leasing, the Secretary of the Interior cannot “subordinate the best interests of the tribes to public values or the national interest,” including environmental interests, because federal statutes governing such leasing impose a fiduciary duty on the Secretary to tribal mineral owners. Royster, supra note 377, at 364. This trust obligation may not reach all other agencies when it comes to environmentally harmful mineral development and, as the Navajo Nation II case shows, the U.S. government does not always live up to its trust obligations.

[510] As Professor Imre Sutton, the scholar who perhaps has done the most work on Indian geography and the nature of reservation land, explains, “[A] reservation provides the base and the locus for the functioning of the tribe as a political or jural entity within its own bounds, but this should not be construed to mean that the reservation is a distinct and separate political unit equivalent to a state, a county, or even a municipality.” Imre Sutton, Sovereign States and the Changing Definition of the Indian Reservation, 66 Geographical Rev. 281, 287 (1976); see also Marren Sanders, Clean Water in Indian Country: The Risks (and Rewards) of Being Treated in the Same Manner as a State, 36 Wm. Mitchell L. Rev.  533, 551 (2010) (describing imposition of EPA standards as an “affront to the sovereignty” of some tribes).

[511] Mary Christina Wood, Fulfilling the Executive’s Trust Responsibility Toward the Native Nations on Environmental Issues: A Partial Critique of the Clinton Administration’s Promises and Performance, 25 Envtl. L. 733 (1995) [hereinafter Wood, Partial Critique]; see Wood, supra note 325; Mary Christina Wood, Protecting the Attributes of Native Sovereignty: A New Trust Paradigm for Federal Actions Affecting Tribal Lands and Resources, 1995 Utah L. Rev. 109 [hereinafter Wood, New Trust Paradigm].

[512] See Wood, New Trust Paradigm, supra note 511, at 143 (“Otherwise, the federal trust obligation essentially collapses into a rule of absolute deference to a tribal council’s decision . . . .”).

[513] See id. at 141 (“[T]he government should achieve a degree of protection that is appropriate to protect the tribe’s way of life on the reservation, even if this level of protection exceeds what is otherwise mandated by statutory law.”); id. at 227 (“[C]ourts should enforce the procedural mandate of the trust obligation independent of the statutory procedures called for by NEPA.”).

[514] See id. at 111.

[515] Navajo Nation I, 537 U.S. 488, 506 (2003) (quoting United States v. Mitchell, 463 U.S. 206, 225 (1983)). The Indian trust doctrine is firmly established as a principle of federal Indian law that has been acknowledged repeatedly by the Supreme Court. See, e.g., Seminole Nation v. United States, 316 U.S. 286, 296 (1942) (“[T]his Court has recognized the distinctive obligation of trust incumbent upon the Government in its dealings with these dependent and sometimes exploited people.”).

[516] See supra notes 158–74 and accompanying text.

[517] The judiciary is not alone in its skepticism regarding the trust doctrine:

[T]he Department of [the] Interior has begun to distance itself from any notion of a general trust responsibility. In decision-making documents, the Department of the Interior once embraced the trust responsibility, often using it as an alternative basis for a decision in many areas of Indian affairs. In more recent years, Interior has been much more guarded, rarely mentioning the trust responsibility.

Kevin K. Washburn, Remarks at Harvard Law School Panel Discussion (Mar. 20, 2008), in Kevin  K. Washburn et al., Paternalism or Protection? Federal Review of Tribal Economic Decisions in Indian Gaming 2, 3 (Ariz. Legal Studies Working Paper Group, Discussion Paper No. 08-25, 2008), available at http://ssrn.com/abstract=1226542 (follow “One-Click Download” hyperlink).

[518] Wood, supra note 325, at 1496.

[519] See Wood, New Trust Paradigm, supra note 511, at 235–36.

[520] Id. at 113.

[521] See Wood, supra note 325, at 1558–64 (arguing federal government review of tribal council decisions may be the only way to review environmental impacts that prevent preservation of the traditional way of life).

[522] Professor Wood’s faith in the trust doctrine and federal oversight is surprising given the Navajo Nation facts and record of BIA, which “in balancing its trust responsibilities with Indian self-determination, has both squandered tribal resources and saved tribes from short-sighted expediency and greed.” David Rich Lewis, Still Native: The Significance of Native Americans in the History of the Twentieth-Century American West, 24 W. Hist. Q. 203, 216 (1993).

[523] Wood, supra note 325, at 1564.

[524] Id. at 1480. (“As a practical matter, however, the BIA simply approves transactions that tribal governments support.”).

[525] See id. at 1537–40 (explaining and critiquing the dismissal along “indispensible party” grounds of two such cases). For more on tribal sovereign immunity, see Note, In Defense of Tribal Sovereign Immunity, 95 Harv. L. Rev. 1058 (1982).

In some respects, Professor Woods seems to agree with judicial hesitation. Although the first law review article advocates “aggressive judicial enforcement,” Wood, supra note 325, at 1569, the subsequent article offers a clarification: “A prudent judicial approach to such conflicts might be to reserve decisions that depart from tribal council prerogatives for those cases presenting extreme circumstances.” Wood, New Trust Paradigm, supra note 511, at 145.

[526] Wood, supra note 325, at 1480 (“[C]hallenges typically originate from dissenting individuals within the tribe.”); id. at 1536 (“Given this deference to the tribal council, the only parties who would likely challenge the federal approval decision on trust grounds are individual Indian plaintiffs or groups of tribal members who are opposed to the decision made by the tribal council.”); see also Louis G. Leonard, III, Sovereignty, Self-Determination, and Environmental Justice in the Mescalero Apache’s Decision to Store Nuclear Waste, 24 B.C. Envtl. Aff. L. Rev. 651, 674 (1997) (“The Trust Doctrine may be used in this way by tribal members to challenge practices such as the BIA’s approval power over land uses . . . .”).

[527] Wood, New Trust Paradigm, supra note 511, at 149 (“[A] court should consider the permanency of the land use, its relation to existing and future spacial needs of the tribe, and collateral effects which may further detract from the usable land base.”).

[528] Wood, supra note 325, at 1562–64.

[529] Id. at 1551; see also Wood, New Trust Paradigm, supra note 511, at 156–57 (“Second guessing tribal council decisions, even in a broad policy context, may affront contemporary notions of tribal sovereignty.”).

[530] Wood, supra note 325, at 1550; see also Wood, New Trust Paradigm, supra note 511, at 128.

[531] Wood, supra note 325, at 1540–41 (“[T]he presumption that the tribal government always provides an adequate forum of redress for tribal members may be unwarranted.”). Government processes go beyond providing redress, and it similarly has been asserted that the trust responsibility is important based on the argument that “some tribes do not have the institutional and enforcement mechanisms needed to guarantee that tribal resources will be developed responsibly.” Andrea S. Miles, Note, Tribal Energy Resource Agreements: Tools for Achieving Energy Development and Tribal Self-Sufficiency or an Abdication of Federal Environmental and Trust Responsibilities?, 30 Am. Indian L. Rev. 461, 472 (2006).

[532] Wood, New Trust Paradigm, supra note 511, at 143, 167.

[533] Id. at 143. Tribal councils are not alone in having a limited ability to resist; the same can  be true of the federal agencies. See Wood, Partial Critique, supra note 511, at 746 (“These private stake-holders often exert overwhelming pressure on agencies to render decisions favorable to them, and often public or environmental values fall sway to more immediate and quantifiable economic interests.”).

[534] Wood, supra note 325, at 1568–69 (emphasis added); see also Leonard, supra note 526, at 689 (making a similar argument—that “the federal government is now using the concept of tribal sovereignty as an excuse”—regarding the siting of nuclear waste on Indian reservations).

[535] Wood, supra note 325, at 1564 (emphasis added).

[536] Wood, New Trust Paradigm, supra note 511, at 221.

[537] Professor Wood writes, “[T]he trust obligation to protect tribal resources should often translate into a higher level of ecological protection than that which might result when solely non-Indian interests are affected.” Wood, Partial Critique, supra note 511, at 745. A heightened reservation standard reflects Professor Wood’s disdain for the relationship non-Indian society has with the environment. Professor Wood notes the “ominous horizon of ecological damage that haunts the majority’s industrial society,” Wood, supra note 325, at 1569, and later describes the indigenous model as “the very antithesis of the industrial model,” Wood, New Trust Paradigm, supra note 511, at 153.

Professor Wood is not alone in her disdain for the relationship of non-Indian society to the environment; Professor Rebecca Tsosie begins her article on self-determination and the environment by writing of the United States as “a nation faced with the dismal legacy of overdevelopment.” Tsosie, supra note 71, at 225.

[538] Wood, New Trust Paradigm, supra note 511, at 163.

[539] Wood, supra note 325, at 1568.

[540] Wood, Partial Critique, supra note 511, at 740.

[541] Wood, New Trust Paradigm, supra note 511, at 181; see also Wood, supra note 325,
at 1561 (“A negative approval, whether emanating from the BIA or a court reviewing the BIA’s decision, represents less of a directive on how the tribe should use its land and more of a restraint on the particular private firm seeking to access the reservation’s resources.”).

[542] Wood, New Trust Paradigm, supra note 511, at 235.

[543] For more on the stereotyping of Indians as environmentalists, see supra Part III.

[544] Wood, New Trust Paradigm, supra note 511, at 143; see also Wood, supra note 325, at 1562 (“[I]nternal dissension over such offers [as waste facilities] is often muted in the outside policy realm by an overall appearance of tribal willingness created by the tribal government’ own sponsorship of the waste proposal.”); id. at 1567 (“[T]he deep aversion of a significant portion of the native population to industrial development of their lands is largely overlooked in the face of tribal council approvals . . . .”).

[545] Wood, supra note 325, at 1558.

[546] See, e.g., Helman, supra note 361, at 88 (discussing the Desert Rock power plant).

[547] See id. (explaining that the initial Desert Rock proposal came at a time of “rampant power plant construction . . . spurred by rolling blackouts across California”).

[548] Rebecca Tsosie, Tribal Sovereignty and Intergovernmental Cooperation, in Tribal Water Rights: Essays in Contemporary Law, Policy, and Economics 13, 30 (John E. Thorson et al. eds., 2006).

[549] The “development of intergovernmental agreements” is identified as a “trend” by a Harvard Law Review note exploring the advantages and risks of cooperative agreements.
Note, Intergovernmental Compacts in Native American Law: Models for Expanded Usage,
112 Harv. L. Rev. 922, 922 (1999).

[550] Michael A. Burnett, The Dilemma of Commercial Fishing Rights of Indigenous Peoples: A Comparative Study of the Common Law Nations, 19 Suffolk Transnat’l L. Rev. 389, 421 (1996).

[551] Walker & Gover, supra note 233, at 250 (calling such agreements a way to avoid litigation and political battles around nuclear waste in Indian country).

[552] Kristina M. Reader, Case Note, Empowering Tribes: The District of Columbia Circuit Upholds Tribal Authority to Regulate Air Quality Throughout the Reservation Lands in Arizona Public Service Company v. Environmental Protection Agency, 12 Vill. Envtl. L.J. 295, 329 (2001).

[553] Johnson, supra note 196, at 528.

[554] Collins & Hall, supra note 130, at 343.

[555] Robert N. Clinton, Comity & Colonialism: The Federal Courts’ Frustration of Tribal‑Federal Cooperation, 36 Ariz. St. L.J. 1, 20 (2004); Rachel San Kronowitz et al., Comment, Toward Consent and Cooperation: Reconsidering the Political Status of Indian Nations, 22 Harv. C.R.-C.L. L. Rev. 507, 584–85 (1987) (using cross-deputization agreements as an example of a pragmatic solution to a local problem that does not deny Indians their sovereignty).

[556] Alex Tallchief Skibine, Reconciling Federal and State Power Inside Indian Reservations with the Right of Tribal Self-Government and the Process of Self-Determination, 1995 Utah L. Rev. 1105, 1156.

[557] Id. at 1108.

[558] P.S. Deloria & Robert Laurence, Negotiating Tribal-State Full Faith and Credit Agreements: The Topology of the Negotiation and the Merits of the Question, 28 Ga. L. Rev. 365, 382 (1994).

[559] Charles Wilkinson & The Am. Indian Res. Inst., Indian Tribes As Sovereign Governments 48 (2d ed. 2004).

[560] Tsosie, supra note 548, at 34. But, as Judge Canby notes, even if the importance of
tribal-state negotiations increases, court decisions help establish “the legal armament that each side brings to the negotiating table.” Canby, supra note 478, at 22.

[561] Matthew L.M. Fletcher, Retiring the “Deadliest Enemies” Model of Tribal-State Relations 24 (Mich. State Univ. Coll. of Law Working Paper Group, Research Paper No. 05-03, 2007), available at http://ssrn.com/abstract=1007756 (follow “One-Click Download” hyperlink).

[562] Id. at 26.

[563] Laurence, supra note 192, at 19 (emphasis added) (discussing the desirability of a new treaty-making era).

[564] See Ezra Rosser, Caution, Cooperative Agreements, and the Actual State of Things: A Reply to Professor Fletcher, 42 Tulsa L. Rev. 57 (2006).

[565] Moreover, the back and forth between tribes and non-Indian governments over tribally proposed projects may reduce the possibility of future agreements, even on unrelated issues. Professor Philip Frickey gives an example of a negotiation that succeeded because, rather than being about a single controversy, the parties approached the negotiations “with an eye towards accommodating . . . the long-term relationship as well.” Philip P. Frickey, Adjudication and Its Discontents: Coherence and Conciliation in Federal Indian Law, 110 Harv. L. Rev. 1754, 1780–81 (1997). But importantly, the negotiations were between the tribe and the federal government and did not involve state or local governments. Id.

[566] Laurence, supra note 192, at 22.

[567] This approach borrows from Professor Robert Porter’s definition of indigenous sovereignty as “freedom of a people to choose what their future will be.” Robert B. Porter, The Meaning of Indigenous Nation Sovereignty, 34 Ariz. St. L.J. 75, 75 (2002).

[568] While laws allowing tribes to take over traditionally federal roles and service provisions are a start, their coverage as far as governance is limited, and more “importantly, they frame the services being carried out first and foremost as federal obligations—not the tribe’s.” Davies, supra note 498, at 367.

[569] This is true notwithstanding the conclusion of a 1992 EPA study that “[t]ribal programs could translate traditional cultural and spiritual values into . . . the substantive requirements of pollution permits issued under the modern federal environmental programs.” Grijalva, supra note 15, at 11–12.

[570] Sam Deloria highlights the complications associated with “sovereignty”:

[W]e should take the word sovereignty and put it on the shelf for about ten years because it is a very confusing concept to a lot of people. It makes me feel bad to go to a meeting and see some unfortunate person’s soul so transfixed by the word sovereignty that they can’t think their way through the simplest problems.

Sam Deloria, Commentary on Nation-Building: The Future of Indian Nations, 34 Ariz. St. L.J. 55, 55 (2002).

[571] See Thomas Biolsi, Deadliest Enemies: Law and the Making of Race Relations on and off Rosebud Reservation 190 (2001).

[572] There are a number of scholarly approaches to federal Indian law, but not surprisingly, most of the approaches identified in a textbook epilogue (placing scholars into “Foundationalist,” “Critic,” “Pragmatist,” or “Tribal Realism” camps) rely heavily upon Supreme Court opinions as an analytical starting point. Robert T. Anderson et al., American Indian Law: Cases and Commentary 895–99 (2008). “Critic” Professor Robert B. Porter observes,

Even those who write from what you might call a “pro-Indian perspective” seem resigned to accept the reality that the United States really does have plenary power over the Indian nations, that there exists a federal trust responsibility for Indigenous peoples, and that the Indian nations really are “domestic dependent nations.”

Porter, supra note 567, at 97.

[573] Walker & Gover, supra note 233, at 262. The Walker and Gover article at times seems to accept federal primacy. See id. at 244 (“By assuming primary responsibility under the federal environmental laws whenever tribal amendments so allow, tribes can establish environmental quality standards suited to local and individual situations, rather than accept EPA’s generalized standards that may have little to do with local conditions.”). At other points the authors focus on cooperative agreements as a good approach. See id. at 250. However, overall the article supports unfettered tribal control. See id. at 244

[574] See, e.g., Collins & Hall, supra note 130, at 317 (“The question for Indian nations is first, who decides? Only after that query is answered in favor of Indian sovereignty can we turn our attention to the second question, what shall be done?”).

[575] Walker et al., supra note 205, at 390; see also Walker & Gover, supra note 233, at 231 (arguing that the fact that tribes reject most waste industry proposals is itself proof “that tribal governments are fully capable of evaluating waste proposals”). Such insistence in the ability of tribes to decide for themselves also might reflect frustration at non-Indian “ethnocentric if not racist” assumptions of tribal incompetence. Grijalva, supra note 15, at 155.

[576] Grijalva, supra note 15, at 155–56. Fear among environmentalists that tribal oversight would mean lesser environmental protection than under federal oversight mirrors assumptions made by policymakers that federal management of tribal resources is better than tribal control; yet, given the record of U.S. management, tribes probably “would do no worse” than the United States has historically. Peter C. Maxfield, Tribal Control of Indian Mineral Development, 62 Or. L. Rev. 49, 71–72 (1983). The Navajo uranium experience and even EPA’s seemingly political flip-flop on Desert Rock’s PSD permit attest to shortcomings in federal oversight. Although writing about jurisdiction over nonmembers, Professor Robert Clinton’s admonition that decolonization of Indian law involves getting rid of the “underlying . . . distrust of tribal governance” applies with regard to environmental regulation as well. Clinton, supra note 101, at 152.

[577] 21 U.S. (8 Wheat.) 543 (1823).

[578] Id. at 574. The doctrine of discovery “did not come from any principle of constitutional law . . . but rather from a doctrine of international law.” Pommersheim, Broken Landscape, supra note 481, at 261.

[579] Cherokee Nation v. Georgia, 30 U.S. (5 Pet.) 1, 17 (1831).

[580] See, e.g., Krakoff, supra note 124, at 1110.

[581] When he was Chief Justice of the Navajo Nation Supreme Court, Robert Yazzie observed that “[t]here are a lot of agonizing law review articles coming out these days about what a mess Indian law happens to be,” and continued by suggesting that state and federal judges do not read the articles. Robert Yazzie, “Watch Your Six”: An Indian Nation Judge’s View of 25 Years of Indian Law, Where We Are and Where We Are Going, 23 Am. Indian L. Rev. 497, 501 (1999).

[582] See, e.g., Steven Paul McSloy, Back to the Future: Native American Sovereignty in the 21st Century, 20 N.Y.U. Rev. L. & Soc. Change 217, 300–01 (1993).

[583] Frank B. Higgins, International Law Consideration of the American Indian Nations by the United States, 3 Ariz. L. Rev. 74, 84 (1961).

[584] For a lively scholarly exchange on this question, see Robert Laurence, Learning to Live with the Plenary Power of Congress over the Indian Nations: An Essay in Reaction to Professor Williams’ Algebra, 30 Ariz. L. Rev. 413 (1988); Robert A. Williams, Jr., Learning Not to Live with Eurocentric Myopia: A Reply to Professor Laurence’s Learning to Live with the Plenary Power of Congress over the Indian Nations, 30 Ariz. L. Rev. 439 (1988); Robert A. Williams, Jr., The Algebra of Federal Indian Law: The Hard Trail of Decolonizing and Americanizing the White Man’s Indian Jurisprudence, 1986 Wis. L. Rev. 219; see also Clinton, supra note 101, at 121 (“Any effort to decolonize federal Indian law, therefore, must begin with a rejection of the plenary power doctrine . . . .”).

[585] E.g., Barsh, supra note 237, at 86 (arguing for the reemergence of indigenous peoples “as subjects of international law”); McSloy, supra note 582, at 280 (arguing that the United States should “treat Native nations as nations”); Skibine, supra note 556, at 1109 (“International law should be applied to the relationship between the United States and the Indian tribes.”). The Executive Director of the Indian Law Resource Center, Robert “Tim” Coulter, explains the basis for thinking of Indians as nation-states: “Many Indian nations clearly have the required elements of nationhood. It has been noted that several Indian nations have more territory, larger populations and probably better governments than some of the nations now sitting in the United Nations.” Robert T. Coulter, Contemporary Indian Sovereignty, in Rethinking Indian Law 109, 117 (Comm. on Native Am. Struggles, Nat’l Lawyers Guild ed., 1982). Coulter continues, “Thus, viewing Indian sovereignty in terms of international law, contemporary writers have concluded, as John Marshall did in Cherokee Nation v. Georgia that at least some Indian nations are, or indeed have the right to be, nation-states within the meaning of international law.” Id. at 119.

[586] The “international” approach is controversial and is not universally accepted by Indian law scholars. Some believe it to be of little practical utility given the improbability that the U.S. government will abandon plenary power and afford tribes nation-state status. In a candid essay on Indian law, Professor Robert Laurence, for example, states, “I see little short-term help—that is to say within the next couple of generations or so—from international law.” Laurence, supra  note 192, at 4. These scholars view such work as unhelpful and fear that such internationally focused scholarship is dangerously utopian, in a way that might inspire a judicial or popular backlash against Indian sovereignty. See, e.g., Suagee, supra note 210, at 5 (“[A] gung-ho believer in tribal sovereignty can be just as dangerous as someone who just doesn’t understand the concept to begin with.”). But see S. James Anaya, Keynote Address: Indigenous Peoples and Their Mark on the International Legal System (Mar. 16, 2006), in 31 Am. Indian L. Rev. 257, 257 (2007) (“[W]e are in a time when international law speaks concretely to the issues of Native Americans in this country . . . and it does so not just from the standpoint of theory or proposal by a scholar writing some time ago. It not only speaks to these issues, but it also establishes certain standards of obligation for our government . . . .”).

[587] See, e.g., supra text accompanying notes 455–58 (discussing environmentalists’ opposition to Desert Rock as an attack on the Navajo Nation’s sovereignty).

[588] Some tribes are arguably enjoying an “Indian renaissance.” See Joseph Bruchac, Indian Renaissance, Nat’l Geographic, Sept. 2004, at 76, 90 (“[The] situation is changing as Indians across the U.S. exert new influence over their lives and their communities.”). And policy changes, such as those exemplified in President Richard Nixon’s 1970 Special Message to Congress, have played a role in tribal improvements. President’s Special Message to the Congress on Indian Affairs, 1970 Pub. Papers 564, 565 (July 8, 1970). These changes came as a result of struggle: BIA, for example, went from making “virtually all decisions for individual tribes,” to allowing for greater tribal autonomy as a response “to pressure from younger and more aggressive tribal leaders.” Cohen & Mause, supra note 78, at 1824. Robert Coulter’s description of the importance of struggle also explains the need for such struggle: “The present status of Indian nations is the result of the constant erosion of Indian governmental rights by the courts and by Congress and the steady, persistent efforts of Indian nations to strengthen and maintain their existence and governments.” Robert T. Coulter, Present and Future Status of American Indian Nations and Tribes, in Indian Self-Governance: Perspectives on the Political Status of Indian Nations in the United States of America 37, 42–43 (Carol J. Minugh et al. eds., 1989). For an enjoyable and eye-opening account of the struggles behind increased tribal independence and the people involved, see generally Charles F. Wilkinson, Blood Struggle: The Rise of Modern Indian Nations (2005). But while the “Indian renaissance” is promising, it is not shared by all tribes, nor, I believe, is it likely to be accompanied by dramatically better federal Indian policies.

[589] John Howard Clinebell & Jim Thomson, Sovereignty and Self Determination: The Rights of Native Americans Under International Law, 27 Buff. L. Rev. 669, 714 (1978).

[590] For example, Professor James Grijalva’s conclusion to his comprehensive study of environmental justice in Indian country, which primarily looked at EPA policy and federal Indian law, explains his book’s focus by noting, “We might hope the time comes when the preservation of American indigenous culture needs no federal agency, court or legislative body. Until that day, tribal primacy for federal environmental programs may well be the most effective means for addressing environmental injustice in Indian country.” Grijalva, supra note 15, at 200.

[591] The development and significance of international indigenous rights is best understood through the work of Professor S. James Anaya. E.g., S. James Anaya, Indigenous Peoples in International Law (2d ed. 2004) (the leading book in the field); S. James Anaya, International Human Rights and Indigenous Peoples: The Move Toward the Multicultural State, 21 Ariz. J. Int’l & Comp. L. 13 (2004) (discussing a number of important rights indigenous communities have under international law).

Many other scholars have at different points in their writing also highlighted the significance of international indigenous rights in how the rights of Indians are understood. See, e.g., G. William Rice, Teaching Decolonization: Reacquisition of Indian Lands Within and Without the Box—An Essay, 82 N.D. L. Rev. 811 (2006) (discussing tribal reacquisition of land under the United Nations Draft Declaration on the Rights of Indigenous Peoples); Rebecca  Tsosie, Indigenous People and Environmental Justice: The Impact of Climate Change, 78 U. Colo. L. Rev. 1625 (2007) (calling for indigenous rights to environmental self‑determination based on human rights norms); Pommersheim, Broken Landscape, supra note 481, at 259–93.

[592] Hopi Tribal Council Bans Environmental Groups, Navajo-Hopi Observer, Sept. 29, 2009, http://www.navajohopiobserver.com/main.asp?SectionID=1&subsectionID=1&articleID=11876 (last visited Apr. 18, 2010).

[593] Press Release, Office of the President & Vice President, Navajo Nation, supra note 456, at 1 (quoting Navajo President Shirley).

[594] Carol Berry, The Green Divide Meets Tribal Politics, Indian Country Today, Oct. 2, 2009, http://www.indiancountrytoday.com/national/63296187.html (last visited Apr. 18, 2010) (quoting Scott Canty, Hopi Tribal Counsel).

[595] Press Release, Office of the President & Vice President, Navajo Nation, supra note 456, at 2 (quoting Navajo Nation President Shirley).

[596] See, e.g., Felicia Fonseca, Hopi, Navajos Say Environmentalists Not Welcome, Reznet, Sept. 30, 2009, http://www.reznetnews.org/article/hopi-navajos-say-environmentalists-not-welcome-39650 (last visited Apr. 18, 2010); Mary Annette Pember, Leaders Disguise a Deep Tribal Dispute, Daily Yonder, Oct. 12, 2009, http://www.dailyyonder.com/leaders-disguise-deep-tribal-dispute/2009/10/12/2390 (last visited Apr 18, 2010); Jonathan Thompson, Op-Ed., Whose  Sovereignty Is It?, High Country News (Paonia, Colo.), Oct. 27, 2009, http://www.hcn.org/wotr/whose-sovereignty-is-it (last visited Apr. 18, 2010).

[597] Royster, supra note 377, at 340.

[598] Reflecting the field of Indian law’s stability, Professor Philip Frickey, perhaps the leading doctrinal scholar of federal Indian law, argues that “the field is structurally immunized against substandard doctrinal reevaluation.” Frickey, supra note 565, at 1778.

[599] Professor Grijalva notes that “environmentalists like most Americans know little of the nuances of federal Indian law and the doctrine of retained tribal sovereignty.” Grijalva, supra note 15, at 198. And Dean Suagee notes, “The Supreme Court doesn’t understand Federal Indian law, so why should we expect non-Indian environmental lawyers to do that?” Suagee, supra note 210, at 5. But I believe such understanding should be expected of environmentalists working on reservation issues.

[600] See supra notes 455–58 and accompanying text.

[601] Rice, supra note 591, at 814.

[602] Laurence, supra note 192, at 7 (differentiating Santa Clara Pueblo’s sovereignty from Bolivia’s).

[603] See S. James Anaya, Environmentalism, Human Rights and Indigenous Peoples: A Tale of Converging and Diverging Interests, 7 Buff. Envtl. L.J. 1, 2 (2000) (discussing the important role that international indigenous human rights issues have in the modern environmental movement).

[604] See, e.g., Fergus MacKay, Indigenous Peoples’ Right to Free, Prior and Informed Consent and the World Bank’s Extractive Industries Review, 4 Sustainable Dev. L. & Pol’y (Special Issue) 43, 43, 52 box 1 (2004) (discussing the acceptance of indigenous peoples’ rights to FPIC in the international community and listing international environmental organizations that have accepted indigenous peoples’ rights to FPIC).

[605] The author thanks Professor David Hunter for highlighting FPIC’s importance for understanding how environmental organizations relate to indigenous peoples internationally.

[606] Indigenous people and indigenous non-governmental organizations have gained some right to participate, but as Professor Jeff Corntassel cautions, “an illusion of inclusion” does not mean “indigenous voices are truly being heard.” Jeff Corntassel, Toward Sustainable
Self-Determination: Rethinking the Contemporary Indigenous-Rights Discourse
, 33 Alternatives 105, 111 (2008).

[607] See, e.g., James Gustave Speth, International Environmental Law: Can It Deal with the Big Issues?, 28 Vt. L. Rev. 779, 793 (2004) (arguing that international environmental law, as it stands today, is unable to effectively address global environmental issues).

[608] Alfred, supra note 268, at 44 (arguing that Indigenous leaders have the responsibility “to expose” this pretence).

[609] The ineffectiveness of international environmental law is closely linked to “the failure of green governance at the international level,” according to Yale School of Forestry and Environmental Studies’s Dean James Gustave Speth. Speth, supra note 607, at 793.

[610] Though President George W. Bush’s rejection of the Kyoto Protocol to the United Nations Framework Convention on Climate Change, Dec. 11, 1997, 37 I.L.M. 22, probably symbolizes U.S. resistance to global environmental limits, the son was merely continuing in his father’s footsteps. President George H.W. Bush was the “most visible opponent to a legally binding treaty” connected with the 1992 Earth Summit and actively “resisted calls for action” on numerous environmental treaties, ranging from global warming to forest protection. Miguel A. Santos, Limits and Scope of Environmental Law 306 (1995).

[611] Although written by my colleague in 1992, Professor David Hunter’s observations regarding the limits of international law largely remain true today: “[T]he international legal system, reflecting as it does an archaic acceptance of the nation-state as the root of all power, may be fundamentally incapable of meeting [the] challenges” of global environmental problems. David B. Hunter, Toward Global Citizenship in International Environmental Law, 28 Willamette L. Rev. 547, 548 (1992).

[612] Mahnoush H. Arsanjani, Environmental Rights and Indigenous Wrongs, 9 St. Thom. L. Rev. 85, 88 (1996).

[613] U.N. Conference on Env’t & Dev., Rio de Janeiro, June 3–14, 1992, Rio Declaration on Environment and Development, princ. 22, U.N. Doc. A/CONF.151/5/Rev.1 (June 14, 1992), reprinted in 31 I.L.M. 874, 880 (1992) [hereinafter Rio Declaration]; see also Arsanjani, supra note 612, at 90 (labeling Rio’s incorporation of indigenous peoples “sympathetic” but “rather superficial”).

[614] United Nations Declaration on the Rights of Indigenous Peoples, G.A. Res. 61/295, art. 29, ¶ 1, U.N. Doc. A/Res/61/295 (Sept. 13, 2007), available at http://www.un.org/esa/socdev/unpfii/ documents/DRIPS_en.pdf. The Declaration goes on to say that states shall not store or dispose of “hazardous materials” on the lands of indigenous peoples without their consent. Id. art. 1, ¶ 2.

[615] Carpenter et al., supra note 284, at 1036. As a nonbinding instrument, the Declaration does not impose legal obligations on signatories. Connie K. Chan, Response, Lisa J. Laplante & Suzanne E. Spears, Out of the Conflict Zone: The Case for Community Consent Processes in the Extractive Sector, 11 Yale Hum. Rts. & Dev. L.J. 117, 120 (2008).

[616] Textbook coverage of indigenous peoples in the IEL field arguably reflects their peripheral status. See, e.g., Patricia Birnie et al., International Law and the Environment (3d ed. 2009) (including discussion of indigenous peoples in four out of 810 pages); International Law and Sustainable Development: Principles and Practice (Nico Schrijver & Friedl Weiss eds., 2004) (containing four brief mentions and one page with discussion in 698 pages).

[617] S. James Anaya, Divergent Discourses About International Law, Indigenous Peoples, and Rights over Lands and Natural Resources: Toward a Realist Trend, 16 Colo. J. Int’l Envtl. L. & Pol’y 237, 240 (2005).

[618] Id. at 241.

[619] Id.

[620] For a brief history of the gains indigenous peoples have made in having their sovereignty recognized in different countries around the world and before international institutions, see U.N. Comm’n on Human Rights, Sub-Comm’n on the Promotion & Prot. of Human Rights, Indigenous Peoples’ Permanent Sovereignty over Natural Resources, ¶ 17–30, U.N. Doc. E/CN.4/Sub.2/2004/30 (July 13, 2004) (prepared by Erica-Irene A. Daes) [hereinafter U.N. Comm’n on Human Rights, Permanent Sovereignty].

[621] Anaya, supra note 617, at 241.

[622] Id. at 258.

[623] Id. at 257 (focusing on Indian advocates and control over reservation resources, not the role of environmental organizations).

[624] Hurst Hannum, Sovereignty and Its Relevance to Native Americans in the Twenty-First Century, 23 Am. Indian L. Rev. 487, 494 (1999) (“[E]ven if sovereignty might be meaningful for the Navajo, it is more difficult to comprehend the relevance of sovereignty to much smaller nations, some of which number only in the hundreds.”).

[625] Id. at 492.

[626] Frickey, supra note 313.

[627] See id. at 31 (“[T]ribal sovereignty is not ‘created by and springing from the Constitution,’ but rather is an inherent sovereignty that ‘existed prior to the Constitution’ and is, therefore, not subject to it.” (quoting Talton v. Mayes, 163 U.S. 376, 382, 384 (1896)) (footnotes omitted)).

[628] Id. at 79. International law, to the extent that “the evolving component of it concerning the rights of indigenous peoples” is incorporated, can include international human rights norms regarding indigenous peoples. Id. at 37.

[629] Id. at 78.

[630] Special Rapporteur on the Situation of Human Rights and Fundamental Freedoms of Indigenous Peoples, Professor S. James Anaya, makes a shortened version of Professor Frickey’s argument: “[C]ontemporary domestic law concerning Native Americans remains frozen in the international law of 200 years ago. . . . So, it makes perfect sense to look to contemporary international norms, to come up with interpretations of domestic federal law doctrine.” Anaya, supra note 586, at 271–72.

[631] Coulter, supra note 588, at 48.

[632] S. James Anaya & Robert A. Williams, Jr., The Protection of Indigenous Peoples’ Rights over Lands and Natural Resources Under the Inter-American Human Rights System, 14 Harv. Hum. Rts. J. 33 (2001).

[633] Anaya, supra note 591, at 97.

[634] G.A. Res. 61/295, supra note 614, art. 3.

[635] U.N. Dev. Group, Inter-Agency Support Group on Indigenous Issues, Guidelines on Indigenous Peoples’ Issues, at 4, U.N. Doc. HR/P/PT/16 (2009), available at http://www.un.org/ esa/socdev/unpfii/documents/UNDG_guidelines_EN.pdf.

[636] Id. at 15 (endnote omitted).

[637] See Hari M. Osofsky, The Inuit Petition as a Bridge? Beyond Dialectics of Climate Change and Indigenous Peoples’ Rights, 31 Am. Indian L. Rev. 675, 696 (2007) (“[I]ndividually-oriented human rights protections run into serious legitimacy issues in the context of indigenous peoples.”).

[638] See Morton v. Mancari, 417 U.S. 535, 554 (1974) (referring to the uniqueness of BIA’s relationship with Indians). A note of caution is in order. Late Professor Erik Bluemel observed of the sui generis category of indigenous claims or rights that while it “can be a very important, analytically distinct category,” the contents of the category is not yet “clearly defined.” Erik B. Bluemel, Separating Instrumental from Intrinsic Rights: Toward an Understanding of Indigenous Participation in International Rule-Making, 30 Am. Indian L. Rev. 55, 71 (2005). Professor Bluemel therefore chose to deemphasize the sui generis nature of some indigenous claims in his own analysis. Id. Others in contrast seem to fully support the idea of sui generis indigenous rights. See, e.g., Anaya, supra note 591, at 142; Tsosie, supra note 591, at 1653 (“[I]ndigenous peoples are distinctive and . . . their rights cannot be coextensive with those of any other group.”).

[639] Lillian Aponte Miranda, The Hybrid State-Corporate Enterprise and Violations on Indigenous Land Rights: Theorizing Corporate Responsibility and Accountability Under International Law, 11 Lewis & Clark L. Rev. 135, 141–44 (2007).

[640] Id. at 144; see also Fergus MacKay, Universal Rights or a Universe unto Itself? Indigenous Peoples’ Human Rights and the World Bank’s Draft Operational Policy 4.10 on Indigenous Peoples, 17 Am. U. Int’l L. Rev. 527, 604 (2002) (“[H]uman rights standards, as set out in treaties, in jurisprudence interpreting those treaties, and in emerging standards, all require that countries recognize and respect indigenous ownership rights, at a minimum, over lands traditionally occupied.”).

[641] Anne Perrault et al., Partnerships for Success in Protected Areas: The Public Interest and Local Community Rights to Prior Informed Consent (PIC), 19 Geo. Int’l Envtl. L. Rev. 475, 490 (2007). For more on the legal basis for indigenous peoples’ rights to land, natural resources, and development, see Anaya, supra note 591, at 141–50.

[642] Questions such as whether Indian advocates arguing before the United States should base their arguments in part on international norms, such as the U.N. Declaration on the Rights of Indigenous Peoples, are divisive. Some believe that, like international human rights, international indigenous rights offers a way to escape the ethnocentrism and limits of federal Indian law; others believe that because the United States is unlikely to respond favorably to international developments, indigenous peoples advocacy is ineffective or, worse, counterproductive. See, e.g., Kristen A. Carpenter, Interpreting Indian Country in State of Alaska v. Native Village of Venetie, 35 Tulsa L.J. 73, 123–25 (1999) (discussing the potential of using international law norms to secure indigenous rights); Pamela Stephens, Applying Human Rights Norms to Climate Change: The Elusive Remedy, 21 Colo. J. Int’l Envtl. L. & Pol’y 49, 80–81 (2010) (describing potential difficulties in using international law in a federal law setting).

[643] See supra note 586 and accompanying text.

[644] Proposing a new direction in U.S.-Indian relations is beyond the scope of this Article. Given the respect I have for scholars and the scholarship of those who would like to undo existing federal Indian law, it was a compliment to be accused by one reader of seeming “to have joined the dark (really, other) side” by urging use of international human rights. But rather than being a broad assertion of the need for the United States to incorporate international human rights into its relationship with Indian nations, the focus here is purposefully limited to how environmental organizations relate to Indian nations and, therefore, the accusation or compliment is unearned. To put it another way, the Article does not pick a side, except when it comes to environmental organizations.

[645] See, e.g., Wiggins, supra note 186, at 350–51 (detailing environmentalist support for the Yanomami in Brazil).

[646] See supra Part IV.A.

[647] Although FPIC arguably applies to all communities impacted by development proposals, support for FPIC’s requirements is strongest with indigenous peoples because of their uniquely recognized rights. Lisa J. LaPlante & Suzanne A. Spears, Out of the Conflict Zone: The Case for Community Consent Processes in the Extractive Sector, 11 Yale Hum. Rts. & Dev. L.J. 69, 93 (2008) (“The Declaration on the Rights of Indigenous Peoples . . . constitutes recognition of indigenous peoples’ right to FPIC by most members of the international community.”); Perrault et al., supra note 641, at 478 (noting indigenous people’s longstanding relationship with the land). The article refers to prior informed consent (PIC), but as explained later in the article, PIC and FPIC are equivalent. Id. at 521–22.

[648] Brant McGee, The Community Referendum: Participatory Democracy and the Right to Free, Prior and Informed Consent to Development, 27 Berkeley J. Int’l L. 570, 576 (2009). For more on the origins and legal basis for FPIC, see id. at 576–93.

[649] U.N. Dep’t of Econ. & Soc. Affairs, Div. for Soc. Policy & Dev., Contribution of the Indian Law Res. Ctr., Workshop on Free, Prior and Informed Consent, Jan. 17–19, 2005, Indigenous Peoples’ Right of Free Prior and Informed Consent with Respect to Indigenous Lands, Territories and Resources, at 2, U.N. Doc. PFII/2004/WS.2/6; see also International Conference on Engaging Communities, Brisbane, Austl., Aug. 15, 2005, Engaging Indigenous Peoples in Governance Processes: International Legal and Policy Frameworks for Engagement 10–12 (breaking FPIC into a description of its elements).

[650] McGee, supra note 648, at 578.

[651] Laplante & Spears, supra note 647, at 87. The contrast should not be overstated: Weak versions of what consent requires—“consent may be given through good-faith consultation and participation”—share in consultation’s indeterminacy. Donald M. Goldberg & Tracy Badua, Do People Have Standing? Indigenous Peoples, Global Warming, and Human Rights, 11 Barry L. Rev. 59, 70 (2008).

[652] McGee, supra note 648, at 571 (explaining the Environmental Law Institute’s definition of FPIC); see also Perrault et al., supra note 641, at 477 (“[C]ommunities have the right to give or withhold consent at decision-making points during the project cycle.”).

[653] McGee, supra note 648, at 635.

[654] Id. at 603–26 (providing examples of the history of select referenda on specific projects internationally); see also Bluemel, supra note 638, at 93–95 (discussing the significance of the undemocratic, unrepresentative aspect of some indigenous groups’ leadership). But see Perrault et al., supra note 641, at 512 (noting that design and process problems can make referenda “vulnerable to manipulation”).

[655] Laplante & Spears, supra note 647, at 96.

[656] See supra Part II.C.

[657] Perrault et al., supra note 641, at 522.

[658] Alex Page, Indigenous Peoples’ Free Prior and Informed Consent in the Inter-American Human Rights System, 4 Sustainable Dev. L. & Pol’y 16, 19 (2004).

[659] Perrault et al., supra note 641, at 524.

[660] See id. at 522 (“Consent does not necessarily mean that every member of affected people(s)/communities must agree . . . .”).

[661] Fergus MacKay, Coordinator of the Legal and Human Rights Programme at Forest Peoples Programme, observes, “Indigenous peoples’ right to [FPIC] is gaining increasing currency in international law, particularly in the jurisprudence of international human rights bodies.” MacKay, supra note 604, at 43. MacKay goes on to describe the World Bank Group as a “notable exception” to the increasing international acceptance of FPIC. Id. But while the Bank favors “consultation,” not “consent,” even this is somewhat tempered by the Bank’s legal department interpretation of “meaningful consultation” as necessarily including the right for consulted communities to say “no” in a way that approaches consent. Robert Goodland, Free, Prior and Informed Consent and the World Bank Group, 4 Sustainable Dev. L. & Pol’y 66, 66 (2004).

[662] Anaya, supra note 603, at 13; see also Pommersheim, Broken Landscape, supra note 481, at 279 (describing indigenous consultation rights as a “shadow or penumbral” right relative to the right of self-determination).

[663] U.N. Comm’n on Human Rights, Permanent Sovereignty, supra note 620, ¶ 47.

[664] Id. ¶ 48 (emphasis added). Daes goes on to link indigenous peoples’ natural resource rights with rights to self-determination, culture, “and the enjoyment of other human rights” that cannot be realized in situations of extreme poverty. Id. ¶ 58.

[665] Perrault et al., supra note 641, at 490.

[666] U.N. Comm’n on Human Rights, Permanent Sovereignty, supra note 620, ¶¶ 48, 58.

[667] Perrault et al., supra note 641, at 493–94.

[668] See G.A. Res. 61/295, supra note 614, arts. 3, 8, 10, 11; Robert T. Coulter, The U.N. Declaration on the Rights of Indigenous Peoples: A Historic Change in International Law, 45 Idaho L. Rev. 539, 543–45 (2009) (describing the efforts by indigenous peoples and their advocates leading to the Declaration).

[669] A brief history for those not in the Indian law field: The treaty-making period was characterized by Indian participation (albeit under strain and with some duplicity by the other negotiating party), and even centuries later rights originating out of the period are recognized. Allotment, with insignificant Indian participation and implementation imposed, had disastrous results; so too with termination. The Indian Reorganization Act—as well as the later Alaska Native Claims Settlement Act, 43 U.S.C. §§ 1601–1629h (2006)—provided tribes a choice (singular) but not the opportunity to define their own choice set, and results were mixed. The self-determination period has in contrast recognized the right of Indian nations to a far greater spectrum of choice across more areas of governance, and the policy has had better results.

[670] See Coulter, supra note 668, at 543–45.

[671] Although “skeptics argue that international human rights law is virtually irrelevant in the United States,” Professor Tsosie’s response echoes the argument of this Part: “It is worth contemplating the possibility of constructing a more just system of domestic law by investigating principles that are emerging through international consensus.” Tsosie, supra note 591, at 1652.

[672] 436 U.S. 49 (1978).

[673] See id. at 51–52 (holding that the Act cannot be read to allow gender discrimination actions against a tribe or its officers).

[674] Id. at 51.

[675] Id. For an excellent summary of the case with citations to the extensive scholarly debate related to the case, see Angela R. Riley, (Tribal) Sovereignty and Illiberalism, 95 Cal. L. Rev. 799, 810–23 (2007); see also Greg Rubio, Reclaiming Indian Civil Rights: The Application of International Human Rights Law to Tribal Disenrollment Actions, 11 Or. Rev. Int’l L. 1 (2009) (focusing on tribe violations of tribal members’ international human rights, focusing on the controversial disenrollment of Cherokee Freedmen).

[676] See supra Part V.A.1.

[677] See Robert J. McCarthy, Civil Rights in Tribal Courts: The Indian Bill of Rights at Thirty Years, 34 Idaho L. Rev. 465, 478–83 (1998) (discussing tribal sovereign immunity).

[678] Notably, four of the five chapters near the proposed site passed symbolic resolutions opposing Desert Rock. Tony Barboza, Pollution for Jobs: A Fair Trade?, High Country News (Paonia, Colo.), Sept. 5, 2005, at 4, 4.

[679] See Perrault et al., supra note 641, at 522 (explaining that the information must be both “accessible and understandable”).

[680] See id. (“[P]otentially affected people(s)/communities must be fully informed of their own rights and understand the legal processes guiding implementation of the project.”).

[681] Reflecting the, at times, one-sided nature of pro-Indian advocacy, Jana L. Walker and Kevin Gover complained that the Campo Band “confronted the bitter reality that Indian people suffer in political fora which often are unresponsive to Indian interests,” but did not seem aware of the irony, considering that non-Indians cannot participate in the election of tribal leaders, of highlighting the Campo Band’s “extraordinary meansures to address the concerns of the local non-indian population.” Walker & Gover, supra note 233, at 259. By noting the irony I am in no way suggesting that non-Indians should have the right to vote in tribal elections, but this is another example of how established tribal rights may conflict with a human rights approach.

[682] See Coulter, supra note 668, at 543–45 (recounting the origin of the Declaration that began in 1976 and included hundreds of tribal representatives).

[683] See, e.g., Christopher P. Cline, Note, Pursuing Native American Rights in International Law Venues: A Jus Cogens Strategy After Lyng v. Northwest Indian Cemetery Protective Association, 42 Hastings L.J. 591, 594 (1991) (describing the efforts of tribes to have the Office of American States recognize a U.S. violation of the tribes’ human rights).

[684] Tsosie, supra note 591, at 1666–67.

[685] Press Release, Office of Navajo Nation Human Rights Comm’n, NNHRC Addresses Members of the Expert Mechanism on the Implementation of the Declaration on the Rights of Indigenous Peoples (Aug. 11, 2009), available at http://www.nnhrc.navajo.org/press
releases/2009/aug09/Geneva%20PR.pdf.

[686] Id.

[687] See, e.g., id. (noting that Navajo Nation Human Rights Commission Chairperson Duane Yazzie’s remarks focused on conditions the U.S. attaches to the right to self-determination).

[688] Angela R. Riley, Good (Native) Governance, 107 Colum. L. Rev. 1049, 1123 (2007) (citations omitted).

[689] See id. at 1052–53 (discussing international debate over the requirements of good governance).

[690] Id. at 1054–55 (arguing that native governance involves using “indigenous principles of government” rather than requiring that “Indian nations either fully depart from or emulate the developed West”).

[691] Id. at 1107.

[692] See The Harvard Project on Am. Indian Econ. Dev., Overview of the Harvard Project, http://www.ksg.harvard.edu/hpaied/overview.htm (last visited Apr. 18, 2010). Many of the Project’s publications can also be found on its website.

[693] Duane Champagne, Challenges to Native Nation Building in the 21st Century, 34 Ariz. St. L.J. 47, 51 (2002) (describing making tribal governments effective as “[o]ne of the challenges of the twenty-first century”).

[694] Suagee, supra note 496, at 161 (“[I]f tribes do not want states asserting that they have jurisdiction for environmental regulation in Indian country, tribes need to have effective programs in place.”).

[695] See Tribal Court Clearinghouse, Tribal Laws/Codes, http://www.tribal-institute.org/ lists/codes.htm (last visited Apr. 18, 2010) (listing various tribal codes).

[696] Arguably, Indian tribes have a greater entitlement to pollute than other parts of the United States. Principle 7 of the Rio Declaration on Environment and Development states,

In view of the different contributions to global environmental degradation, States have common but differentiated responsibilities. The developed countries acknowledge the responsibility that they bear in the international pursuit of sustainable development in view of the pressures their societies place on the global environment and of the technologies and financial resources they command.

Rio Declaration, supra note 613, princ. 7. The common-but-differentiated-responsibility principle is not fully accepted by the U.S. government, perhaps primarily because it could impose a heavy cost on the world’s foremost polluter. See generally Tuula Honkonen, The Common but Differentiated Responsibility Principle in Multilateral Environmental Agreements 253–58, 298 (2009) (discussing the reluctance to fully adopt the common-but-differentiated-responsibility principle in developed countries and focusing on the United States’s criticism of the Kyoto Protocol). But the principle does suggest that the focus should be on off‑reservation projects and that the Navajo Nation—with a per capita income well below the World Bank’s line between developing and developed economies—has more right to develop a coal-fired power plant than do other parts of the United States. Yet, while Navajo Nation’s Desert Rock proposal was blocked, 36 coal-fired power plants are progressing towards completion in the United States as of June 2009. Powerpoint: Erik Shuster, Office of Sys. Analyses & Planning, Nat’l Energy Tech. Lab., Tracking New Coal-Fired Power Plants 6 tbl.1 (Oct. 8, 2009), available at http://www.netl.doe.gov/coal/refshelf/ncp.pdf. In the second quarter of 2009 alone, four plants became operational, and there are an additional 47 plants announced or in early stages of development. Id.

In light of the common-but-differentiated-responsibility principle, the Navajo Nation’s right to development arguably deserves allowances not shared by the rest of the United States, at least until the income gap closes. Furthermore, an argument can be made that U.S. environmental organizations should get U.S. emissions in order before using a federally defined process of environmental oversight to block the Navajo Nation. The Navajo Nation’s per capita income in 2004—the most recent available year—was $7734 annually. Choudhary, supra note 352, at T 49 tbl.21. Developed countries, according to the World Bank, have per capita incomes above $11,906 per year. See World Bank, World Bank List of Economies (2009), available at http://siteresources.worldbank.org/DATASTATISTICS/Resources/CLASS.XLS (defining developed as “high income”); The World Bank, Data—Country Statistics, http://web.worldbank.org/WBSITE/ EXTERNAL/DATASTATISTICS/0,,contentMDK:20420458~menuPK:64133156~pagePK:64133150~piPK:64133175~theSitePK:239419,00.html (last visited Apr. 18, 2010).  The U.S. per capita income, in contrast, was $26,804 in 2007. Carmen DeNavas-Walt et al., U.S. Census Bureau, Income, Poverty, and Health Insurance Coverage in the United States: 2007, at 8 tbl.1 (2008), available at http://www.census.gov/prod/2008pubs/p60-235.pdf.

[697] The author thanks Professor Patrick Simms for his insight into how the precedent-setting aspects of federal approval can make environmental organizations put aside their hesitation about interfering with tribal sovereignty.

[698] Royster, supra note 96, at 1092. Tribal values would only be prioritized up to a point, because under the statute the Secretary of the Interior retains a right to review tribal environmental determinations. Id. at 1095–97. For this reason, the Navajo Nation objected to ITEDSDA as being a reduction of the U.S. trust responsibility without truly turning over authority to Indian nations. Id. at 1098–99.

[699] See generally Judith V. Royster, Mineral Development in Indian Country: The Evolution of Tribal Control over Mineral Resources, 29 Tulsa L.J. 541, 613 (1994) (highlighting that the federal government has decided to let “the appropriate federal agency” regulate until the tribes are prepared to administer the “federal [environmental] standards and programs”).

[700] Maxfield, supra note 576, at 72. In his characteristically strong way of phrasing things, Ward Churchill, responding to the fear of “restoration of native land rights precipitating some sort of ‘environmental holocaust,’” points to accounts by “early European invaders” of North America’s “pristine wilderness” and writes, “[C]ontrast that reality to what’s been done to this continent over the past couple of hundred years . . . and you tell me about environmental devastation.” Ward Churchill, Struggle for the Land: Indigenous Resistance to Genocide, Ecocide and Expropriation in Contemporary North America 420 (1993). As a U.N. report on climate change’s effect on indigenous peoples notes, “[T]he United States, with a population of 300 million, makes up only 4 [percent] of the total world population, but accounts for about 25 [percent] of world [greenhouse gas] emissions.” U.N. Econ. & Soc. Council, Permanent Forum on Indigenous Issues, Impact of Climate Change Mitigation Measures on Indigenous Peoples and on Their Territories and Lands, ¶ 17, U.N. Doc. E/C.19/2008/10 (Mar. 20, 2008) (prepared by Victoria Tauli-Corpuz & Aqqaluk Lynge), available at http://daccess-dds-ny.un.org/doc/UNDOC/ GEN/N08/277/65/PDF/N0827765.pdf?OpenElement.

[701] Clinton, supra note 101, at 152 (focusing in on the distrust evident in cases involving jurisdiction over non-Indians). Distrust extends beyond Indian environmental programs; the preference of national environmental organizations for national environmental protection is reflected in an “impassioned rhetoric of distrust toward local self-determination,” whether exercised by western states or Indian tribes. Daniel Kemmis, This Sovereign Land: A New Vision for Governing the West 158 (2001).

[702] Fixico, supra note 142, at 181.

[703] See, e.g., Ezra Rosser, The Nature of Representation: The Cherokee Right to a Congressional Delegate, 15 B.U. Pub. Int. L.J. 91, 99–117 (2005) (exploring the nature of the leadership dispute between John Ross and John Ridge in the context of the Treaty of New Echota and the way the United States used the lack of a unified front).

[704] Krech, supra note 185, at 227.

[705] See, e.g., Tsosie, supra note 591, at 1669 (“[I]ndigenous peoples hold particularly relevant knowledge as to how to achieve [sustainability] due to their familiarity with certain environments . . . .”).

[706] For more on alternative energy development in Indian Country focusing on wind, see Patrick M. Garry et al., Wind Energy in Indian Country: A Study of the Challenges and Opportunities Facing South Dakota Tribes, 54 S.D. L. Rev. 448 (2009); Kathleen R. Unger, Change Is in the Wind: Self-Determination and Wind Power Through Tribal Energy Resource Agreements, 43 Loy. L. A.L. Rev. 311 (2009);  Victoria Sutton, Wind and Wisdom, 1 Envtl. & Energy L. & Pol’y J. 345 (2007); Bob Gough, Panel V: Revitalizing Economies, Preserving Cultures & Protecting the Environment: Striking the Balance in South Dakota and Indian Country, 7 Great Plains Nat. Resources J. 67 (2002).

[707] Jonathan M. Hanna, Natural Res. Law Ctr., Univ. of Colo. Law Sch., Native Communities and Climate Change: Legal and Policy Approaches for Protecting Tribal Legal Rights 31 (2007), available at http://www.colorado.edu/Law/centers/nrlc/ publications/ClimateChangeReport-FINAL%20_9.16.07_.pdf.

[708] Id.

[709] See id. at 5, 8, 23–24.

[710] Id. at 31.

[711] U.N. Permanent Forum on Indigenous Issues, Climate Change and Indigenous Peoples, http://www.un.org/esa/socdev/unpfii/en/climate_change.html (last visited Apr. 18, 2010).

[712] Conference on Indigenous Peoples and Climate Change, Copenhagen, Den., Feb. 21–22, 2008, Meeting Report, at 3, U.N. Doc. E/C.19/2008/CRP.3 (Mar. 10, 2008), available at http://www.un.org/esa/socdev/unpfii/documents/E_C_19_2008_CRP3_en.pdf.

[713] U.N. Permanent Forum on Indigenous Issues, supra note 711.

[714] See Hanna, supra note 707, at 22.

[715] As Dean Speth writes, “If there is one country that bears most responsibility for the lack of progress on international environmental issues, it is the United States.” Speth, supra note 607, at 790.

[716] Krech, supra note 185, at 216; see also Deloria, supra note 1, at 205–06 (“But many scholars—who note the romantic view of Indians in earlier stages of Euro-American history—have themselves been blinded by the same romantic tradition today and deny us our political life and our humanity. . . . We [Indians] have made mistakes, and you [Indian scholars] do us a disservice by almost uniformly shifting the blame elsewhere.”).

[717] Posting of Mark Walker to Am. Coll. of Envtl. Lawyers, Global Warming Litigation Heating Up—Village of Kivalina Lawsuit, http://www.acoel.org/2008/08/articles/natural-resource-damages/global-warming-litigation-heating-up-village-of-kivalina-lawsuit (Aug. 21, 2008) (last visited Apr. 18, 2010) (quoting Complaint at 2, Native Village of Kivalina, Alaska v. ExxonMobile, 663 F. Supp. 2d 863 (N.D. Cal. 2009) (No. C 08-1138 SBA)); see also Osofsky, supra note 637 (discussing the significance of a climate change–based Inuit petition to the Inter‑American Commission on Human Rights); John H. Knox, Climate Change and Human Rights Law, 50 Va. J. Int’l L. 163, 191–92 (2009) (summarizing the same petition); Tsosie, supra note 591, at 1669–74 (summarizing the same petition).

[718] Complaint at 46, Native Village of Kivalina, Alaska v. ExxonMobile, 663 F. Supp. 2d 863 (N.D. Cal. 2009) (No. C 08-1138 SBA). For a brief summary of the case and motivation to sue, see Felicity Barringer, Flooded Village Files Suit, Citing Corporate Link to Climate Change, N.Y. Times, Feb. 27, 2008, at A16.

[719] EPA Hearing III, supra note 442, at 57 (statement of Orion Yazzie, resident of Aztec, N.M.).

[720] In general, Professor Tsosie notes that “tribal decisions on mining policy are not clearly ‘right’ or ‘wrong.’” Tsosie, supra note 71, at 302.

[721] See Sherry, supra note 124, at 11 (calling attention to the “striking disregard for adverse environmental and social costs on local communities” caused by the Navajo Nation’s seizing upon “any economic opportunities” to “support a large bureaucracy and a population that depends on it for jobs”).

Climate Change Adaptation and the Structural Transformation of Environmental Law

By J.B. Ruhl*

The path of environmental law has come to a cliff called climate change, and there is no turning around. As climate change policy dialogue emerged in the 1990s, however, the perceived urgency of attention to mitigation strategies designed to regulate sources of greenhouse gas emissions quickly snuffed out meaningful progress on the formulation of adaptation strategies designed to respond to the effects of climate change on humans and the environment. Only recently has this “adaptation deficit” become a concern now actively included in climate change policy debate. Previously treating talk of adaptation as taboo, the climate change policy world has begrudgingly accepted it into the fold as the reality of failed efforts to achieve global mitigation policy has combined with the scientific evidence that committed warming will continue the trend of climate change well into the future regardless of mitigation policy success.

But do not expect adaptation policy to play out for environmental law the way mitigation policy has and is likely to continue. Mitigation policy has been framed as an initiative primarily within the domain of environmental law—a form of pollution control on steroids—and thus it will be environmental law that makes the first move and other policy realms that apply support or pushback. By contrast, environmental law does not “own” adaptation policy; rather, numerous policy fronts will compete simultaneously for primacy and priority as people demand protection from harms and enjoyment of benefits that play out as climate change moves relentlessly forward. This makes it all the more pressing for environmental law, early in the nation’s formulation of adaptation policy, to find its voice and establish its place in the effort to close the adaptation deficit.

Toward that purpose, this Article examines the context and policy dynamics of climate change adaptation and identifies ten trends that will have profound normative and structural impacts on how environmental law fits in: 1) shift in emphasis from preservationism to transitionalism in natural resources conservation policy, 2) rapid evolution of property rights and liability rules associated with natural capital adaptation resources, 3) accelerated merger of water law, land‑use law, and environmental law, 4) incorporation of a human rights dimension in climate change adaptation policy, 5) catastrophe and crisis avoidance and response as an overarching adaptation policy priority, 6) frequent reconfigurations of transpolicy linkages and trade‑offs at all scales and across scales, 7) shift from “front end” decision methods relying on robust predictive capacity to “back end” decision methods relying on active adaptive management, 8) greater variety and flexibility in regulatory instruments, 9) increased reliance on multiscalar governance networks, and 10) conciliation.

 I. Introduction

The path of environmental law has come to a cliff called climate change, and there is no turning around. Someday, maybe soon, the federal government will take the big leap and enact new legislation designed to curb our nation’s greenhouse gas emissions. Whether it is through a carbon tax, a cap-and-trade program, or some new regulatory innovation, the measure will be hailed by many and derided by many others. The supporters will throw a big party, and the opponents will hold a wake. When the hangovers wear off the next day, however, one thing will still be soberingly true no matter how aggressive the newly-minted legislation: Humans and our fellow species are looking into a future of climate change that will last a century or more, and we’ve done very little in the United States to prepare ourselves for it.

Indeed, the policy world’s fixation on achieving, or blocking, federal greenhouse gas emission legislation as part of our national strategy for climate change mitigation[1] has contributed to our neglect of national policy for climate change adaptation.[2] This wrong turn happened early in the development of domestic climate change policy. As Professor Dan Tarlock observed in 1992, at the time there was “a growing split between environmentalists who advocate mitigation, and ‘rational’ resource policy analysts who have strongly endorsed adaptation.”[3] Adaptation was winning the day, on the premise that “we should adopt the easy, low cost mitigation strategies to reduce energy use and then concentrate on selecting the most efficient adaptation strategies.”[4] Tarlock insightfully suggested three reasons for exercising caution in pursuing that approach:

First, adaptation is based on the ideology of scientific progress, a faith that is open to question. The principle message of environmentalism is that the tenets of Enlightenment thinking must be re-evaluated since science and technology may not always prevent serious harm or make things better. Second, the degree of friction in the proposed institutional responses is often underestimated so institutions may not perform as expected. Adaptation clearly exposes winners and losers in a reallocation. It is not reasonable to expect losers to accept all losses. More generally, institutional inflexibility is increasingly being adopted as a means to protect legitimate interests excluded from dominant resource allocation regimes. . . . Third, many institutions have no fair and adequate mechanism to deal with global warming. In these cases, adaptation is the adoption of a no action strategy, which may often be the most costly one.[5]

As news about climate change grew steadily worse in the years after Tarlock’s assessment,[6] the domestic policy pendulum quickly swung sharply in mitigation’s direction. Indeed, the challenge of climate change was portrayed as so exceptional, and the need for a new mitigation policy of sweeping dimensions thus so pressing, that talk of adaptation became taboo for fear it might knock the mitigation train off its tracks and lead to complacency.[7] In their impressive book on the topic, The Earthscan Reader on Adaptation to Climate Change,[8] E. Lisa F. Schipper and Ian Burton sum  up the tension that existed through the 1990s and well into the following decade:

[I]nterest in adaptation was overwhelmed by concern about the need to reduce greenhouse gas emissions and stabilize atmospheric greenhouse gas concentrations. Proponents of adaptation faced two obstacles that were attributed to adaptation: reducing the apparent need for mitigation; and playing down the urgency for action. For one, ‘adaptationists’ were distrusted because their proposals seemed to undermine the need for mitigation. Critics felt that belief in the potential value of adaptation would soften the resolve of governments to grasp the nettle of mitigation and thus play into the hands of the fossil fuels interests and the climate change [skeptics]. In addition, because climate change was popularly perceived as a gradual process, adaptation was not considered urgent as there would be time to adapt when climate change and its impacts became manifest. These views dominated in the mid and late 1990s.[9]

The problem is that mitigation policy soon ran into the same three problems Tarlock suggested would plague adaptation policy: Institutions lack the political will to impose tough lifestyle sacrifices on people in general; those who expect to be losers, were a mitigation regime to gear up, have squawked loudly in objection to the anticipated regulatory measures; and no fair and adequate mechanism has been devised to deal with the distributional effects of a comprehensive regulatory regime even if the political will were there to put one in place.[10] So, as with adaptation, mitigation is often portrayed as a scientific and technological challenge that eases us out of the climate change problem without sacrifices or losers—pump greenhouse gases into the ground; invent a cheap solar panel; launch mirrors into space; seed the oceans with iron.[11]

Today it is abundantly clear that these drags on the formulation of our domestic climate change policy are persistent and debilitating. A comprehensive national strategy that successfully reduces greenhouse gas emissions to levels thought to be adequate to arrest climate change, a feat which the United States obviously could not accomplish alone even if it were known what those levels should be, quite clearly is not around the political corner.[12] And it is just as clear that the miracle technological breakthrough is not past the research stage. Add to that the unavoidable reality of so-called committed warming—the climate change already built into the climate system as a result of past greenhouse gas emissions—which will play out for many decades even if one of these breakthroughs happened yesterday,[13] and the cold war between mitigation and adaptation is finally thawing. Climate change is already happening, and more is yet to come no matter what, thus a consensus is building that mitigation needs adaptation, and vice versa, even if they fundamentally are different and sometimes competing policy thrusts.[14]

It is not, in other words, an either-or choice between mitigation and adaptation.[15] The time when such a choice could have been made—when starting to install a meaningful mitigation regime could have obviated the need to ever have to think about adaptation—is long since past by many decades. There is no choice any longer: “Mitigation and adaptation are both essential parts of a comprehensive climate change response strategy.”[16] There certainly is room for argument over the relative mix of the two strategies and how much to spend respectively on them, questions I do not address here.[17] But almost all recent legal scholarship and policy dialogue now recognizes that formulating and implementing adaptation strategies must in any case be a significant component of our domestic climate change law and policy.[18]

The period during which adaptation policy was in the doghouse, however, stunted progress on forging its theory, design, and implementation. The accruing “adaptation deficit”[19] has grown large, putting us far behind the European Union, Australia, and many other nations in this respect.[20] In short, “the United States . . . lacks sufficient investment in the sciences required for moving beyond climate science to define impacts and vulnerabilities.”[21] Domestic law and policy are in no better shape. To be sure, legal scholarship on climate change policy is sharply on the rise.[22] Most of it, however, focuses on the configuration of instruments and institutions to accomplish mitigation, as in the debates over the efficacy of carbon taxes versus
cap-and-trade[23] and the advantages of federal top-down versus local bottom-up initiatives.[24] Although discussion of climate change adaptation, especially more recently, is often included in those scholarly contributions,[25] it is seldom included as a significant focus and almost never with concrete domestic policy proposals offered.[26] Indeed, the vast majority of legal scholarship touching on climate change adaptation explores not domestic preparedness, but rather the scope of responsibility developed nations have to assist the adaptation efforts of the least developed nations most vulnerable to the effects of climate change.[27] The latter is an important policy concern, but the former deserves urgent and focused attention as well.

Likewise, the actual on-the-ground law of climate change, albeit still limited in scope, is overwhelmingly about mitigation.[28] Most of the litigation aimed at shaping climate change policy is about either forcing the government to regulate or prohibit new sources of greenhouse gas emissions or stopping the government from doing so.[29] Likewise, virtually all federal, state, and local climate change law on the books or proposed for adoption addresses mitigation.[30] Only a few adaptation planning efforts, and even fewer concrete policies, have been adopted, so far mostly (as with mitigation policies) by state and local governments.[31] Overall, very little litigation, legislation, policy, or regulation in the United States has to do with how to manage the effects of climate change on people or the environment.

This Article is intended to further catalyze and, I hope, help organize a dialogue in legal scholarship and among policy makers with the principal focus of developing the environmental law and policy dimension of climate change adaptation. It adopts several premises about which little further discussion is provided: 1) work on mitigation law and policy will continue globally at multiple governance scales for several decades before significant legal regimes are in place; and 2) regardless of how aggressively that work progresses, climate warming committed to date will be exacerbated by additional net increases in greenhouse gas emissions for the foreseeable future until the mitigation measures take hold; meaning that 3) there will necessarily be an extended period of measurably significant climate change; but 4) at some point, probably many decades into the future, the mitigation measures will gain traction on greenhouse gas emissions and will arrest further climate change to lead us into a new stabilized climate regime.

The first three premises, already mentioned above, seem so beyond serious contestation that only a Pollyanna would argue to the contrary, and thus point inexorably to the need to define an adaptation component of climate change law. The fourth premise—that there is actually an “end” to climate change if we start working hard and soon on a mitigation strategy—is the hopeful one about which we cannot be certain. It raises the normative question that adaptation policy ultimately must answer: when we get to the “other side” of climate change, what do we hope to have accomplished with adaptation law and policy? We have no analog for what the world will look like then.[32] Unlike mitigation policy, for which the goal is clear, adaptation policy thus has no well-defined target.[33] My final premise, therefore, is that the adaptation component of climate change law has two overarching dynamic goals. First, it is to effectively and equitably manage the harms and benefits of climate change while mitigation policy does its work.[34] Second, it is to supply interim strategies to put us in a position to resume long-term planning for sustainable development when climate change is “over.”[35] Adaptation law, in other words, is about building a bridge to get us across the chasm of climate change intact.

To be sure, adopting both of those goals will trigger intense normative debates about what are “harms” and “benefits” of climate change, how do we “manage” them, and what set of conditions will position us to resume “sustainable development.” I do not attempt to resolve those questions here. Rather, this Article is intended to describe the policy space within which those questions will be debated in the field of environmental law. Climate change will impose unyielding physical, biological, and social constraints on what is possible to achieve through environmental law, but it will also exert tremendous structural pressures on the very design and implementation of the law itself. Environmental law, in other words, will undergo its own structural transformation regardless of the normative adaptation goals we set for it, which in turn will limit the normative goals we can hope to achieve with it. This Article, therefore, is aimed primarily at describing how environmental law is likely structurally to be shaped, constrained, and even liberated by the realities and demands of climate change adaptation, so that we can better understand how to apply it and what to expect to accomplish with it.

Part II briefly describes the context within which climate change adaptation and adaptation law will evolve. It starts with a survey and synthesis of some of the prevailing theories of climate change adaptation, then outlines the features of climate change adaptation in its three modes: 1) resisting the effects of climate change to maintain the status quo in situ; 2) transforming in situ to new physical, economic, and social arrangements to adapt to climate change; and 3) moving in search of better conditions for adaptation. Climate change impacts prompting one or more of these adaptive responses will come in three simultaneous waves putting relentless pressure on environmental law. First will be the direct alterations to regional and local environments caused by the macro effects of climate change, such as inundation of wetlands caused by sea level rise and vegetation transition caused by reduced rainfall. Central goals of environmental law, such as ecological conservation, will be severely challenged in these contexts. Second will be the direct environmental impacts of human adaptation responses, such as coastal armoring to withstand sea level rise and increased water diversion and usage to offset lower rainfall. Environmental law has always attempted to manage human behavior toward the environment, and that job will be more complex than ever when aimed at climate change adaptation behavior. Finally, environmental law must interact with other fields of law and policy and manage the indirect environmental spillover effects of adaptive responses that have little or nothing to do directly with the environment, such as in national security, immigration, public health, human rights, finance, housing, and trade policies. Environmental law has long recognized the need to address policy spillover effects, but they will be intensified in the climate change adaptation context.

Part III of the Article then describes the ten structural trends I predict environmental law will experience over the next few decades as it is shaped by the adaptation modes and pressures outlined in Part II. Although I confess to relying on a strong dose of my own experience and perspective in formulating the trends, I have endeavored in earnest to make them more than just the world according to J.B. Ruhl. First, I conducted a literature survey by culling through the legal scholarship covering climate change adaptation in some substantial way and accounting for dominant themes and perspectives.[36] Based on that assessment, I articulated and organized a set of trends, which I then briefly described in several postings on the environmental law professors listserv, envlawprofs, for reactions from anyone willing to comment. I received many insightful comments, based on which I refined my list to these ten trends:

  1. Shift in emphasis from preservationism to transitionalism in natural resources conservation policy
  2. Rapid evolution of property rights and liability rules associated with natural capital adaptation resources
  3. Accelerated merger of water law, land-use law, and environmental law
  4. Incorporation of a human rights dimension in climate change adaptation policy
  5. Catastrophe and crisis avoidance and response as an overarching adaptation policy priority
  6. Frequent reconfigurations of transpolicy linkages and trade-offs at all scales and across scales
  7. Shift from “front end” decision methods relying on robust predictive capacity to “back end” decision methods relying on active adaptive management
  8. Greater variety and flexibility in regulatory instruments
  9. Increased reliance on multiscalar governance networks

10.   Conciliation

The first six of the trends reflect forces that will transform the boundaries and capacity of environmental law. The next three trends anticipate shifts in the policy instruments, decision methods, and institutional restructuring that will follow inevitably from the first six trends. The final trend captures some holistic observations about the posture of environmental law in the period of climate change adaptation.

Notwithstanding the rather sprawling scope encompassed in the ten trends, an overarching theme emanates from their collective impact: Do not expect adaptation policy to play out for environmental law the way mitigation policy has and is likely to continue. Mitigation policy has been framed as an initiative primarily within the domain of environmental law, a

form of pollution control on steroids, and thus it will be environmental law that makes the first move and other policy realms that apply support or pushback. By contrast, environmental law does not “own” adaptation policy; rather, numerous policy fronts will compete simultaneously for primacy and priority as people demand protection from harms and enjoyment of benefits. This makes it all the more pressing for environmental law, early in the nation’s formulation of adaptation policy, to find its voice and establish its place in efforts to close the adaptation deficit.

II. What Is Climate Change Adaptation?

I ask readers to take as a given that climate change impacts under any realistic mitigation scenario are going to be complex and unpredictable over the next century.[37] The major categories of probable impacts for humans and the environment in the United States include the following:

Climate change will stress water resources. . . .

. . . Crop and livestock production will be increasingly challenged. . . .

. . . Coastal areas are at increasing risk from sea level rise and storm surge. . . .

. . . Risks to human health will increase. . . .

. . . Climate change will interact with many social and environmental stresses. . . .

. . . Thresholds will be crossed, leading to large changes in climate and ecosystems.[38]

I provide details in Part III where needed to advance the discussion, but for now it suffices to acknowledge that climate change will play out over the globe in a multitude of dynamic, feedback-plagued, nonlinear physical and biological trends that will be uneven spatially and temporally across the planet and will pose numerous policy trade-offs.[39] Sea level will rise here and fall there;[40] there will be more rain here and less there;[41] some species will die, some will move, and some will stay;[42] some crops will fail where they once thrived and some will thrive where they once had no hope;[43] some humans will get poorer, some richer, some will move around, and some will die. The picture of how these and other impacts will play out will change over time, and it will all be happening under a new set of rules about which we know very little at the moment.[44] How bad it will be for any particular local or regional community is unclear; indeed, it won’t be so bad for some people or other species in some places—it might even be smashingly good.[45]

The bottom line for policy, therefore, is that planning for the future based on the climate of the past will lead to folly.[46] Climate change will require people to develop new strategies for avoiding and recovering from its harms and capturing and harnessing its benefits. This will become a costly global undertaking[47] with potentially significant environmental impacts of its own.[48] Environmental law thus necessarily will be part of the policy formulation mix, and to play that role, environmental law will need a theory of adaptation to better understand the modes in which people will adapt and the pressures doing so will place on the environment and environmental law.

A. Adaptation Policy Parameters

Unlike the story in legal scholarship, the body of literature on climate change adaptation from the physical, social, and policy sciences is already massive and growing at a stunning rate. It is also difficult to make sense of the emerging theory in terms relevant to legal discourse, as the literature proposes all variety of models for understanding what climate change adaptation is about but offers very little in the way of concrete frameworks for building hard law to apply at national, state, and local governance scales. I cannot hope here to comprehensively review the full scope of the theoretical foundations being advanced; rather, I have extracted and synthesized from the various leading sources seven parameters that authors present as the predominant drivers of adaptation policy design, each of which defines a range of policy perspectives or options summarized in Table 1 at the conclusion of this section.

1. Actor

Although formulation of climate change policy is more often associated with the public sector leading the way with planned initiatives, climate change adaptation policy will be profoundly influenced by strategies and initiatives from the private sector taking autonomous initiatives.[49] Private markets and institutions will adapt to climate change with individualized and industry-wide strategies and initiatives that may go a long way toward facilitating the reduction of harms and the harnessing of benefits of climate change. Moreover, within the two categories, public and private, a broad array of actors is defined, including various scales of government and types of private actors, including individuals, corporations, and nongovernmental organizations, all with keen interest in adaptation policy.[50] In addition to basic questions of which governance scale is appropriate for public planning, therefore, the public sector also will need to consider the role and regulation of private autonomous adaptation efforts.

2. Response Orientation

Many adaptation policy theorists distinguish between proactive adaptation strategies (also known as preventative, or anticipatory) and reactive strategies.[51] Proactive strategies anticipate climate change impacts to design measures that will reduce harm or harness benefits in the future, such as crop and livelihood diversification, seasonal climate forecasting, community-based disaster risk reduction, famine early warning systems, insurance, water storage, supplementary irrigation, and so on.[52] By contrast, reactive strategies design responses based on observed climate change impacts as they occur through measures such as emergency response, disaster recovery, and migration.[53] Many climate change impacts could be addressed through either orientation. The United States Fish and Wildlife Service explains the distinction:

Reacting to climate change . . . is reactive adaptation. Combating rising sea levels by pumping sand ashore to replenish beaches and maintain existing habitat for nesting sea turtles and shorebirds is an example of reactive adaptation. A second approach to responding to climate change is to manage toward future, and often less certain, landscape conditions by predicting and working with the effects of climate change. . . . An example of anticipatory adaptation is planning for sea level rise by modeling future shoreline conditions; developing shoreline “retreat” plans (including relocation of infrastructure) that allow rising sea levels to erode existing beaches and establish new shorelines landward for nesting sea turtles and shorebirds; and monitoring the results.[54]

In general, the perception is that “a ‘wait and see’ or reactive approach is often inefficient and could be particularly unsuccessful in addressing irreversible damages, such as species extinction or unrecoverable ecosystem damages, that may result from climate change,” though in some cases there may be no choice but to wait and see.[55]

3. Adaptation Goals

It is stating the obvious that the goal of most climate change adaptation policy development is to minimize and recover from the harms of climate change. But that cannot be the exclusive focus. Although it is not often acknowledged in the climate change mitigation dialogue, which is mostly about preventing climate change because of its perceived distributional harm to some populations and net aggregate harm to humans and the environment, climate change will produce benefits for many human communities and other species, in some cases substantial benefits.[56] Temperature and rainfall changes, for example, will open up new agricultural or recreational possibilities for areas previously limited in these respects.[57] Hence, the goal of regional and local climate change adaptation policy frequently will be about taking advantage of change and making life better, not worse, for people and other species. This will no doubt be politically sensitive, as many communities will be struggling predominantly to reduce harm, but securing benefits when and where they are available will nonetheless be an inevitable goal of adaptation policy in general and often times a primary goal locally.

4. Management Target

In broad terms climate change will initiate environmental impacts in two different dimensions. One will be changes in variability of natural events for which we already have developed adaptive strategies, such as floods, hurricanes, and fire.[58] Also known as Type I adaptation, the challenge here will be whether the existing adaptive strategies are sufficiently robust to manage the effects of increased or decreased frequency of these natural events.[59] The other dimension of effects involves the absolute changes to the environment that will result from climate change, such as sea level changes, reduced glacial coverage, and higher mean surface temperatures.[60] We have not developed tested adaptation strategies for these changes, also known as Type II adaptation, simply because we have not experienced them in the past several centuries over any significant period of time.[61] There will also be synergistic effects between these two types of change, as for example when increased hurricane frequency combines with higher sea levels to exacerbate coastline and inland vulnerability in some areas.[62]

5. Policy Foundation

Climate change adaptation will involve a mix of substantive and procedural strategies and innovations. Professor Alex Camacho describes government substantive adaptation in three categories: 1) altering the environment to minimize the effects of climate change, 2) regulations and other measures to alter the way private actors interact with the environment, and 3) agency management planning designed around adaptation.[63] By contrast, procedural adaptation involves “strategies that manage the regulatory programs and processes that develop more direct strategies.”[64] These could include new decision making processes, such as the use of adaptive management in natural resources management, and far broader changes to institutional and governance systems.[65] The same two‑pronged approach could be used in private sector climate change adaptation as well.

6. Capital Employed

Climate change adaptation will be a capital-intensive undertaking, but we will not be limited to using only technological capital. We will also be deploying financial capital to invest in new technologies and institutions, human capital in the form of adaptation knowledge and skills, social capital in groups and institutions with new norms and practices, and natural capital such as wetlands and coastal dunes to provide adaptive capacity.[66] Responding to increased storm surge frequency and intensity along coasts, for example, could rely on technological capital in the form of seawalls, financial capital in the form of modified insurance and financing policies, human capital in the form of improved building techniques, social capital in the form of emergency response and retreat practices, and natural capital in the form of enhanced coastal wetlands and dune systems.[67] It will only infrequently be obvious which form of capital investment will prove most effective at avoiding harm or harnessing benefits, and often there will be trade-offs inherent in selecting one mix of capital versus an alternative.

7. Strategy

Adaptation to climate change impacts will leverage two different but closely related strategies focused on deflecting and recovering from the blows of climate change.[68] One is to reduce vulnerability by improving the reliability of infrastructure and other mechanisms designed to shield human communities and ecosystems from the harmful effects of climate change, such as by constructing seawalls to protect coastal areas or limiting new development permits on coasts likely to experience sea level rise.[69] If the risks associated with vulnerability can be reduced through such methods, less harm will be sustained and less capital will need to be deployed to recover from the effects of climate change. Yet, not all the risks of climate change can be reduced in this manner, as costs, technological constraints, lack of knowledge, and mistaken assumptions will limit the capacity to improve reliability. The other strategy thus focuses recovering from the blow of climate change by enhancing resilience to impacts, such as through improved emergency response techniques and habitat restoration methods.[70] Many human communities and ecological landscapes will require a mix of these strategies to make effective use of available technological, financial, human, social, and natural capital.[71]

Table 1. Climate Change Adaptation Design Parameters

 

Parameter

Design Options

Actor

Public-Planned Û Private-Autonomous

Orientation

Proactive (a/k/a Preventative, Anticipatory) Û Reactive

Goals

Avoid and Repair Harm Û Capture and Harness Benefits

Management Target

Change in Variability Û Absolute Change

Policy Foundation

Substantive Û Procedural

Capital Employed

Technological Û Financial Û Human Û Social Û Natural

Strategy

Reduce Vulnerability Û Enhance Resilience

B. Modes of Adaptation

As the previous Subpart illustrates, climate change adaptation measures will come in many combinations of policy parameters and the mix of federal, state, local, and private responses is likely to be exceedingly complex. But no matter what the mix and what form any particular adaptation policy assumes, every adaptation measure is designed to facilitate one or more of three possible modes of adaptation for local and regional human populations and for other species and their ecosystems: 1) resist the effects of climate change to maintain the status quo in situ; 2) transform physical, social, environmental, or economic conditions in situ to minimize harm or maximize benefits associated with climate change impacts; or 3) move humans or other species to locate better adaptive capacities.

Take as examples the city of Miami, Florida, and the nearby Biscayne Bay Aquatic Preserve, which the state of Florida established in 1974 to be “preserved in an essentially natural condition so that its biological and aesthetic values may endure for the enjoyment of future generations.”[72] These human and natural environments face substantial threats from climate change impacts such as sea level rise, introduction and loss of species, loss of coastal resources, and more frequent and intensive storm events, to name but a few.[73] Miami’s city managers and the Preserve’s resource managers could adopt either of the three adaptation policy goals, but with vastly different policy implications.

1. Resist

Some people like the status quo. Miami, for example, might want to stay as close as possible to the way Miami is today, notwithstanding climate change. The city might invest in this resist mode of adaptation by building seawalls, using pesticides to control invasive disease-bearing insects and parasites, importing more sand, energy, and water to support its beach tourism industry, and establishing health management systems to deal with increased disease. The Preserve managers might work tirelessly to import water, soils, and other resources to prop up wetlands and corals diminished from climate change, and they may intervene to prevent species from moving into or out of Biscayne Bay in response to climate change.[74]

Obviously, this kind of resistance to climate change can only go so far on a local basis. The capital costs needed to resist all the effects of climate change would be daunting in many locations. Even where sufficient financial capital is available to make that kind of investment, fierce competition among localities for access to water, energy, and other resources necessary for sustained resistance is likely to be the norm. Indeed, on a macroregional or national scale the resist strategy cannot be uniformly maintained—to the extent managing numerous areas such as Miami and the Preserve for the status quo depends on importing water, energy, or other resources from somewhere else, then obviously not every human and natural environment can be managed for the status quo. Nevertheless, it is likely many areas of the nation will take measures to retain at least some aspects of the status quo through adoption of the resist mode of climate change adaptation strategies.

2. Transform

The transformative effects climate change will have on conceptions of variability and change in human and natural environments will undermine the very premise of many resistance strategies. The resist mode of adaptation is likely to be swamped by climate change in many contexts, shifting the focus of performance from maintaining the status quo to measuring how far off the status quo conditions have moved. Given this reality, some communities and resource managers are likely simply to adopt a transform mode of adaptation from the start. Transform modes of adaptation assume that maintaining the status quo is either not feasible or is not a desirable policy goal because of costs or other trade-offs, and thus adopt transition and change as integral parts of adaptation policy.[75] Miami’s city managers, for example, may hope to replace beach tourism with some other form of tourism. And rather than try to hold on to existing coastal structures and infrastructure supporting them, Miami might decide to impose significant beachfront setbacks and stop providing new public infrastructure to continue supporting new private development along the existing coast.[76] Similarly, the Preserve’s managers may decide to replace species-specific goals with broader goals such as conserving an overall mix of biodiversity without regard to species assemblage or the health of a particular species. What passes as “Miami” or the “Preserve,” in other words, would no longer be referenced from the status quo of the past but rather from the anticipated future.

3. Move

The stark reality of climate change is that conditions could exhibit extreme swings for the better or worse in some areas. In those circumstances, it is possible neither the resist mode nor the transform mode of adaptation will be viable. Conditions may become too stressed in some areas to tolerate, or too good in other areas to forego. If people decide to leave Miami for other areas, or if the Preserve’s resource managers decide to engage in assisted migration of species to other aquatic settings, that reflects a decision that maintaining the status quo in situ is not feasible or practicable and that transformation with change in situ is not viable either.[77]

The move strategy is already evident in the shifting ranges of some species.[78] Of even greater concern to climate adaptation policy is the likelihood that people numbering in the hundreds of millions may be displaced from climate change “hot spots” and seek refuge elsewhere.[79] Human migration in response to environmental change has been experienced before mostly in connection with local disasters, whereas climate change may trigger broader, longer, and more persistent migratory responses.[80] But who will welcome climate refugees, and who is prepared for them whether welcome or not?

C. Environmental Policy Pressures

Climate change adaptation carried out through the three modes, using various combinations of the adaptation policy parameters, will present three sources of pressure on the environment that will require formulation of environmental policy decisions: 1) direct environmental effects, 2) the environmental effects of human adaptation, and 3) policy spillover effects.

1. Direct Environmental Effects

One set of environmental policy decisions for climate change adaptation will involve measures to respond on behalf of the environment to the direct effects of climate change, such as sea level rise, species migrations, and shifting hydrology, that mitigation policy has yet to arrest and which have not been the target of broader adaptation policy initiatives. Environmental law has always had the dual functions of controlling sources of harm (e.g., pollution control) and responding to the effects that have not been or cannot be avoided (e.g., site remediation).[81] Climate change adaptation will require us to think more innovatively, however, as we design policy measures in the resist, transform, and move modes to assist species and ecosystems in avoiding harm and harnessing benefits of climate change.

For example, Section 4(a) of the Endangered Species Act (ESA)[82] provides for designation of “critical habitat” of endangered species that includes “specific areas outside the geographical area occupied by the species . . . upon a determination . . . that such areas are essential for the conservation of the species.”[83] This authority could provide a viable way to respond to ecological reshuffling of species. To the extent climate models can predict with reasonable certainty where a species might successfully migrate to adapt to changes brought about by climate change, a credible interpretation of the critical habitat provisions would allow the agency to “reserve” those areas through critical habitat designations,[84] thus helping to secure migratory corridors and the species’ transitional and final ecological homes.

This approach to facilitate species as they adapt through a move mode would also provide an effective tool to guide human adaptation measures to minimize effects in designated areas, thus securing a greater chance for the species to withstand climate change transitions and establish a viable population in its new ecological home. Of course, that is part of the problem—measures designed to assist species and ecosystems in adapting to climate change could constrain human adaptation measures, and vice versa, which leads to the next type of policy pressure.

2. Environmental Effects of Human Adaptation

Just as the primary threats to species and ecosystems before climate change centered around human-induced ecological change, it is likely that the resist, transform, and move modes of human adaptation to climate change will play a leading role in threatening environmental resources. For example, climate change is likely to lead human populations to increase rainwater harvesting and water storage, adjust the timing and location of crop plantings, relocate seawalls and other storm barriers, move urban infrastructure to account for changing water supply opportunities, and shift recreational facilities such as ski slopes to higher altitudes, to name just a few probable responses.[85]

Several forms of human adaptation impacts will present the most pernicious of such threats. First, many human communities are likely to find it necessary and possible to migrate to avoid rising sea levels along coastal areas, to relocate agricultural land uses, and to obtain secure water supplies from ever distant locations.[86] These migrations and transfers of resources will necessarily involve some conversion of land uses in areas that presently provide suitable ecological conditions for particular species, in some cases at scales sufficient to pose a threat to the species.[87] Relocated human communities will likely also introduce ecological degradations from new or amplified pollution, noise, water diversions, and other stresses.[88] Many human communities, relocated or not, also will implement climate change mitigation and adaptation measures designed primarily to protect human health and welfare, such as coastal flood barriers, which in some cases could threaten ecological conditions for other species.[89] Even planting of forests to sequester carbon could degrade conditions for some species.[90] Lastly, human adaptation to climate change involving population relocations and increased flow of goods and resources to new settlement areas is likely to introduce nonnative species to local ecosystems, some of which will establish successfully.[91]

3. Policy Spillover Effects

Climate change adaptation will engage a far broader policy realm than just environmental policy, and the focus of other policy fronts such as national security, immigration, public health, and food supply is likely not to place environmental impacts at the forefront of decision-making processes.[92] Environmental law thus will be faced with managing the spillover environmental effects of these other policy decisions, and often will do so not as an “insider” in the decision process. This will not be a new role for environmental law by any means, but climate change could present such pressing and immediate policy response needs in these other contexts that environmental law sees itself pushed even harder to the margins.

III. Ten Structural Trends in Environmental Law

The previous Part outlines the policy context of climate change adaptation. There will be widespread need at national, state, and local governance scales to design and implement strategies that facilitate how humans, other species, and ecosystems resist, transform, and move in response to climate change.[93] Every such adaptation initiative can choose from a complex mix of policy parameters, and every such adaptation initiative could present environmental impacts of its own. Particularly over the next two decades, as adaptation policy initially ramps up, environmental lawyers can expect a highly dynamic period of change.

To be sure, no one could reasonably accuse environmental law of being static; indeed, the forty-year story of modern statutory environmental law is one largely of change. But it has been a story primarily of goal-oriented change motivated from within environmental law to address discrete pollution media and conservation objectives.[94] Those days are over. Environmental law does not “own” climate change adaptation policy. Rather, it may be just the reverse, as national, state, and local adaptation priorities place tremendous pressure on environmental law to partner with other fields of law in facilitation of adaptation. I am not sure where this leads, but I have some ideas about how climate change adaptation policy will most profoundly transform environmental law—ten of them to be exact.

A. Trend One: Shift in Emphasis from Preservationism to Transitionalism in Natural Resources Conservation Policy

The development of environmental law has taken many of its cues from environmental and ecological sciences, which themselves have evolved over time.[95] With ecology in particular, the trend over the past half-century has been increasingly to focus on the complex flux qualities of ecosystems and to place less emphasis on conceptions of stasis and natural stability.[96] Nevertheless, the “dynamic equilibrium” model that is now firmly in place in ecology is based on the assumption of “stationarity,” which as Milly et al. explains is “the idea that natural systems fluctuate within an unchanging envelope of variability.”[97] Although ecologists understand that the envelope can be stretched by natural and anthropogenic events, those are considered manageable disturbances. In the context of water resources, for example, Milly et al. argue that

[t]he stationarity assumption has long been compromised by human disturbances in river basins. Flood risk, water supply, and water quality are affected by water infrastructure, channel modifications, drainage works, and land-cover and land-use change. Two other (sometimes indistinguishable) challenges to stationarity have been externally forced, natural climate changes and low-frequency, internal variability (e.g., the Atlantic multidecadal oscillation) enhanced by the slow dynamics of the oceans and ice sheets. Planners have tools to adjust their analyses for known human disturbances within river basins, and justifiably or not, they generally have considered natural change and variability to be sufficiently small to allow stationarity‑based design.[98]

Legal scholars who have traced the influence of this scientific paradigm shift on environmental law find, as is often the case, law lagging behind.[99] Legal regimes that formed before the dynamic equilibrium model was well developed, particularly conservation programs such as the ESA, the Wilderness Act,[100] and the National Wildlife Refuge System,[101] to this day depend heavily on the natural stability model of ecosystems and the strategy of setting aside habitat reserves to implement it.[102] Only recently has the discipline of ecosystem management emerged with any concrete policy force to prompt movement toward the dynamic equilibrium model.[103] This newer, more flexible conservation orientation, however, still depends strongly on the stationarity premise and its appeal to “natural” and “native” models of ecosystem dynamics.[104] For example, the disciplines of habitat restoration and enhancement, which rest at the foundation of newer approaches to conservation policy such as wetlands and habitat mitigation banking, assume that we know the bounds of the stationarity envelope for the given ecosystem and can work to preserve them in perpetuity.[105]

The stationarity premise and all on which it based, however, are going to fall to pieces in the era of climate change. In its stead ecologists now warn of the no-analog future—ecological variability unprecedented in the history of ecology, riddled with nonlinear feedback and feedforward loops, previously unknown emergent properties, and new thresholds of irreversible change.[106] The “envelope” of variability will grow to dimensions not previously experienced, and ecologists, including paleoecologists who have studied past climate change eras, have no analog for predicting where it is headed.[107] Clearly, therefore, the stationarity premise, which threw the natural stability premise out the window, is about to be thrown out the window itself.

Resource managers have begun to come to grips with this reality. Climate change, in the words of the U.S. Fish and Wildlife Service, “is the trans-formational conservation challenge of our time, not only because of its direct effects, but also because of its influence on the other stressors that have been and will continue to be, major conservation priorities.”[108] Similarly, in the water resources context Milly et al. suggest that

[i]n view of the magnitude and ubiquity of the hydroclimatic change apparently now under way, however, we assert that stationarity is dead and should no longer serve as a central, default assumption in water-resource risk assessment and planning. Finding a suitable successor is crucial for human adaptation to changing climate.[109]

So, what is the successor for conservation policy? Clearly, the preservationist foundations of the habitat reserve strategy, whether applied in the form of a wildlife refuge, a habitat mitigation set aside for an endangered species, a wilderness area, or a wetlands mitigation bank, are on shaky ground.[110] What is it that the reserve is preserving if “natural” and “native” no longer have the same meaning as they do under the stationarity premise? Is a species migrating from a now inhospitable climate-altered ecosystem “invasive” in its new ecosystem, or is it to be commended and protected for its “natural” adaptation? Is a wildlife refuge established for waterfowl a failure if it dries up, and if so should we import water to keep it “natural” so the “native” species can remain there?[111] We could debate these questions, of course, but my point is that the prevailing model of conservation has no answers. These questions only exist because we are entering a whole different ballgame.

In short, if stationarity is dead in conservation science, preservationism is dead in conservation policy. This is a constraint climate change will impose on environmental law regardless of our needs and desires. Preservation of natural ecological conditions, which would require going all in with our conservation chips in the resist mode of climate change adaptation, is going to be either impossible in many circumstances or more expensive than could possibly be justified in others.[112]

Over time, our ability to “manage for resilience” of current systems in the face of climate change will be limited as temperature thresholds are exceeded, climate impacts become severe and irreversible, and socioeconomic costs of maintaining existing ecosystem structures, functions, and services become excessive. At this point, it will be necessary to “manage for change,” with a re-examination of priorities and a shift to adaptation options that incorporate information on projected ecosystem changes.[113]

Hence the successor, managing for change, must embrace the transform and move modes, looking toward a transition to the future for its reference points rather than to the past as preservationism does. The transition, to put it bluntly, is from the nature we once knew to the nature that we expect to find around us on the other side of climate change. Only when we get there, however, can we begin to talk again about what belongs where under the new set of natural conditions.

What does this mean for conservation policy during the century of climate change adaptation? One option is simply to let ecosystems ride out climate change and see what we get, but most ecologists believe active management of some kind is needed to better serve the twin goals of adaptation—to minimize harm along the way and to position us to resume sustainability planning in the future.[114] Two overarching principles seem to rise in answer to those goals. First, although techniques of restoration and enhancement will still be used in practice, they must be directed toward new transitional strategies.[115] For example, whereas the critical habitat program under the ESA has been fixated on identifying and preserving existing essential habitat for species, it will probably do many climate-threatened species more good to roll in conservation strategies across the landscape over time to track where species are migrating or likely will migrate.[116] The critical habitat for a climate-threatened species, in other words, might be not only where the species is found today, but also where it will try to go in
the future.[117]

Second, the central objective of conservation policy for climate change adaptation should be focused broadly on biodiversity conservation rather than on conservation of particular species, particular refuge purposes, or particular wilderness conditions.[118] Rather, ecosystem resilience is what will best position us for resuming sustainability planning in the next century, and ecosystem resilience resides in biodiversity.[119] In short, environmental law is going to have to give up on the preservation strategy, which will be immensely difficult given how deeply ingrained it is in environmentalism’s psyche. The job of its successor, transitionalism, will be to shape conservation policy toward the transform and move modes of climate change adaptation.

B. Trend Two: Rapid Evolution of Property Rights and Liability Rules Associated with Natural Capital Adaptation Resources

A fairly reliable rule of thumb is that if the insurance industry is convinced something is going to be a problem, it is going to be problem. And the insurance industry is convinced climate change is going to be a problem.[120] What this means is that insurers are anticipating that climate change will lead to costly property losses, business damages, and personal injuries to insured and insurable interests, and that adaptation to avoid or repair those damages will also be costly.[121] This, of course, raises both opportunities and risks for insurers, but that is, after all, the nature of insurance. My point in bringing up the insurance industry, though, is that insurers tend to be astute at detecting significant shifts in relationships and expectations looming on the horizon and try to anticipate how new forms of injury will work their way through the insurance coverage and liability system.[122] Thus it is no surprise that the industry has moved quickly to begin to assess the impacts of climate change.

What has piqued the insurance industry’s interest in climate change is also sure to grab the attention of legal systems. Much of the focus in that respect has been in establishing the public law of mitigation and adaptation strategies through legislative and regulatory initiatives.[123] We should not forget, however, about the common law. In particular, the same unsettling of relationships and expectations that is on the mind of insurers is bound to creep into the common law through pressure on existing property rights and liability rules. Climate change adaptation will inextricably and fundamentally link people in ways they have not experienced before, and new controversies are bound to surface in connection with their property and their safety. Put simply, some people are going to take actions with their property and personal behaviors, or fail to take actions, that put the property and safety of other people at significant risk of injury. It is inevitable that those injured will pursue remedies, and the courts will have to determine who should pay.[124]

Take for example the owner of coastal property with an intact dune system. As sea level rises and hurricane activity intensifies, that property will become increasingly important as a buffer from storm surge for inland properties.[125] Should that change the way we view the property rights associated with the property? To be sure, an extensive public law regime exists to limit the use of coastal and other natural resources in the interest of public goals such as conservation, but it has not been directed primarily at formulating the relationship between private parties with stakes in the protective functions of natural resources.[126] With rising sea levels, loss of coastal dunes will increase risks to inland property, businesses, and people.[127] Similar scenarios could be played out for coastal wetlands, aquifer recharge resources, inland wetlands providing groundwater recharge and thermal regulation, and a host of other settings. To the extent the common law is settled on the scope of relative property rights in these contexts—for example, that there is no restraint as a matter of the common law of nuisance on the destruction of coastal dunes—that was all settled before climate change came into the law’s consciousness.

And we know the common law evolves to take into account new developments in the law’s consciousness. Indeed, Justice Scalia has reminded us of this in a context directly on point in his majority opinion in Lucas v. South Carolina Coastal Council, where he established the “relevant background principles” of state property law as the reference point for testing whether public regulation or private property—in that case, development of coastal dunes—goes so far as to constitute a categorical taking of property.[128] He also confirmed, however, that those background principles evolve with “changed circumstances or new knowledge,” such that, over time, what was once allowed under common law no longer is.[129] No doubt this is not what he intended, but those few lines have opened up a cottage industry of lawyers searching for new knowledge and changed circumstances to move the background principles one way or the other.[130]

Over the past decade, for example, the discipline of ecological economics has produced a burgeoning body of research illuminating the significant economic value that functioning ecosystems, acting as natural capital, supply humans in the form of direct and indirect ecosystem services, such as the capacity of coastal wetlands to mitigate storm surges.[131] Even without having to take into account climate change impacts, this body of new knowledge is already surfacing in commentary and the courts to put pressure on common law property doctrine, particularly the law of public and private nuisance and of the public trust doctrine, to reconfigure relative property rights accordingly.[132] And well it should, as it simply requires that property owners use property efficiently and pay for their negative externalities.

Climate change will only accelerate this evolutionary process.[133] Already, for example, renewable energy markets emerging in response to climate change mitigation policies are causing property law scholars to reexamine old topics such as access to solar energy[134] as well as to explore uncharted territory such as access to wind energy[135] and who owns the underground space that might be devoted to carbon sequestration.[136] Climate change adaptation strategies are even more likely to trigger property rights disputes in need of new judicial examination given mounting knowledge about ecosystem services.[137] As natural capital resources that provide ecosystem services such as storm surge mitigation factor increasingly into climate change adaptation policy—which will happen precisely because of the ecosystem services provided—it is likely that the common law will grab hold of this new knowledge even more aggressively. Indeed, whereas the public nuisance and other common law claims that states and other interests have lodged against large sources of greenhouse gas emissions as part of a mitigation litigation strategy are high profile media stories notwithstanding limited success,[138] it is likely to be in the more discrete, small-scale context of adaptation in which the common law will have reason to evolve.

Of course, the common law ought to develop in this respect to serve the purposes of the common law. Nuisance law, for example, polices unreasonable use of property in particular contexts,[139] and the public trust doctrine protects important but limited public interests in water resources.[140] They are by no means doctrines on which we can rest all or most of climate change adaptation law, and I am not suggesting we violate the basic underpinnings of the common law in order to get climate change adaptation mileage out of them. Rather, it seems inevitable that many nuisance, public trust, and other claims like this are going to be made—claims that one property owner can’t take actions that substantially impair the climate change adaptation profile of other property owners or the public—and that courts are highly unlikely to (and should not) throw the claims out on motions to dismiss. The litigation grist mill will gear up to resolve these claims, and new ground is likely to be covered to further the traditional common law interests of efficient use of property.

I will come clean here, however, and confess full awareness that an important secondary effect of any movement of the common law along these lines, perhaps more important than the evolution of relationships defined by common law, will be the corollary Justice Scalia established in Lucas that public environmental law can move in behind the common law evolutionary step to establish more comprehensive regulatory regimes without pushback from takings claims.[141] In this sense the development of the common law of climate change adaptation may liberate the public environmental law of adaptation to do more than it otherwise could have. Notwithstanding that the underlying rationale for evolution of the common law I am suggesting rests in economic efficiency and cost internalization, this prospect sends shivers down the backs of libertarians and free market environmentalists.[142] I refer their complaints to Justice Scalia, who, after all, planted this Trojan horse in Lucas; my interest is only in ensuring that common law doctrine incorporates the immense economic value of ecosystem services the same way it does other economic attributes of property. Climate change adaptation is in all likelihood going to be the catalyst for that to happen with uncharacteristic speed for the common law.

C. Trend Three: Accelerated Merger of Water Law, Land‑Use Law, and Environmental Law

Water law scholars, Professor Dan Tarlock in particular, were the first to focus attention on climate change adaptation policy,[143] and land-use law is well represented among the now broader scope of legal scholarship engaging adaptation.[144] There is good reason both of these fields have become prominent topics in the adaptation mix—land-use and water allocation decisions are likely to be the hottest of hot button issues as climate change effects take hold over the landscape.

The intersection between land-use law, water law, and environmental law is nothing new, making “the interrelationship of water resources and land use . . . one of the hottest topics in land‑use today.”[145] Many contemporary large-scale problems involve all three fields of law working in a complex amalgam, making it difficult to characterize the problem as about land use, water allocation, or the environment.[146] Climate change will rapidly move the three fields of law even closer together, likely to the point that it will be meaningless in many contexts to think of them as separate fields of law and policy.

It is no surprise that water law scholars were the first movers on climate change adaptation, as water will likely be the first vital natural resource hit hard by climate change.[147] Consider Milly et al.’s summary of the climate change impacts scenario for water resources:

[S]ubstantial anthropogenic change of Earth’s climate is altering the means and extremes of precipitation, evapotranspiration, and rates of discharge of rivers. Warming augments atmospheric humidity and water transport. This increases precipitation, and possibly flood risk, where prevailing atmospheric water-vapor fluxes converge. Rising sea level induces gradually heightened risk of contamination of coastal freshwater supplies. Glacial meltwater temporarily enhances water availability, but glacier and snow-pack losses diminish natural seasonal and interannual storage.

Anthropogenic climate warming appears to be driving a poleward expansion of the subtropical dry zone, thereby reducing runoff in some regions. Together, circulatory and thermodynamic responses largely explain the picture of regional gainers and losers of sustainable freshwater availability that has emerged from climate models.[148]

The bottom line is that in some regions of the nation communities with adequate or marginally adequate existing access to freshwater supplies will find themselves high and dry. The move mode of adaptation strategies may be viable for some small communities, but it is more likely that substantial cities such as Los Angeles and Phoenix will, understandably, prefer to stay where they are, meaning they will have to resort to the resist and transform strategies. The resist strategy would likely involve searching for new supplies, such as desalination and more water transfers, and more intensive conservation measures.[149] In addition to shifts in regional industrial and agricultural profiles, the transform strategy may involve taking a serious look at the continued viability of applying what is now centuries old water law to questions of allocation and conservation of water resources.[150] In either case, however, the fact that entire major cities and regions will be on the line makes it likely that getting water to them will rise to the top of adaptation law and policy priorities, leading to intensified controversies between urban and rural areas as well as between states and regions of the nation.[151] Environmental impacts of these adaptive strategies, we can hope, will be integrated in the decision making, but in all likelihood managing for environmental effects will take a back seat to keeping urban communities and regional economies alive.

On the flip side, some regions of the nation presently lacking adequate water resources will benefit from climate change through increased precipitation, runoff, and recharge.[152] The new abundance of water will open up opportunities, such as increased agricultural capacity and room for residential and industrial development. Indeed, it may be critical to the national adaptation strategy that the regions climate change blesses with more water adapt specifically to provide a secure food supply and industrial base. Once again, we can hope that the environmental impacts of these adaptive uses of “new water” will be integrated into water resources development decisions. And so as not to repeat the mistakes of the “old water” regions that were experiencing supply stress well before climate change (and will be in crisis mode), one also can hope that the water law of these newly wetter regions will strike a different path to ensure more efficient use and allocation.[153] The bottom line, however, is that to the extent our national food supply and industrial capacity are put in jeopardy as a result of a new hydroclimatic regime, getting water to the right places will be the priority and the environmental impacts of doing so will often be of secondary concern.

Where water is and isn’t influences land-use decisions. The altered freshwater regime discussed above, therefore, will lead not only to new water law developments but also to profound land-use decisions in regions moving from wet to dry or dry to wet. Professor Tony Arnold has explored the increasingly intimate connection between land-use law, water law, and environmental law that existed well before this hydroclimatic shift. His assessment is that “[l]and use regulation and planning have taken an ‘environmental turn’: a pervasive and inescapable attention to the impact of land use and land development on the natural environment.”[154] This effect unquestionably will grow in importance as climate change moves water resources around the nation in ways never before contemplated. As we chase water, temperature, and other resources to develop new agricultural districts or expand existing ones, and as people move to locate new employment and residential opportunities, new land-use decisions will be made. As Arnold’s work suggests, with tighter integration of land and water concerns these new land-use decisions, we can hope, will be fused closely with environmental management in mind. Yet while environmental impacts will nest within these merged water allocation and land-use domains, the question will be under what priority.

Above all else, however, one has to believe that sea level rise will trigger a phenomenal series of land-use decisions for coastal communities. Assuming cities like Miami and New York plan to weather the century of climate change adaptation, they will need a new land-use vision. One author suggests, for example, that national land-use law will be needed,[155] while another offers the Dutch levee land-use system as a new land-use model for the coastal United States.[156] Clearly, this ultimate resist mode adaptation strategy would be an immense infrastructure project for any community, implicating property rights, land-use, and environmental concerns in a mix unlike any they have previously encountered. Moreover, smaller coastal communities may not have the resources to erect this kind of substantial coastal barrier, and will have to rely on transform strategies such as increased use of natural coastal resources for dampening the effects of sea level rise. Some communities may simply yield to the sea and recede landward, which would raise a host of land-use and property rights issues.[157] In all these and other possible scenarios, land, water, and the environment will intersect in ways that will demand new forms of land-use regimes.[158]

It is hard to say what the position of environmental law will be when embedded in this new land and water policy mix. It is possible that in some contexts, particularly the coastal contexts, the division between the three fields will truly cease to exist and lawyers will be practicing a new breed called “costal adaptation law.” But it is not clear how the environment will be represented. On the one hand, it may be pragmatic to reconnect what were once fragmented areas of law, but through their merger environmental interests could get lost in the amalgam. We can promise to be vigilant about securing the environment its due priority, but the prospects of Los Angeles without water and Miami knee deep in the wrong kind are likely to focus policy attention more on getting the adaptive strategy in place and less on worrying about its impacts on the environment.

D. Trend Four: Incorporation of a Human Rights Dimension in Climate Change Adaptation Policy

Just as climate change impacts will be felt unevenly across the globe, so too is the capacity to adapt unevenly distributed. In both cases, unfortunately, it is the least developed countries that drew the short straw—they will feel climate change more severely and have the least capacity to reduce vulnerability and boost resilience.[159] This double whammy effect has led the international law community to characterize global adaptation policy as a human rights issue.[160] Indeed, the vast majority of legal scholarship on climate change adaptation focuses on international law and international relations addressing four principal facets of this human rights dimension—the responsibilities of developed nations to 1) assist the adaptation efforts of least developed nations,[161] 2) assist the adaptation efforts of small island nations,[162] 3) assist the adaptation efforts of indigenous people,[163] and 4) assist the migration efforts of people from these three communities who are displaced by climate change notwithstanding adaptation assistance.[164]

While the United States will surely be at center stage as those “climate justice” issues play out in the international community dialogue on climate change adaptation,[165] a domestic version of the human rights dimension of adaptation policy is likely to emerge as well. Even before climate change came into the picture, an environmental justice theme emerged around the inequitable burdens the poor and people of color have sustained in terms of disproportionate exposure to pollutants, proximity to industrial sites and contaminated lands, and limited access to environmental amenities.[166] And from the aftermath of Hurricane Katrina in New Orleans and other hard-hit areas has emerged a similar theme of disaster justice.[167] As a report by the Congressional Black Caucus Foundation suggested as early as 2004, climate change will be a catalyst for fusing these two related movements into one focused on securing a human rights dimension to domestic climate change adaptation policy.[168] Where and how equitably will adaptation capital such as seawalls be deployed and financed? How will the health of low-income urban populations vulnerable to heat waves and pollution be protected? Who will get the water in areas drying out? For areas transforming with climate change, how will redevelopment and job creation play out across the community? If the only option is to move, how will low-income populations manage that?

Only a few legal scholars have addressed even the tip of the iceberg of this looming question of domestic climate justice policy,[169] and in general “the national debate on climate change policies has given insufficient attention to their environmental justice implications.”[170] Partly this may be due to the fact that the United States on balance does not fare that badly under generally accepted climate change scenarios, certainly not when compared to many other countries.[171] But that is just on balance. A recent study from the University of Southern California’s Program for Environmental and Regional Equity identifies how imbalances in vulnerability to climate change impacts and access to climate change adaptation resources will create a domestic “climate gap” in the United States, with communities of color and low-income on the short end.[172] Of principal concern are heat waves, increased air pollution, access to basic necessities, reduced job opportunities, and protection and recovery from extreme weather events.[173] Professor Alice Kaswan offers a flavor of how the already established environmental justice community has incorporated the climate justice theme to address these concerns:

In the climate change context, environmental justice groups are beginning to articulate overarching principles. . . . Recognizing the particular vulnerability of the poor and people of color, a number of the principles focus on the potential consequences of climate change and the critical importance of reducing GHG emissions. Several other principles focus on the implications of climate change policies, including a call for adaptation assistance for poor communities, as well as compensation for workers and others impacted by the potential economic costs of climate change policies. The environmental justice movement’s participatory goals are reflected in the call for community participation. The principles express caution about the emergence of international and national carbon markets. California environmental justice groups have been even more critical of market-based approaches.[174]

What lessons come out of this emerging theme of domestic human rights for domestic environmental law? One seems inevitable and critical to bear in mind—that it will be important to define the human right of climate justice and distinguish it from the concept that there is a human right to a certain level of environmental quality.[175] With respect to the adaptation side of climate policy, climate justice articulates not a right to environmental quality, but rather a right to equitable distribution of the benefits of climate change adaptation, which may or may not align with environmentalist norms of minimum conditions of environmental quality. Equitable distribution of climate adaptation resources and protections may not always fulfill conventional environmental protection norms such as conserving ecosystems and imperiled species, as, for example, when seawalls or beach renourishment may be needed to protect human communities unable to transform or move, or when water may need to be transferred to sustain urban populations of poor and people of color who have no options. This is not to say that climate justice will not promote environmental protection, but primarily when doing so serves climate justice interests. Climate justice, in other words, is first and foremost about protecting the poor and people of color, not the environment.

E. Trend Five: Catastrophe and Crisis Avoidance and Response as an Overarching Adaptation Policy Priority

Generally speaking, people are not in favor of catastrophes and crises. Yet the synergistic effects of changes in variability of storm, flood, drought, and fire events with absolute changes in sea level, temperature, and other climate features will lead to higher risks of catastrophic events and pandemic crises. People will demand protection.

This is not Chicken Little calling. Even relatively conservative scenarios of increased mean surface temperature lead to significant increases in risk of catastrophic events and pandemic health and safety crises. California’s adaptation strategy plan, for example, details high-level risk potentials involving a wide array of factors including heat waves,[176] disease vectors,[177] coastal extreme weather events,[178] water shortages,[179] food security,[180] fires,[181] and infrastructure damage.[182] Researchers anticipate numerous localized and reversible “disasters” involving these effects, as well the possible “mega-catastrophe”—“an event that is global in scale and has a high degree of irreversibility” and which, notwithstanding its low probability, “may account for a large portion of expected losses” from climate change.[183] Catastrophes of this magnitude could be triggered either as climate regimes cross nonlinear thresholds[184] or “the possibility that a series of more localized disasters could trigger other disasters, and that this cascade of consequences could become severe enough to create a
mega-catastrophe. This could include national security concerns, since a series of weather-related disasters could trigger political destabilization, mass migration, or violence.”[185]

Responding to this suite of risks, which will be demanded of both public and private actors, is likely to include adaptation methods and mechanisms to reduce vulnerability and enhance resilience, measures that in many cases will not be environmentally friendly.[186] On the table for consideration, one can imagine, will be environmentally intrusive adaptation initiatives such as seawalls, coastal armoring, water diversions, increased energy demand, new dams, relocated agriculture, removing habitat of disease vectors, new or raised levees, and other technological fixes that today receive intensive scrutiny under environmental laws and opposition from environmental protection interests.[187]

Measures like these when taken today, however, are implemented primarily as conveniences to ease urban life and prop up suburban and coastal property values, not as matters of necessity.[188] We can afford to entertain tough environmental standards and slowed-down approval procedures in that context, but as such measures are put into the climate change adaptation policy mix they will be portrayed as facilitating urgent and necessary adaptation strategies, particularly those built around the resist and transform modes, not as environmental intrusions to be contested until all the environmental impacts are fully accounted for. And to the extent people flee areas experiencing heightened risk of catastrophe and crisis notwithstanding improved technologies, the move mode of adaptation imposes its own set of environmental stresses.

Although other nations are moving forward with planning and policy for this scale of damage control[189] and some climate policy scholars have offered thoughtful adaptation policy models,[190] outside of a few states’ fledgling planning initiatives[191] the United States has compiled close to zero in the way of coordinated anticipatory adaptation policy for managing the risk in the United States of climate change catastrophe and crisis.[192] Our existing disaster management regime, moreover, was not designed around risk causes and consequences of this complexity and potential physical and geographic magnitude:

Despite the potential of both the Disaster Mitigation Act and the Coastal Zone Management Act, neither law is specifically designed to address the nation’s ability to adapt to climate change. Moreover, the lack of solid connections between and at various levels of government provides a significant barrier to the integration of land use management and other mitigation and response strategies. Within the U.S. system, confusion in planning and response is far more common than coordinated efforts and clearly delineated roles. As a result, an effective federal approach to mitigation requires a law similar to the Disaster Management Act but one that was specifically written to address climate change adaptation.[193]

This is a direct result of the adaptation deficit, not some rationalized decision to adopt a wait-and-see reactive adaptation orientation.[194] There is much catching up to be done.

I am headed here in much the same direction as with climate justice policy, which is a form of risk management for particular populations: Environmental law will be one among many players in the design of climate change catastrophe and crisis risk management. As the United Nations
has suggested,

[T]he complexity of risk-generating processes, the range of socio‑economic and environmental considerations that would come into play, and the diverse and complex nature of the social intervention required, requires the search for coherence and coordination . . . .

. . . The complexity of risk contexts demands increased integration, harmonization, and cooperation between until now separate concerns, caucuses and interest groups.[195]

Environmental law will need to find its footing in this new policy landscape, and given the high stakes for people it will not likely be the policy realm calling the shots. If dengue fever comes to Florida,[196] all bets are off.

F. Trend Six: Frequent Reconfigurations of Transpolicy Linkages and Tradeoffs at All Scales and Across Scale

The breadth and magnitude of problems associated with climate change, only some of which I have surveyed above, have led to calls for nations to assume a “war” mentality to combat the causes and consequences.[197] What is meant, of course, is that the steps necessary to bring climate change under control may require public and private measures on a scale similar to that of wartime. Indeed, that may very well be necessary, but the war usually held in mind in these policy proposals has been one against greenhouse gas emissions. The war on climate change, however, will not begin and end with mitigation—adaptation will be its other theater.

The adaptation front of this war is going to be fundamentally different from the mitigation front. The enemy in the mitigation war is easy to identify—greenhouse gas emission sources—so the battles will be over modifying behavior and technology to win the day. By contrast, the adaptation war, known in the adaptation theory literature as “mainstreaming” adaptation,[198] has climate change itself as the enemy. We’re not fighting only ourselves, in other words, we’re fighting something much bigger and over which we will have little control for at least this century. More akin to the Hundred Years War than an intense and swift battle, in this fight we resist, transform, and move over the long-term. That’s why it’s called adaptation.

As my previous five trends have begun to suggest, however, there is a lot more to how we fight in the adaptation theater of the war on climate change than will fit under the umbrella of environmental law.

Adaptation to climate change does not occur in isolation from the influence of other forces, but instead occurs amid a complex set of economic (micro and macro), social and institutional circumstances which establish a location‑specific context for human-environment interactions. In effect, there are many ‘non-environmental’ factors which impede or mediate change in human systems . . . .[199]

This complex of policy linkages will take place over three broad, interconnected dynamics that will challenge the ability of law to continue to operate on the premise of “stationarity” in social and economic affairs. The first will involve feedback between various fronts of climate change adaptation policy as local, state, federal, and private institutions attempt to mainstream adaptation strategies as a flow of coordinated decisions linking environmental policy with national security, immigration, trade, public health, finance, foreign aid, tax, social welfare, business policy, and housing polices, to name just a few, and do so across all governance scales.[200] Legal scholarship has begun to explore the depth to which the evolution of these transpolicy linkages will disrupt and reorder legal and policy domains that have depended on a relatively stable envelope of policy space within which the domestic legal world has worked over time.[201]

The second major dynamic will be the interaction of climate change adaptation policy holistically with other major global change drivers. Chief among these, according to an interdisciplinary team of researchers, will be increasing antibiotic resistance; increasing economic, social, and ecological connectivity; rising human numbers and urbanization; increasing per capita resources use; nuclear proliferation; international terrorism; energy, food, and water crises; declining fisheries; increasing ocean acidification; and emerging diseases.[202] These “intertwined global-scale challenges spawned by the accelerating scale of human activity” are “outpacing the development of institutions to deal with them and their many interactive effects.”[203]

The third major dynamic integrates the international dimension of climate change adaptation into national policy, as the United States loses its global hegemonic position and thus increasingly must set its national adaptation policy with other nations’ adaptation strategies taken into account. Some nations will hoard resources, some will send people outward, some will become unstable politically, some will become belligerent to neighbors, and so on. A number of international law scholars have identified this aspect of climate change policy as being perhaps the most vexing for the United States given the existing degree of fragmentation in international law and relations and the history of the United States’s self-proclaimed exceptionalism in our posture with other nations.[204]

Domestic policy decisions about whether and how to resist, transform, or move at local and regional scales thus will necessarily intersect a wide and dynamic array of policy realms. Environmental law, to the extent it retains a distinct identity in this complex, transpolicy, multiscalar network of decision making, will be but just one player. Moreover, like any complex network system, the linkages between components and between scales of components will evolve over time, meaning environmental law better stay alert and, like the Red Queen, run hard just to stay in place.

My ultimate message in this may be unsettling to environmentalists: Climate change adaptation policy is going to transcend environmental law quickly and decisively. Environmental law will be competing with a shifting array of other adaptation policy demands possessing potentially greater urgency and importance. Unlike mitigation policy, where environmental law is setting the agenda,[205] in adaptation policy environmental law is more likely to be told its place in line. This will be a hard pill to swallow, for environmental law has long positioned itself as the arbiter of what is good and bad development. For many people, however, adaptation fundamentally is not about development—it is about survival. It seems highly unlikely, therefore, that adaptation policy, as an amalgam of dozens of interests and needs ranging from urgent to critical, is going to anoint environmental law as its czar.

So what is environmental law to do? Adapt!

G. Trend Seven: Shift from “Front-End” Decision Methods Relying on Robust Predictive Capacity to “Back-End” Decision Methods Relying on Active Adaptive Management

Environmental law has positioned itself over time as a gatekeeper of development and infrastructure projects by imposing the requirement that a comprehensive environmental impact assessment be conducted prior to final government approval of the project under relevant permitting programs, the classic example being the National Environmental Policy Act (NEPA).[206] At the same time, environmental law, as part of the broader field of regulatory law, has also incorporated (often less than willingly) the discipline of cost-benefit analysis as the comprehensive gatekeeper test for the merits of development and infrastructure projects.[207] The details of both methodologies are intricate, and neither is free of criticism.[208] All that matters for my purposes are their two central attributes: 1) they are, as Professors Rob Glicksman and Sidney Shapiro put it, “front-end” decision tools comprehensively conducted and concluded prior to making the decision final,[209] and 2) as such they rely on a robust capacity to predict and assess environmental impacts of a project and the project’s overall costs and benefits. For example, regulations promulgated under the ESA provide for consultations between the U.S. Fish and Wildlife Service (FWS) and other federal agencies about the effects of their actions on protected species. These regulations require FWS to “[e]valuate the effects of the action and cumulative effects” and decide “whether the action, taken together with cumulative effects, is likely to jeopardize the continued existence of listed species.”[210] Section 404 of the Clean Water Act (CWA)[211] similarly requires the Corps to predict future cumulative effects and to integrate that prediction into its decision whether or not to permit developments that involve filling of wetlands.[212]

For purposes of climate change adaptation policy, the demand for predictive capacity will be the Achilles’ heel for the application of conventional environmental impact assessment and cost-benefit analysis. As previously discussed, the impacts of climate change necessitating human and environmental adaptation will be excruciatingly difficult to predict.[213] Nonlinearities in change dynamics, environmental feedback properties, and the interactions of social and ecological responses will soon exceed the boundaries of environmental stationarity that have allowed environmental impact assessment and cost-benefit analysis to maintain what reliability and credibility they have. Indeed, even before climate change adaptation became a pressing need, the challenges of front-end environmental impact assessment were evident in ecological contexts increasingly understood to be exceedingly complex.[214] For example, a 1997 guide on considering cumulative effects under NEPA explains that “[d]etermining the cumulative environmental consequences of an action requires delineating the cause‑and‑effect relationships between the multiple actions and the resources, ecosystems, and human communities of concern. Analysts must tease from the complex networks of possible interactions those that substantially affect the resources.”[215] The guide advises analysts to “gather information about the cause-and-effect relationships between stresses and resources” and to develop “a conceptual model of cause and effect . . . . Networks and system diagrams are the preferred methods of conceptualizing cause-and-effect relationships.”[216]

We simply don’t have the tools to apply that methodology to climate change adaptation and produce comprehensive front-end environmental impact assessments that will prove reliable over the long term. As noted previously, for example, the Intergovernmental Panel on Climate Change (IPCC) estimates of climate change impacts made just three years ago already are proving to have overshot and undershot observed changes.[217] Regional impact studies remain very coarse in detail,[218] and this is even more the case at local scales.

One of the main messages to emerge from the past decade of synthesis and assessments is that while climate change is a global issue, it has a great deal of regional variability. There is an indisputable need to improve understanding of climate system effects at these smaller scales, because they are often the scales of decision making in society. Understanding impacts at local scales will also help to target finite resources for adaptation measures.[219]

With respect to the last point made—targeting finite resources for adaptation—cost-benefit analysis fares no better than environmental impact assessment in the climate change adaptation world. The IPCC, for example, has concluded that “[t]he literature on adaptation costs and benefits remains quite limited and fragmented in terms of sectoral and regional coverage.”[220] The upshot is that

adaptation costs and benefits are usually embedded within climate damage functions which are often extrapolated from a limited number of regional studies. Furthermore, the source studies which form the basis for the climate damage functions do not always reflect the most recent findings. As a result, these studies offer a global and integrated perspective but are based on coarsely defined climate change and adaptation impacts and only provide speculative estimates of adaptation costs and benefits.[221]

The greatest impediment to relying on conventional front-end comprehensive cost-benefit analysis in the climate change adaptation context will be what Carolyn Kousky and Roger Cooke of Resources for the Future describe as the “unholy trinity” of fat tails, tail dependence, and microcorrelations:[222]

These are distinct aspects of loss distributions, such as damages from a disaster or insurance claims. With fat-tailed losses, the probability declines slowly, relative to the severity of the loss. Tail dependence is that propensity of dependence to concentrate in the tails, such that severe losses are more likely to happen together. Micro-correlations are negligible correlations between risks which may be individually harmless, but very dangerous when aggregated. These three phenomena—types of catastrophic and dependent risks—undermine traditional approaches to risk management.[223]

The double whammy effect of the loss of predictive capacity in both environmental impact assessment and cost-benefit analysis will materialize when climate change adaptation decisions confront choices between different adaptation technologies and between anticipatory and reactive adaptation orientations. If both the environmental impacts and the overall costs and benefits are difficult to predict, how useful will these comprehensive front-end methodologies be? For example, should coastal communities build seawalls, and if so how high, or should they rely on enhanced coastal wetlands as a natural capital solution, or should they move inland? It is difficult to say if we cannot reliably predict ultimate sea level rise and its inshore impacts and if the relationship between storm surge protection and area of coastal wetlands is nonlinear and thus not detected or anticipated early in the history of gains or losses.[224]

Recognizing these limitations, legal scholars have begun to question the efficacy of using conventional comprehensive front-end environmental impact assessments and cost-benefit analyses in climate change adaptation decisions.[225] The alternative they propose, however, is not to ditch environmental impact assessment and cost-benefit analysis and go blindly forward, but rather to shift their methodological fundamentals toward a more adaptive “back-end” approach. The critical component of this approach is to scale back (but not abandon) the comprehensive front-end focus, which assumes all effects can be predicted and assessed before the decision, and introduce formal follow-up mechanisms demanding that the decision maker integrate new information into an ongoing decision adjustment process. As Professor Daniel Farber explains,

One of NEPA’s major flaws, which climate assessment needs to avoid at all costs, is the absence of dynamic learning. NEPA does not require agencies to  perform later checks on their EIS predictions, and agencies do not generally do so. . . .

. . . .

Without the check provided by such feedback, overly optimistic predictions can result.[226]

Farber works through this and other lessons learned from the NEPA experience to outline a more dynamic, learning oriented decision process he calls “climate impact assessments.”[227]

Of course, in order to be able to learn from the feedback provided through these climate impact assessments, decision making itself must gravitate to adaptive back-end methodologies. Indeed, well before climate change became a severe policy concern, scientists and lawyers in growing numbers called for greater use of the discipline of “adaptive management” in natural resources policy.[228] The adaptive management strategy traces its origins to C.S. Holling’s critique of front-end predecisional approaches in his influential book from the late 1970s, Adaptive Environmental Assessment and Management.[229] Holling and his colleagues found conventional environmental management methods, particularly the environmental impact assessment process under NEPA, at odds with the emerging model of ecosystems as complex, dynamic systems. Under the dynamic model of ecosystems, they concluded, management policy must put a premium on collecting information, establishing measurements of success, monitoring outcomes, using new information to adjust existing approaches, and possessing a willingness to change.[230] Attempting to predict all the consequences of an action before deciding to go forward and then never looking back, they argued, was at odds with the adaptive management strategy.[231] Adaptive management theory thus rejects NEPA’s premise that all the cumulative effects caused by and affecting an action over time can be reliably predicted at the time the action is designed.[232] Yet effective adaptive management goes beyond that to promote active “learning while doing” in the implementation of decisions over time.[233] Thus, an adaptive management plan must address how to handle new information and contingencies and adjust decisions accordingly.[234]

Adaptive management has evolved well beyond an idea. For example, FWS has portrayed it as an important practical tool that “can assist . . . in developing an adequate operating conservation program and improving its effectiveness.”[235] Indeed, there is broad consensus today among resource managers and academics that adaptive management is the only practical way to implement ecosystem-scale resource management.[236] Not  surprisingly, the trend in climate change scholarship is moving in this direction as well. For prominent examples, Professor Robert Glicksman has broadly outlined how adaptive management would improve federal public lands management policies and implementation in the climate change context,[237] Professor Alejandro Camacho has comprehensively detailed how adaptive management can be applied for climate change adaptation in natural resources management,[238] and Professor Robin Kundis Craig has made adaptive management one of her principles of climate change adaptation policy implementation.[239] Experts from environmental organizations, such as the Environmental Law Institute’s Carl Bruch, concur in the important role adaptive management will play.[240] Fully institutionalizing adaptive management in climate change adaptation policy, however, will require that environmental law relax its front-end gatekeeper grip as well as accommodate new forms of public participation and judicial review.[241] Yet   given the serious limitations of using comprehensive front-end environmental impact assessment and cost-benefit analysis in the climate change adaptation context, this movement seems inevitable for environmental law to remain a viable player in adaptation decision making.

H. Trend Eight: Greater Variety and Flexibility in Regulatory Instruments

If adaptive management will be environmental law’s methodology for climate change adaptation, what will be its instruments for adaptation decision implementation? Here environmental law’s main concern will be managing the effects of adaptation measures on the environment, in particular how adaptation measures increase the scarcity of and competition for critical adaptation resources such as land, timber, minerals, and water. Given the need to shift resources and people around to bolster adaptive capacities, adaptation will be a resource-intensive undertaking no matter what blend of capital is used. For example, urban population growth over the past century has occurred on less than 3% of the earth’s land surface, but that population accounts for 78% of carbon emissions, 60% of residential water use, and 76% of industrial wood use.[242] This kind of disproportionate impact from the aggregates of local and individual behaviors is likely to be experienced in many contexts of climate change adaptation.

As Professor Michael Vandenbergh has explored in a series of
co-authored publications, climate law mitigation policy has moved quickly to lay blame for emissions primarily at the feet of power plants and the automotive industry, with far less attention being given to the more obvious low hanging fruit of emission sources—individuals’ consumption decisions.[243] Putting the onus of mitigation responsibility on corporate actors, while demanding little more of individual consumer choices than is found in reduce, reuse, recycle jingles, may be a necessary expedient to make mitigation politically viable, but it will be much harder for climate change adaptation policy to let individuals and local communities off the hook so easily. There is no easy policy bull’s-eye in the form of concentrated sources of adaptation problems, as power plants and other industrial sources serve for mitigation policy. Adaptation policy, in other words, isn’t going to be about crunching down on some discrete, readily identifiable behavior of environmental law’s traditional industrial targets. Rather, for environmental law, climate change adaptation will be about policing the impacts of how hundreds of millions of people, millions of small businesses and farms, and hundreds of thousands of local communities respond to climate change in a multitude of decision contexts. Something far more dynamic, deep, and norm-shaping than regulating the pants off of big industry will be necessary to reach this level.

So far environmental law has not been very successful in this setting. The classic example is nutrient-laden runoff pollution from farms, which has led to the intractable problem of hypoxia in estuaries around the nation.[244] Traditional command-and-control regulation has proven ineffective in such contexts, where a multitude of actors’ decisions, each individually negligible in effect, aggregate into massive problems over large spatial and temporal scales.[245] It takes little imagination to envision how climate change adaptation could cascade into numerous such cumulative impact problems, necessitating a serious overhaul of instrument choice decisions at all governance scales.

In this regard, a growing number of environmental law scholars have gravitated to what has been dubbed New Governance theory, which turns “away from the familiar model of command-style, fixed-rule regulation by administrative fiat, and toward a new model of collaborative, multi-party, multi-level, adaptive, problem-solving” governance.[246] The central organizing principles of New Governance theory are stakeholder participation, collaboration among interests, diversity of and competition between instruments, decentralization of governance structures, integration of policy domains, flexibility, and an emphasis on noncoerciveness and adaptation.[247] Rigidly relying on fixed, uniform regulatory instruments, such as technology standards and regulatory prescriptions, forecloses adaptation to the kind of evolving, complex problems climate change adaptation will present. Governance institutions will need a broader array of instruments, ranging from “hard” prescriptive mandates to “soft” incentive- and information-based tools, to test for leverage over the more tractable attributes of climate change adaptation problems over time.

For example, as controversial as so-called compensatory mitigation has become under the nation’s core wetlands protection law, section 404 of the CWA,[248] extensive structural infrastructure is likely to be placed in riparian and coastal wetland areas to advance climate change adaptation, and flexible but effective compensatory mitigation instruments will be necessary to manage the environmental impacts of these projects. Sea level rise

would expose a number of large U.S. cities, such as Miami and Boston, to storm damage and, ultimately, inundation of low lying areas. It is unlikely that our society will abandon this level of investment, so engineers are already designing protection schemes. While non-structural “natural” protection measures may help at some locations, structural solutions will be required at others. As has been the case in the Netherlands, such solutions would likely involve extensive dredging and filling of coastal wetlands and alteration of other natural coastal features.[249]

The role of environmental law, if it is to contribute to climate change adaptation, cannot be to impede and obstruct such measures through rigid command-and-control mechanisms and endless litigation over the adequacy of front-end impact assessments. Rather, environmental law will contribute meaningfully if it delivers an adaptive process for “identify[ing] which areas of the coastline can adapt to changing sea levels, where non-structural measures can be employed, where engineered protection must be put in place and how the impacts of such construction can be mitigated.”[250] Identifying and creatively responding to the needs of climate change adaptation is how environmental law can retain a vital role in the policy development process.[251]

I. Trend Nine: Increased Reliance on Multiscalar Governance Networks

As mentioned previously, climate change mitigation policy has become fixated on the federalism question—which level or levels of governance should bear primary responsibility, or even preemptive authority, for instituting nationwide mitigation policy?[252] By contrast, “[t]here has been little if any discussion . . . about the appropriate roles of the states and the federal government in adapting to climate change.”[253] Here again mitigation and adaptation differ substantially in how such fundamentals will be framed and resolved. Mitigation policy has the luxury of asking the federalism question in a relatively narrow context because, regardless of which scale prevails, it is all about the same goal—cutting down greenhouse gas concentrations in the atmosphere. Adaptation, by contrast, is about many different effects, varied across the nation, operating at many different and sometimes competing scales.

In the mitigation context, debate over the federalism question is reminiscent of the well-known “Matching Principle,” which claims that “regulatory authority should go to the political jurisdiction that comes closest to matching the geographic area affected by a particular externality.”[254] Yet it is difficult enough to conceive of which scale best does so for mitigation policy;[255] searching for the right scale in adaptation policy is an even more complex undertaking.

On the one hand, the case for local and regional governance in adaptation policy is strengthened by the variations in climate change impacts across the landscape. Adaptation for Florida, where sea level rise is the primary threat,[256] will not be what it is for Nevada, where even less water is the likely scenario.[257] Even within many states, local impacts will be sufficiently varied as to demand specialized adaptation profiles.[258] It seems unlikely that the federal government could effectively devise a national adaptation strategy that fulfills the needs of every state and local community. By contrast, a molecule of carbon dioxide causes the same impact on the climate system regardless of where it is emitted, hence there is no inherent reason why local and regional autonomy is necessary for mitigation policy to gain traction on causal factors. To be sure, mitigation policy will need to be attentive to regional and local interests just as conventional air pollution control has been, but the case for localism in adaptation policy goes well beyond this political consideration—it is a matter of physical reality. Not surprisingly, therefore, one finds legal scholarship on adaptation often focusing on local and regional scales.[259]

On the other hand, it is not as if the federal government has no stake in climate change adaptation as a matter of national interest. Some aspects of adaptation policy are inherently national in scope, such as immigration policy, a secure national food supply, conservation of marine resources, migratory species, and pandemic disease control. Moreover, how state and local governments respond to adaptation needs will inevitably aggregate socially and economically into nationwide impacts. Water scarcity may pit state against state even more than is the case already, hard-nosed resistance strategies in the face of increasingly severe weather may expose coastal cities to catastrophic risks, and movement of people between states could present new interstate conflicts. Yet outside of the issue of national policy toward adaptation in least developed nations, which has received considerable attention,[260] few legal scholars have proposed comprehensive development of national domestic adaptation policies.[261]

Attempting to resolve this tension to find the just right scale of governance for adaptation would be a futile undertaking—adaptation policy must operate at all scales in an interconnected network of decision making. Although it has not been focused on climate change adaptation policy, the emerging theory of Dynamic Federalism[262] has captured the attention of environmental law scholars for how it could address the multiscalar attributes of other large-scale environmental problems, and it is likely to gain credence in the adaptation context as well. Under Dynamic Federalism, “federal and state governments function as alternative centers of power and any matter is presumptively within the authority of both the federal and the state governments.”[263] The theory is not radical—it does not suggest overhauling the basic federal-state-local structure of governance. Rather, it explicitly calls for overlapping federal and state (and, through states, local) jurisdictions.[264] Scholars of Dynamic Federalism reject the “minimal overlap” model in which there is a “particular allocation of at least primary regulatory authority between the states and the federal government,” replacing it with one “in which multiple levels of government interact in the regulatory process.”[265] As a result, Dynamic Federalism “reject[s] the traditional static optimization model for an adaptive one.”[266] As Professors David Adelman and Kirsten Engle explain, in a Dynamic Federalism strategy,

neither federal nor state governments limit themselves to what many legal scholars have deemed to be their appropriate domains. The federal government continues to regulate local issues, such as remediation of contaminated industrial sites, which have few direct interstate connections and few benefits from federal uniformity. At the same time, state and local governments are not content to confine their attention to issues of local concern, but are developing policies on environmental issues of national or even international scale, such as global climate change. Nor do environmental issues “stay” in the control of any particular level of government, but rather tend to pass back and forth between them like the proverbial football.[267]

Proponents of Dynamic Federalism have primarily focused on its advantages of plurality, dialogue, redundancy, accountability, and economies of scale.[268] The key point relating to the federalism question in climate change adaptation policy is the theory’s overlapping, flexible distribution of authority between federal, state, and local agencies. Namely, while it may appear inefficient to have several agencies at different scales working away on some mutual adaptation policy problem,[269] the built-in redundancy of Dynamic Federalism can provide significant benefits. It gives the overall system of governance more rather than less policy space,[270] which surely will be needed for climate change adaptation. Having multiple agencies working on a problem within overlapping scales can also promote synergy between the agencies and the formation of informal networks.[271]

These properties resonate with the emerging theory of Transgovernmental Networks.[272] Transgovernmental Network theory was forged initially in the context of international law, where nation states, while still the most important actors, have increasingly disaggregated into component institutions sharing roles with nonsovereign bodies.[273] Transgovernmental Network theory emphasizes the nonhierarchical horizontal and vertical networks that are built among the officials of those national and international institutions to exchange information, identify best practices, harmonize approaches, and enforce the overall international policy program.[274] The movement toward Dynamic Federalism and New Governance at domestic, federal and state scales portends the same conditions that are giving rise to such networks in international contexts.[275]

Thus far, however, few commentators have examined the federalism question in the context of climate change adaptation, much less explored how the New Governance, Dynamic Federalism, and Transgovernmental Networks models could be usefully employed in tandem to forge adaptation institutions and instruments.[276] Several commentators deal with the topic tangentially, their focus being mitigation,[277] but only Professor Daniel Farber has offered a focused, albeit preliminary, examination of the federalism question devoted primarily to adaptation.[278] Farber identifies two key issues—financing adaptation[279] and the constitutional limits of federal authority[280]—while acknowledging much remains on the table for consideration. I share his conclusion that “all levels of government will be called upon to play a role in dealing with the impacts of climate change.”[281] How they are configured and coordinated is the looming question for environmental law.

J. Trend Ten: Conciliation

Environmental law is not omnipotent, though one would not gather so from the rhetoric of environmental law on climate change mitigation policy. To be sure, if our nation commits to significant reductions of greenhouse gas emissions, we are unlikely to meet that goal without implementing substantial controls on major emission sources as well as more intensive regulation of smaller sources and individuals, such as controls on buildings for energy efficiency, automobiles for emissions, and farms for land-use and livestock practices. That alone will demand a major deployment of legal resources extending well beyond environmental law. But some strident proponents of emissions regulation have described their agenda as far broader and deeper in scope and intensity. As they put it, “we must launch a thousand arrows immediately,”[282] and the arrows they have in mind are lawsuits under existing federal environmental laws such as the ESA, CWA, and NEPA.

I have contested this strategy as being legally, practically, and politically ill-advised.[283] The ESA, for example, is not structured to provide effective greenhouse gas emissions control. Applying it would require isolating and linking emissions from, say, a power plant in Florida to effects on a distant climate-threatened species—a feat beyond scientific capacity.[284] Saying that climate change globally threatens a species does not establish causal blame on any particular source of emissions; just the opposite, it lays blame on all sources. Using the ESA to sort through that quagmire, in addition to being legally untenable and beyond the capacity of the agencies that implement the statute, would in all likelihood make the statute more of a lightening rod for controversy than it already is.[285]

My fear is that the “thousand arrows” strategy will creep into environmental law’s approach to climate change adaptation as well. If the nation commits to greenhouse gas emission reductions, people, businesses, and governments will expect some regulation. If the nation commits to adaptation—and there seems little choice but to do so aggressively—people, businesses, and governments will expect adaptation. Climate change adaptation thus presents an opportunity for environmental law to break free from its culture of litigation and contestation and build back what that culture has eroded most—trust.[286] Trust generally does not come about through threats to sue.

I am not suggesting that environmental law roll over to every seawall and water diversion project proposed in the name of adaptation. But environmental law has a choice to make and the luxury of making it early in the formulation of climate change adaptation policy—is it going to be about conflict or conciliation?

The other trends I have predicted suggest that it should be about conciliation. Fighting in court to hold on to preservationism defies the biological reality of climate change, whereas using environmental law to facilitate transitional strategies for species and ecosystems holds much promise (Trend One). Following the path of the common law to secure critical natural capital resources through regulation solidifies property rights rather than challenges them (Trend Two). Working with land-use and water law rather than standing alone will put environmental law at the core of adaptation policy rather than on the sidelines (Trend Three). Acknowledging the need to respond to climate justice and catastrophe risk management concerns, the necessary measures for which may not always be environmentally benign, will provide environmental law the chance to influence how these concerns are satisfied (Trends Four and Five). Participating in, rather than against, the complex policy mix that will form around adaptation keeps environmental concerns within the dialogue, not an afterthought (Trend Six). And recalibrating how environmental law uses instruments and institutions to fulfill its objectives will allow it to keep pace with the demand for an adaptive adaptation policy (Trends Seven through Nine). Conflict may be called for at times along the way to fulfilling these trends, but conciliation—the essence of which is overcoming distrust and hostility—must be environmental law’s core norm for participating in climate change adaptation policy.

I fully expect some of the “thousand arrows” crowd to be repulsed by the theme of conciliation. Many of the battles environmental law has fought it had to fight just to get a toehold on development and infrastructure policy,[287] and it is not easy to forget the wounds suffered. But climate change adaptation is not business as usual. It is no exaggeration to think that “[i]f society is faced with massive climate impacts . . . adaptation will become one of society’s highest priorities.”[288] Environmental law must treat it as such.

IV. Conclusion

Climate change adaptation is profoundly about the environment, but it is not profoundly about environmental law. Indeed, environmental law has a debt to repay to the nation’s adaptation deficit. After more than a decade of demanding the nation’s myopic and relentless attention to formulating mitigation policy as a supercharged form of pollution control law, environmental law has discovered adaptation. Yet, while environmental law now recognizes mitigation and adaptation as being joined at the hip, adaptation policy dialogue has thus far not allowed environmental law to stake adaptation as its domain. Rather, environmental law will have to earn its position in the multipolicy mix that will coalesce around the tremendously complex demands of climate change adaptation.

This take on climate change adaptation and environmental law may disappoint or offend those who view environmental law as a mighty weapon in the war against climate change. Recently, for example, the Environmental Law Institute asked a group of environmental law experts what environmental law will look like forty years from now.[289] Some of the prognostications were quite optimistic. One respondent surmised, for example, that “[t]he field of environmental protection will have grown in importance and stature,”[290] and another predicted that “[c]arbon sequestration will prove to be a success.”[291] One respondent believes “[i]n 2049, the practice of environmental law will be on the wane,” but only because “[t]he nation’s most pressing environmental challenges will have taken a dramatic turn for the better following bold actions in Congress, corporate board rooms, and communities across the country.”[292] Similarly, another respondent predicts that “[b]y the midpoint of the 21st century, government-driven environmental regulation will be on a path of increasing irrelevance,” but that will be so only because of the rise of “nongovernmental consensus standards driven by consumer demand and a robust and active market for pollutants and carbon.”[293]

I am not so sanguine. Certainly these predictions cannot be justified as mere extrapolations of current politics and social norms. I would be delighted to be proven wrong (and live to see it), thus making this Article all for naught. But I don’t see that in the cards. Rather, I have to agree with other respondents in conceiving the very real possibility that in 2049 mitigation policy will have come out of the box a watered-down weakling,[294] that “environmental law will be a law of coping with crisis and urgent remediation,”[295] and that we will be focused on “adaptation to a changing climate, evaluating geoengineering options, and addressing disputes over competition for increasingly scarce resources.”[296]

In that scenario, the more likely scenario, my prediction is that environmental law will have trifurcated into three distinct branches. One will retain the conventional focus on pollution control and ecological conservation, but narrowed in the sense that it will have lost dominion over anything having to do with climate change. There will be some environmental issues, however, that go untouched by climate change, such as the level of toxins in groundwater and the regulation of mercury emissions from industrial sources. Environmental law will retain its vitality and relevance for those purposes. The other two branches will deal with climate change mitigation and adaptation, respectively. They are more likely, however, to be identified as the environmental components of mitigation and adaptation law rather than discrete bodies of environmental law.[297] Whatever they are called, however, the environmental interests will share a very large table with a multitude of policy realms, and likely will not be seated at its head.

So I do not see climate change adaptation as necessarily a growth industry for environmental law, one that strengthens its force and expands its scope to match the massive problem the demands of adaptation will present. Rather, if the ten trends I have identified come true, the capacity of environmental law will be seriously tested, and it seems likely what we think of as environmental law will be dramatically transformed and likely constrained in its reach. Ironically, with the growth of climate change mitigation and adaptation legal regimes, both of which will form as amalgams primarily of economic and social policy goals and tradeoffs, it is likely that what lawyers think of fitting under the umbrella of “environmental law” in 50 or 100 years will be close to what environmental law was 40 years ago—mainly a narrow, technical realm of pollution control measures complemented by focused conservation programs. The story of environmental law in the century of climate change adaptation may be about a journey back to the future.

 

 


* Matthews & Hawkins Professor of Property, The Florida State University College of Law, Tallahassee, Florida. B.A., J.D., University of Virginia; LL.M., George Washington University; Ph.D., Southern Illinois University. I am thankful to Lewis & Clark Law School for the opportunity to present the lecture upon which this Article is based as their 2009 Natural Resources Law Institute Distinguished Visitor, and to the talented students and staff at Environmental Law for helping me turn it from a lecture to a written work product. Robin Kundis Craig, David Hodas, Jim Huffman, John Kostyack, David Markell, and John Nagle provided insightful reviews of draft versions and early presentations of this work. I was also tremendously aided by comments and encouragement I received in response to postings of early concepts and later drafts of this work on the environmental law professors listserv, envlawprofs, including those from Tony Arnold, Wil Burns, Cinnamon Carlarne, Barbara Cosens, Deb Donahue, Melinda Harm Benson, Elizabeth Burleson, Joe Feller, Rob Glicksman, Paul Kibel, John Knox, Catherine LaCroix, Andrew Long, Gary Meyers, Linda Malone, Uma Outka, Zyg Plater, Jim Salzman, Rob Verchick, Geoffrey Wandesforde-Smith, Jonathan Wiener, and Doug Yarqon. The FSU College of Law provided support for my research assistants, Jake Cremer and Andrew Hoek, and for my work on the Article in general. All errors and omissions are, of course, my own doing. Please direct questions and comments to jruhl@law.fsu.edu.

[1] Climate change mitigation “refers to options for limiting climate change by, for example, reducing heat-trapping emissions such as carbon dioxide, methane, nitrous oxide, and halocarbons, or removing some of the heat-trapping gases from the atmosphere.” U.S. Global Change Research Program, Global Climate Change Impacts in the United States 10–11 (2009), available at http://downloads.globalchange.gov/usimpacts/pdfs/climate-impacts-report.pdf; see also Intergovernmental Panel on Climate Change, Climate Change 2001: Mitigation app. at 716 (Bert Metz et al. eds., 2001), available at http://www.grida.no/climate/ipcc_tar/ wg3/pdf/app.pdf (mitigation strategies involve “an anthropogenic intervention to reduce the sources or enhance the sinks of greenhouse gases”).

[2] Climate change adaptation “refers to changes made to better respond to present or future climatic and other environmental conditions, thereby reducing harm or taking advantage of opportunity. Effective mitigation measures reduce the need for adaptation.” U.S. Global Change Research Program, supra note 1, at 11; see also Intergovernmental Panel on Climate Change, Climate Change 2007: Impacts, Adaptation and Vulnerability app. at 869 (M.L. Perry et al. eds., 2007) (“Adjustment in natural or human systems in response to actual or expected climatic stimuli or their effects, which moderates harm or exploits beneficial opportunities.”), available at http://www.ipcc.ch/pdf/assessment-report/ar4/wg2/ar4-wg2-app.pdf. Climate change adaptation is also known as “climate proofing,” see Paul Stanton Kibel, Climate Adaptation Policy at the Continental Level: Natural Resources in North America and Europe, 27 Pace Envtl. L. Rev. (forthcoming 2010) (manuscript at 1, on file with author), and as “coping,” see U.S. Envtl. Prot. Agency, Adaptation, http://www.epa.gov/climatechange/effects/ adaptation.html (last visited Apr. 18, 2010).

[3] A. Dan Tarlock, Now, Think Again About Adaptation, 9 Ariz. J. Int’l & Comp. L. 169, 170 (1992).

[4] Id. A representative example of this line of thinking prevailing at the time is found in Richard N. Cooper, Environment and Resource Policies for the World Economy 41–50 (1994). The 1992 United Nations Framework Convention on Climate Change mentioned adaptation but was not regarded at the time as placing any significant emphasis on adaptation strategies as a policy objective, focusing instead on mitigation goals. See E. Lisa F. Schipper, Conceptual History of Adaptation in the UNFCCC Process, in The Earthscan Reader on Adaptation to Climate Change 19, 19 (E. Lisa F. Schipper & Ian Burton eds., 2009) [hereinafter Adaptation to Climate Change]. See generally Daniel Bodansky, The United National Framework Convention on Climate Change: A Commentary, 18 Yale J. Int’l L. 451 (1993) (recounting the decisions made at the convention and its focus on efforts to reduce greenhouse gas emissions).

[5] Tarlock, supra note 3, at 170–71. Tarlock was responding to views about adaptation policy expressed in Paul E. Waggoner, Now, Think of Adaptation, 9 Ariz. J. Int’l & Comp. L. 137 (1992). Tarlock, supra note 3, at 170 n.7.

[6] A premise of this Article is that the climate system is changing at anomalously rapid rates compared to historical trends, and that anthropogenic (human-induced) sources of greenhouse gases (primarily carbon dioxide) are a significant causal factor. I do not endeavor here to convince anyone of this, nor do I go into more detail about the science behind how greenhouse gas emissions and other climate-forcing phenomena contribute to global climate change. The Intergovernmental Panel on Climate Change (IPCC), an international scientific project representing hundreds of scientists, has produced a series of reports, including a comprehensive set in 2007, synthesizing scientific information on climate change and its effects on human and ecological conditions. See, e.g., Intergovernmental Panel on Climate Change, Climate Change 2007: Synthesis Report (2007), available at http://www.ipcc.ch/pdf/ assessment-report/ar4/syr/ar4_syr.pdf. A more recent synthesis of the science and observed trends of climate change is found at United Nations Env’t Programme, Climate Change Science Compendium 2009 (Catherine P. McMullen & Jason Jabbour eds., 2009), available at http://www.unep.org/pdf/ccScienceCompendium2009/cc_ScienceCompendium2009_full_en.pdf. Two highly accessible reports for those less scientifically inclined are available from the National Academy of Sciences. See Nat’l Academy of Scis., Ecological Impacts of Climate Change (2009), available at http://dels.nas.edu/dels/rpt_briefs/ecological_impacts.pdf; Nat’l Academy of Scis., Understanding and Responding to Climate Change (2008), available at http://dels.nas.edu/dels/rpt_briefs/climate_change_2008_final.pdf. I recognize that there remains tremendous uncertainty about how climate systems will in fact change under different emissions scenarios and about the efficacy of different mitigation strategies. It is already evident, for example, that the 2007 IPCC findings overestimated some climate change effects and underestimated others. See Pallava Bagla, No Sign Yet of Himalayan Meltdown, Indian Report Finds, 326 Sci. 924 (2009) (while some glaciers appear to be melting faster than IPCC predictions, glaciers in India may be melting slower); Richard A. Kerr, Amid Worrisome Signs of Warming, ‘Climate Fatigue’ Sets In, 326 Sci. 926 (2009) (discussing examples). The IPCC studies have also been dragged into the “Climategate” public relations fiasco, in which the content of
e-mails and other materials hacked from the accounts of several IPCC scientists at Climatic Research Unit of the University of East Anglia in Norwich, England, has led to questions about the scientists’ personal motives and scientific practices. See Climate Research Unit E-mail Hacking Incident, http://en.wikipedia.org/wiki/Climategate (last visited Apr. 18, 2010) (providing a thorough, up to date, and even-handed account). Nevertheless, I believe the vast weight of evidence points in the direction of anthropogenically caused climate change. My focus is not on causal factors, however, but rather on the ways in which it is likely humans will need or desire to adapt to the harmful and beneficial impacts of climate change at local and regional scales.

[7] For a discussion of the portrayal of climate change mitigation in policy literature as “exceptional” in policy scope and thus demanding measures outside the bounds of conventional air pollution regulation models, see John Copeland Nagle, Climate Exceptionalism, 40 Envtl. L. 53 (2010).

[8] Adaptation to Climate Change, supra note 4.

[9] E. Lisa F. Schipper & Ian Burton, Understanding Adaptation: Origins, Concepts, Practice and Policy, in Adaptation to Climate Change, supra note 4, at 1, 7; see also Waggoner, supra note 5, at 146 (1992) (“The first obstacle to adaptation is reluctance to contemplate it.”). The concern over adaptation crowding out mitigation in political spheres is not unfounded. Mitigation expenditures, for example, impose significant costs in the present, but cannot be expected to deliver results potentially for decades. Investments in mitigation, moreover, have significant positive externalities, as any improvement in climate conditions is shared globally, whereas the benefits of adaptation investments will usually accrue primarily to the community making the expenditures. These features of mitigation compared to adaptation often are argued as leading to an inherent political bias in favor of adaptation investments. See generally Thomas C. Heller, Environmental Realpolitik: Joint Implementation and Climate Change, 3 Ind. J. Global Legal Stud. 295, 309 (1995) (“[T]he usual collective action problems associated with public goods demand that strategies aimed at mitigation create institutions able to coordinate and monitor a cooperative regime. Adaptation, by contrast, is local in character and requires no commitment to common solutions.”). Another source of this bias is what Professor Eric Biber refers to as

the concept of “backlash”—the possibility that there will be a significant push to repeal or roll back regulatory standards in the context of delayed harm problems. Backlash might occur in the context of delayed harms because of the inevitable gap between the initiation of regulatory controls and the beginning of any actual declines in the levels of environmental harm. The risk of backlash is accentuated because of the fragile political support for most regulatory systems that address delayed harms, and because the changes in the environment that delayed harms cause may undermine the political support for continued environmental regulation.

Eric Biber, Climate Change and Backlash, 17 N.Y.U. Envtl. L.J. 1295, 1299 (2009).

[10] As Harvard University oceanographer and IPCC member James J. McCarthy concisely sums up the situation: “What is lacking is resolve.” Earl Lane & Becky Ham, As Climate Change Intensifies, McCarthy Urges Adaptation Focus, 326 Sci. 680, 680 (2009), available at http://www.sciencemag.org/cgi/reprint/326/5953/680.pdf (quoting James J. McCarthy); see also Robert W. Hahn, Climate Policy: Separating Fact from Fantasy, 33 Harv. Envtl. L. Rev. 557, 560 (2009) (“[N]ational leaders appear to lack the political will to achieve global emission reductions in a timely manner.”). Not that we weren’t warned of this way back at the beginning of it all. As Robert M. White, then-president of the National Academy of Engineering, said before the 1990 annual meeting of the American Society of International Law,

It is likely that no matter what policy actions we take, fully arresting the climate warming is just not in the cards. Bringing about international agreement on procedures for mitigating climate warming will be difficult and lengthy. The law of the sea negotiations are a good analogue. They took fifteen years, and the United States has yet to sign the Law of the Sea Treaty. Reasons for the reluctance of the United States relate to the demands of the developing nations for significant technology transfer and economic assistance. These issues, which have so far stymied U.S. adherence to the Law of the Sea Treaty, will be even more complicated and more pervasive in any treaty of the atmosphere that is negotiated.

And so the likelihood is that humanity will have to adapt to some climate changes.

Robert M. White, The Great Climate Debate, 84 Am. Soc’y Int’l L. Proc. 346, 355 (1990).

[11] The efficacy and risks associated with these and other climate engineering fixes are hotly debated in the science and engineering communities. See Gabriele C. Hegerl & Susan Solomon, Risks of Climate Engineering, 325 Sci. 955, 955 (2009); H. Jesse Smith et al., Clearing the Air, 325 Sci. 1641 (2009) (discussing the possibility of successfully implementing carbon capture and sequestration). For discussions of some of the technological proposals and their legal implications, see generally William Daniel Davis, What Does “Green” Mean?: Anthropogenic Climate Change, Geoengineering, and International Environmental Law, 43 Ga. L. Rev. 901, 904–05 (2009); Alexandra Klass, Climate Change and Carbon Sequestration: Assessing a Liability Regime for Long-Term Storage of Carbon Dioxide, 58 Emory L.J. 103, 108 (2008);
Jay Michaelson, Geoengineering: A Climate Change Manhattan Project, 17 Stan. Envtl. L.J. 73, 77–78 (1998); James Edward Peterson, Can Algae Save Civilization? A Look at Technology, Law, and Policy Regarding Iron Fertilization of the Ocean to Counteract the Greenhouse Effect, 6 Colo. J. Int’l Envtl. L. & Pol’y 61 (1995).

[12] I have no expertise and offer no opinion about what levels of reductions in greenhouse gas emissions are necessary globally to arrest climate change, and what share of those reductions the United States ought to bear. Whatever the answer is to both those questions, we are nowhere near to being close to those reductions in either respect; thus, formulation of an adaptation strategy is a necessity.

[13] “[N]o matter how aggressively heat-trapping emissions are reduced, some amount of climate change and resulting impacts will continue due to the effects of gases that have already been released.” U.S. Global Change Research Program, supra note 1, at 11; see also Richard A. Kerr, How Urgent Is Climate Change?, 318 Sci. 1230, 1230 (2007) (“The system has built in time lags. Ice sheets take centuries to melt after a warming. The atmosphere takes decades to be warmed by today’s greenhouse gas emissions.”); V. Ramanathan & Y. Feng, On Avoiding Dangerous Anthropogenic Interference with the Climate System: Formidable Challenges Ahead, 105 Proc. Nat’l Acad. Sci. 14,245, 14,245–46 (2008) (estimating committed warming of 2.4°C even if greenhouse gas concentrations are held to 2005 levels); Susan Solomon et al., Irreversible Climate Change Due to Carbon Dioxide Emissions, 106 Proc. Nat’l Acad. Sci. 1704, 1704 (2009) (estimating a 1000-year committed warming effect).

[14] The Government Accountability Office recently identified this thawing effect:

Thus far, federal government attention and resources have been focused on emissions reduction options, climate science research, and technology investment. In recent years, however, climate change adaptation—adjustments to natural or human systems in response to actual or expected climate change—has begun to receive more attention because the greenhouse gases already in the atmosphere are expected to continue altering the climate system into the future, regardless of efforts to control emissions.

Gov’t Accountability Office, Climate Change Adaptation: Strategic Federal Planning Could Help Government Officials Make More Informed Decisions 2 (2009), available at http://www.gao.gov/new.items/d10113.pdf. Thus, in contrast to the 1992 Convention, see supra note 4, the so-called Copenhagen Accord of 2009 recognizes that “[e]nhanced action and international cooperation on adaptation is urgently required.” Conference of the Parties to the Framework Convention on Climate Change, Copenhagen, Den., Dec. 7–19, 2009, Report  of the Conference of the Parties at Its Fifteenth Session, at 6, U.N. Doc. FCCC/CP/2009/11/Add.1 (Mar. 30, 2010) (advance unedited version of Copenhagen Accord, Dec. 2/CP.15) available at http://unfccc.int/resource/docs/2009/cop15/eng/11a01.pdf#page=4. An alternative way of conceptualizing the thawing of climate change mitigation and adaptation is as components of an overall pollution policy, in this case a global pollution problem. Professor John Nagle has outlined four general responses to pollution: prevention, control, avoidance, and tolerance. See Nagle, supra note 7, at 67–68. Climate change mitigation fits the prevention and control categories of Nagle’s typology, and adaptation encompasses avoidance, in that it reduces harms but not emissions, and tolerance, in that it covers coping with the harms that cannot be avoided. Nagle points out that pollution policy in general has increasingly accommodated avoidance and tolerance strategies, such as measures to impose institutional controls on contaminated sites rather than provide full remediation, and noise abatement ordinances that do not prevent all noisy inconveniences. See id. at 67–68, 86, 88. Climate change adaptation, in this framework, thus seems like pollution policy as usual, albeit on a much more complex scale. Id. at 82–88.

[15] See John Smithers & Barry Smit, Human Adaptation to Climatic Variability and Change, in Adaptation to Climate Change, supra note 4, at 15, 18 (“It is increasingly accepted that the basic decision facing governments and society is not whether to pursue limitation or adaptation strategies, but rather how to combine these approaches . . . . ”).

[16] U.S. Global Change Research Program, supra note 1, at 11.

[17] It is not possible at this time to assemble reliable data and projections required to engage in such an analysis at a level of detail necessary to make meaningful decisions. The obvious tension between mitigation and adaptation is that spending more on one, if the measures are effective, reduces the need for the other, but there is no a priori basis for determining which strategy deserves greater investment globally, regionally, nationally, or locally. See Christopher D. Stone, Beyond Rio: “Insuring” Against Global Warming, 86 Am. J. Int’l L. 445, 474–75 (1992). For some general expositions on these questions reaching a variety of conclusions, see Joseph E. Aldy & William A. Pizer, Issues in Designing U.S. Climate Change Policy (Res. for the Future, Discussion Paper No. 08-20-REV, 2008), available at http://www.rff.org/RFF/Documents/rff-dp-08-20%5B1%5D.pdf; Hahn, supra note 10; Jason Scott Johnston, A Looming Policy Disaster, Reg., Fall 2008, at 38; Jody Freeman & Andrew T. Guzman, Sea Walls Are Not Enough: Climate Change and U.S. Interests (Univ. of Cal. Berkeley Pub. Law & Legal Theory Working Paper Group, Paper No. 1357690, 2009), available at http://ssrn.com/abstract=1357690 (follow “One-Click Download” hyperlink).

[18] See, e.g., Katherine M. Baldwin, NEPA and CEQA: Effective Legal Frameworks for Compelling Consideration of Adaptation to Climate Change, 82 S. Cal. L. Rev. 769, 775 (2009), available at http://weblaw.usc.edu/why/students/orgs/lawreview/documents/BaldwinforWebsite.pdf (“[A]daptation measures must still be employed to combat the impacts of climate change that will inevitably occur, despite the institution of heroic mitigation efforts.”); Alejandro E. Camacho, Adapting Governance to Climate Change: Managing Uncertainty Through a Learning Infrastructure, 59 Emory L.J. 1, 17 (2009) available at http://www.law.emory.edu/fileadmin/ journals/elj/59/59.1/Camacho.pdf (“Unfortunately, legislators and regulators in the United States and elsewhere have only begun to consider the role of adaptation in combating climate change.”); Robin Kundis Craig, “Stationarity Is Dead”—Long Live Transformation: Five Principles for Climate Change Adaptation Law, 34 Harv. Envtl. L. Rev. 9, 14 (2010) (“American environmental law and policy are not keeping up with climate change impacts and the need for adaptation.”); Daniel A. Farber, Adapting to Climate Change: Who Should Pay?, 23 J. Land Use & Envtl. L. 1, 2 (2007) (“Adaptation has been a neglected topic . . . . In my view, this is a mistake.”); Peter Hayes, Resilience as Emergent Behavior, 15 Hastings W.-Nw. J. Envtl. L. & Pol’y 175, 175 (2009) (“[T]he main game is now adaptation which renders mitigation no less urgent, but shifts the political equation in dramatic ways that cannot be ignored any longer.”); Thomas Lovejoy, Mitigation and Adaptation for Ecosystem Protection, 39 Envtl. L. Rep. (Envtl. Law Inst.) 10,072, 10,073 (2009) (“The adaptation part of the climate change agenda is only just beginning to get attention, and needs much more right away.”); Ileana M. Porras, The City and International Law: In Pursuit of Sustainable Development, 36 Fordham Urb. L.J. 537, 593 (2009) (“Most climate change experts and policy-makers recognize that adaptation and mitigation are not mutually exclusive strategies but must, on the contrary be employed in tandem.”). One  contemporary anti-adaptionist holdout in the post-thaw literature is found in Matthew D. Zinn, Adapting to Climate Change: Environmental Law in a Warmer World, 34 Ecology L.Q. 61 (2007). Zinn claims that “climate change presents a choice for public policy: mitigate our contribution to it or attempt to adapt to a changing world.” Id. at 61. Having adopted that questionable either‑or choice as the policy premise, perhaps as a straw man, in an effort to support the “mitigation-preferring policy” choice, id. at 66, Zinn then goes on to explore “how unchecked climate change, in a world of adaptation rather than mitigation, might alter environmental law,” id. at 65. His apocalyptic vision of such a world is, indeed, more than scary, but there are no serious proposals to be found in the prevailing legal or policy literature advocating we adopt what Zinn calls an “adaptation-preferring climate policy—one that wholly or mostly rejects mitigation.” Id. at 63. Any assessment of the evolution of environmental law in such a scenario, or of any field of law for that matter, thus is likely unrepresentative of what can be expected in a dual mitigation-adaptation strategy. That said, Zinn’s work is useful as a strong reminder that mitigation policy must, sooner or later, be effective to avoid having climate change overwhelm our adaptive capacity.

[19] For discussion of the term “adaptation deficit,” see Ian Burton, Climate Change and the Adaptation Deficit, in Adaptation to Climate Change, supra note 4, at 89, 90, 91–92.

[20] The European Union (EU) maintains an active website on climate change adaptation policy with links to adaptation policy white papers and the national adaptation strategies of EU nations. See European Commission, Living with Climate Change in Europe, http://ec.europa.eu/
environment/climat/adaptation/index_en.htm (last visited Apr. 18, 2010). For a recent detailed comparison of the different national strategies, see Rob Swart et al., Partnership for European Environmental Research, Europe Adapts to Climate Change: Comparing National Adaptation Strategies (2009), available at http://www.peer.eu/fileadmin/user_
upload/publications/PEER_Report1.pdf, and for a general overview of the thrust of EU adaptation policy, see Darryn McEvoy et al., Adaptation and Mainstreaming of EU Climate Change Policy: An Actor-Based Perspective (Ctr. for European Policy Studies, CEPS Policy Brief No. 149, 2008), available at http://www.ceps.eu/ceps/download/1424.

[21] Eric J. Barron, Beyond Climate Science, 326 Sci. 643, 643 (2009) (noting the author is the director of the National Center for Atmospheric Research).

[22] In a search conducted April 17, 2010, 1181 files in Westlaw’s Journals and Law Reviews (JLR) database used the terms “climate change” and “mitigat!” (which includes variations such as mitigate, mitigates, mitigation, and mitigative) at least once in the same sentence, with 778 (66%) of those published in 2007 or later. Similarly, 1015 files used the terms “climate change” and “adapt!” at least once in the same sentence, with 655 (65%) published in 2007 or later. In both cases, but particularly with the adaptation references, the coverage in many of the publications is fleeting or even amounts to no more than a citation to a document that contains the search words in its title.

[23] Compare Robert N. Stavins, A Meaningful U.S. Cap-and-Trade System to Address Climate Change, 32 Harv. Envtl. L. Rev. 293 (2008) (advocating a cap-and-trade system), and Jonathan B. Wiener, Property and Prices to Protect the Planet, 19 Duke J. Comp. & Int’l L. 515 (2009) (same), with Reuven S. Avi-Yonah & David M. Uhlmann, Combating Global Climate Change: Why a Carbon Tax Is a Better Response to Global Warming than Cap and Trade, 28 Stan. Envtl. L.J. 3 (2009) (advocating a carbon tax system), Roberta F. Mann, The Case for the Carbon Tax: How to Overcome Politics and Find Our Green Destiny, 39 Envtl. L. Rep. (Envtl. Law Inst.) 10,118 (2009) (same), Michael Waggoner, The House Erred: A Carbon Tax Is Better than Cap and Trade, Tax Notes, Sept. 21, 2009, at 1257 (same), and Michael J. Zimmer, Carbon Tax: Ready for Prime Time?, 8 Sustainable Dev. L. & Pol’y 67 (2008) (same).

[24] Professor Daniel Farber observes there is a “vigorous debate about the appropriate roles of the state and federal governments in reducing greenhouse gases and mitigating climate change.” Daniel A. Farber, Climate Adaptation and Federalism: Mapping the Issues 1 (Univ. of Cal. Berkeley Pub. Law & Legal Theory Working Paper Group, Paper No. 1468621, 2009), available at http://ssrn.com/abstract=1468621 (follow “One-Click Download” hyperlink). Virtually every possible configuration of governance has been advocated. Compare Randall S. Abate, Kyoto or Not, Here We Come: The Promise and Perils of the Piecemeal Approach to Climate Change Regulation in the United States, 15 Cornell J.L. & Pub. Pol’y, 369, 401 (2006) (“State, regional, and local climate change initiatives may be subject to criticism, but in light of the current federal regime, such criticism may be unduly harsh.”), Kirsten H. Engel, Mitigating Global Climate Change in the United States: A Regional Approach, 14 N.Y.U. Envtl. L.J. 54, 58 (2005) (outlining means of implementing a “regional interstate cooperative approach”), Alexandra B. Klass, State Innovation and Preemption: Lessons from State Climate Change Efforts, 41 Loy. L.A. L. Rev. 1653 (2008) (arguing for a more restrictive approach to federal preemption jurisprudence), and Hari M. Osofsky & Janet Koven Levit, The Scale of Networks?: Local Climate Change Coalitions, 8 Chi. J. Int’l L. 409 (2008) (arguing the advantages of a local jurisdiction “bottom-up networking” approach), with Thomas D. Peterson et al., Developing a Comprehensive Approach to Climate Change Policy in the United States that Fully Integrates Levels of Government and Economic Sectors, 26 Va. Envtl. L.J. 227 (2008) (arguing for policy formulation at all levels), and Jonathan B. Wiener, Think Globally, Act Globally: The Limits of Local Climate Policies, 155 U. Pa. L. Rev. 1961, 1962 (2007) (“[S]ubnational state-level action is not the best way to combat global climate change.”). See generally Symposium, Federalism and Climate Change: The Role of the States in a Future Federal Regime, 50 Ariz. L. Rev. 673 (2008). Two points on which there appear to be universal agreement are 1) thus far, climate change mitigation policy has been shaped largely by the states, see Patrick Parenteau, Lead Follow or Get Out of the Way: The States Tackle Climate Change with Little Help from Washington, 40 Conn. L. Rev. 1453 (2008); and 2) federal attention to formulation of a national mitigation policy has intensified in the past year, see Geoffrey Clemm & Mark Griffin Smith, Emerging U.S. Climate Policy: Where We Are and How We Got Here (Colo. College Working Paper Group, Paper No. 2009-04, 2009), available at http://ssrn.com/abstract=1440339 (follow “One-Click Download” hyperlink).

[25] As evidence of the recent merging of the two themes, 465 articles identified in my literature search, supra note 22, mention both mitigation and adaptation in the same paragraph, with 309 (66%) of those published in 2007 or later.

[26] A significant exception comes from the work of water law scholars, who have been examining the implications of climate change adaptation on water law since the early 1990s. Their work is discussed infra Part III.C. Notable examples of more comprehensive contributions to the legal scholarship on climate change adaptation outside of water law include Baldwin, supra note 18 (proposing ways environmental assessment statutes, such as The National Environmental Policy Act of 1969, 42 U.S.C. §§ 4321–4347 (2006), can be used to help formulate adaptation strategies); Camacho, supra note 18 (providing a sweeping overview of the need for adaptation and proposing an “adaptive governance” model for natural resources management agencies); Craig, supra note 18 (outlining general guidelines for formulating adaptation strategies); Farber, supra note 18 (examining allocation of responsibility for effects of climate change and costs of adaptation); Ira Feldman & Joshua H. Kahan, Preparing for the Day After Tomorrow, 8 Sustainable Dev. L. & Pol’y 61 (2007) (providing a broad survey of federal and state adaptation policies); Robert L. Glicksman, Ecosystem Resilience to Disruptions Linked to Global Climate Change: An Adaptive Approach to Federal Land Management, 87 Neb. L. Rev. 833 (2009) (offering principles of adaptive management for public land agencies); and J.B. Ruhl, Climate Change and the Endangered Species Act: Building Bridges to the No-Analog Future, 88 B.U. L. Rev. 1 (2008) (exploring adaptation strategies that can be taken on behalf of endangered species). Interest in the topic among legal scholars is growing fast, however, as evidenced by the University of North Carolina Law School’s recent creation of the Center for Law, Environment, Adaptation, and Resources, the inaugural event of which in 2008 was a conference on climate change adaptation. See Univ. of N. Carolina Sch. of Law, Adapting Legal Regimes in the Face of Climate Change, http://www.law.unc.edu/centers/
clear/workshops/climatechange/default.aspx (last visited Apr. 18, 2010).

[27] For examples, see infra Part III.D.

[28] See Craig, supra note 18, at 18 (“In the United States, much of the legal attention to climate change, whether expressed through litigation, legislation, or scholarship, has focused on mitigation . . . .”).

[29] See generally Robert A. Wyman et al., Significant Climate Issues Likely to Be Raised in the Federal Courts, 39 Envtl. L. Rep. (Envtl. Law Inst.) 10,925, 10,925–43 (2009) (surveying the potential scope of climate litigation but focusing overwhelmingly on issues related to mitigation). A useful depiction of the breadth and depth of climate change litigation can be found at a case-tracking chart that lawyers at the law firm of Arnold & Porter maintain. See Michael B. Gerrard & J. Cullen Howe, Climate Change Litigation in the U.S., available at http://www.climatecasechart.com. The chart divides climate change into three primary categories: statutory claims, common law claims, and public international claims. Id. at 1. Within the statutory claims category are claims to force the government to act, claims to stop government action, and claims to regulate private conduct. Id. My colleague David Markell and I are preparing a more detailed empirical analysis of the cases included in the chart, very few of which, based on our initial review, involve claims that could be described as focused on adaptation strategies.

[30] Ruhl, supra note 26, at 13 n.42.

[31] In their thorough 2007 survey of international and domestic adaptation initiatives, Feldman and Kahan conclude that “states have led the way in climate change adaptation considerations,” while “[f]ederal-level discussions and considerations are preliminary.” Feldman & Kahan, supra note 26, at 66; see also Camacho, supra note 18, at 46–60 (examining the fledgling federal agency initiatives). Confirming this assessment, the Government Accountability Office recently concluded a comprehensive review of federal adaptation policy with the finding that “[w]hile federal agencies are beginning to recognize the need to adapt to climate change, there is a general lack of strategic coordination across agencies, and most efforts to adapt to potential climate change impacts are preliminary.” Gov’t Accountability  Office, supra note 14, at 5. A significant step forward came in President Obama’s October 2009 Executive Order 13,514, which among other things endorsed an interagency Climate Change Adaptation Task Force “already engaged in developing the domestic and international dimensions of a U.S. strategy for adaptation to climate change.” See Exec. Order No. 13,514, 74 Fed. Reg. 52,117, 52,124 (Oct. 8, 2009). To follow the work of the Task Force, see Council on Envtl. Quality, Climate Change Adaptation Task Force, http://www.whitehouse.gov/ administration/eop/ceq/initiaitives/adaptation (last visited Apr. 18, 2010). The Department of the Interior has taken the lead among federal agencies in developing adaptation policy. See generally U.S. Dep’t of the Interior Sec’y Order No. 3,289 (Sept. 14, 2009), available at http://www.interior.gov/climatechange/SecOrder3289.pdf (addressing the impacts of climate change on America’s natural and cultural resources); U.S. Fish & Wildlife Serv., U.S. Dep’t of the Interior, Rising to the Challenge: Strategic Plan for Responding to Accelerating Climate Change 1–2, 10, 12 (2009) (public comment draft), available at http://www.fws.gov/ home/climatechange/strategic_plan.html. The Environmental Protection Agency also has a fact sheet posted on its website providing links to several reports the agency’s Global Change Research Program has produced on climate change impacts and adaptation. See U.S. Envtl. Prot. Agency, supra note 2. Up-to-date information about state mitigation and adaptation strategies can be found through the Seventh Generation Advisors, State Climate Policy Track, http://seventhgenerationadvisors.org/index.php?option=com_content&view=article&id= 79%3Astate-climate-policy-tracker&catid=4&Itemid=19 (last visited Apr. 18, 2010), and through an interactive map tool maintained by the Center for Climate Strategies, U.S. Climate Policy Action, http://www.climatestrategies.us (last visited Apr. 18, 2010). California has established the most detailed state adaptation strategy. See Cal. Natural Res. Agency, California Climate Adaptation Strategy (2009), available at http://www.energy.ca.gov/2009publications/CNRA-1000-2009-027/CNRA-1000-2009-027-F.PDF. Maryland’s Commission on Climate Change also has begun substantial policy analysis and development focused on infrastructure and health issues. See Md. Comm’n on Climate Change, Adaptation and Response Working Groups, http://www.mdclimatechange.us/twg.cfm (last visited Apr. 18, 2010). At the local level, New York City offers an example of a local jurisdiction taking proactive steps toward developing a climate change adaptation policy. See Edna Sussman et al., Climate Change Adaptation: Fostering Progress Through Law and Regulation, 18 N.Y.U. Envtl. L.J. 55 (2010) (discussing various city initiatives).

[32] Many ecologists believe we face a “no-analog” future—one for which we have no experience on which to base projections of ecosystem change and for which models designed to allow active management decisions as climate change takes effect are presently rudimentary and imprecise. See Peter Cox & David Stephenson, A Changing Climate for Prediction, 317 Sci. 207, 207–08 (2007); Matthew C. Fitzpatrick & William W. Hargrove, The Projection of Species Distribution Models and the Problem of Non-Analog Climate, 18 Biodiversity & Conservation 2255, 2255–57 (2009); Douglas Fox, Back to the No-Analog Future?, 316 Sci. 823, 823, 825 (2007); Douglas Fox, When Worlds Collide, Conservation, Jan.–Mar. 2007, at 28, 32–33.

[33] See Burton, supra note 19, at 93 (“What is meant by mitigation is clearly understood. By contrast adaptation means too many unclear things.”).

[34] As discussed at several points later in this Article, climate change is not all about harms—there will be benefits in many forms for many regions of human populations and for many species. Agriculture in the United States, for example, may find benefits to warming temperatures, increased precipitation, and higher carbon dioxide levels. See Olivier Deschênes & Michael Greenstone, The Economic Impacts of Climate Change: Evidence from Agricultural Output and Random Fluctuations in Weather, 97 Am. Econ. Rev. 354, 355–57 (2007). Of particular relief to many is that “the production of high-quality wine grapes is expected to benefit from a warmer climate because of a longer growing season and more favorable growing conditions in the short-term.” Cal. Natural Res. Agency, supra note 31, at 94.

[35] In 1987, the Brundtland Commission, formed by the United Nations General Assembly, endorsed “sustainable development” as “development that meets the needs of the present without compromising the ability of future generations to meet their own needs.” World Comm’n on Env’t & Dev., Our Common Future 43 (1987). Although since then more meat has been added to exactly what that means, this definition remains at the core of sustainable development theory. See John C. Dernbach, Sustainable Development: Now More Than Ever, in Stumbling Toward Sustainability 45, 45 (John C. Dernbach ed., 2002). Within this framework, climate change adaptation can be thought of as an interim strategy for sustainable development during the era of climate change. As I describe climate change adaptation infra, therefore, it is a necessary but short-term predicate for returning to a position of long-term sustainable development planning, in that climate change will be too complex for us to know at any point what is sustainable development within the meaning of the definition. See Robert W. Kates,
et al., Sustainability Science, 292 Sci. 641, 641–42 (2001). Indeed, adaptive measures taken to avoid potentially disastrous effects of climate change, such as massive water transfers to sustain urban populations or erecting vast sea wall complexes to protect coastal populations, may not be compatible with current (or future) conceptions of sustainable development policies and practices. For an insightful discussion of sustainable development in the context of climate change, see David L. Markell, Greening the Economy Sustainably, 1 Wash. & Lee J. Energy, Climate, & Env’t (forthcoming 2010), available at http://ssrn.com/abstract=1376380 (follow “One-Click Download” hyperlink).

[36] As previously mentioned, supra note 22, as of April 17, 2010, 1015 files in Westlaw’s Journals and Law Reviews (JLR) database used the terms “climate change” and “adapt!” at least once in the same sentence. I reviewed all of them to identify those treating the topic of climate change adaptation in law (not limited to environmental law) in some substantial manner. I also culled through entries on the Social Science Research Network and legal blogs in search of similar publications. I reviewed each of the final set of articles to identify the author’s assessment of the development of the law in response to the modes and pressures of climate change adaptation discussed in Part II of this Article.

[37] For evidence, see Intergovernmental Panel on Climate Change, supra note 6, passim; United Nations Env’t Programme, supra note 6, passim; U.S. Global Change Research Program, supra note 1, passim. I offer no specific predictions about the intensity, distribution, or longevity of impacts in any local or regional setting. Indeed, I argue later in this Article that such predictions are beyond current modeling capacity and thus policy decisions should not be made based on the assumption of robust predictive capacity. See infra Part III.G.

[38] See U.S. Global Change Research Program, supra note 1, at 12. For a comprehensive assessment of global impacts and impacts in other countries, see Intergovernmental Panel on Climate Change, supra note 2, passim.

[39] The scientific literature exploring these complex dynamics and exposing our lack of understanding about what lies ahead as temperature rises is legion. See, e.g., Daniel B. Fagre et al., U.S. Climate Change Sci. Program: Thresholds of Change in Ecosystems 5–13 (2008) (public review draft) (U.S. Geological Survey, Synthesis and Assessment Product 4.2, 2009), available at http://downloads.climatescience.gov/sap/sap4-2/sap4-2-final-report-all.pdf (examining numerous positive feedback properties leading to nonlinear thresholds in climate change dynamics); Almut Arneth et al., Clean the Air, Heat the Planet?, 326 Sci. 672, 672–73 (2009) (examining the feedback effects between conventional air pollution control and climate change mitigation, concluding that complex positive and negative feedback links exist, and that, on balance, the evidence and models suggest that “air pollution control will accelerate warming in the coming decades”); Gordon B. Bonan, Forests and Climate Change: Forcings, Feedbacks, and the Climate Benefits of Forests, 320 Sci. 1444, 1444–49 (2008) (explaining the complex and nonlinear forest-climate interactions); I. Eisenman & J.S. Wettlaufer, Nonlinear Threshold Behavior During the Loss of Arctic Sea Ice, 106 Proc. Nat’l Acad. Sci. 28, 28–31 (2009) (describing the nonlinear “tipping points” in the ice‑albedo feedback effect); Jerome Gaillardet & Albert Galy, Himalaya—Carbon Sink or Source?, 320 Sci. 1727, 1727–28 (2008) (explaining the uncertainties of the sinks and sources of the carbon geological cycle); Steven W. Running, Ecosystem Disturbance, Carbon, and Climate, 321  Sci. 652 (2008) (explaining the uncertainties of ecological sinks and sources such as fires and insect epidemics). Dust, pollutant haze, and other aerosols in the atmosphere, for example, deflect incoming solar radiation and thus have a cooling effect. See Richard A. Kerr, Another Global Warming Icon Comes Under Attack, 317 Sci. 28, 28 (2007) (explaining that because “[a]erosols cool the planet by reflecting away sunlight and increasing the reflectivity of the clouds,” climate change models can vary widely depending on assumptions about aerosol levels). Other research focuses on the nonlinear effects these feedback loops have on the pace of change, such as acceleration of ice sheet melting. See Richard A. Kerr, Both of the World’s Ice Sheets May Be Shrinking Faster and Faster, 326 Sci. 217 (2009). As temperatures rise on average, moreover, other positive and negative feedback effects are triggered that could amplify or impede further warming. Melting tundra, for example, releases more greenhouse gases, and researchers have found this effect is far exceeding expected levels because of its feedback properties. See K.M. Walter et al., Methane Bubbling from Siberian Thaw Lakes as a Positive Feedback to Climate Warming, 443 Nature 71 (2006). The effect leads to a positive feedback loop in the following manner: As the greenhouse gases are released, they contribute to warming that melts the tundra faster, which releases more greenhouse gases more rapidly, and so on. See Katey M. Walter et al., Methane Bubbling from Northern Lakes: Present and Future Contributions to the Global Methane Budget,
365 Phil. Transactions Royal Soc’y A 1657, 1671 (2007). This effect is believed to have played a significant role in the last deglaciation. See K.M. Walter et al., Thermokarst Lakes as a Source of Atmospheric CH4 During the Last Deglaciation, 318 Sci. 633, 633 (2007). Ecologists believe these and other transformations in the tundra “could be a one-way ticket,” meaning they are irreversible. See John Bohannon, The Big Thaw Reaches Mongolia’s Pristine North, 319 Sci. 567, 568 (2008). Researchers believe there is a strong potential for similar nonlinear change effects throughout the world’s peatlands. See Nancy B. Dise, Peatland Response to Global Change,
326 Sci. 810 (2009). For other examples of ecological thresholds of irreversibility that climate change is likely to cross, see Advisory Comm. for Envtl. Research & Educ., Nat’l Sci. Found., Transitions and Tipping Points in Complex Environmental Systems 28–31 (2009), available at http://www.nsf.gov/geo/ere/ereweb/ac-ere/nsf6895_ere_report_090809.pdf.

[40] J.X. Mitrovika et al., The Sea-Level Fingerprint of West Antarctic Collapse, 323 Sci. 753, 753 (2009) (suggesting that although generally global sea levels will rise as a result of a collapse of the West Atlantic Ice Sheet, gravitational changes associated with loss of the ice sheet could actually lead to a net sea-level fall in some places).

[41] Intergovernmental Panel on Climate Change, supra note 6, at 8 (explaining likely precipitation increases and decreases in various regions of the world).

[42] Eric Post et al., Ecological Dynamics Across the Arctic Associated with Recent Climate Change, 325 Sci. 1355 (2009).

[43] See, e.g., Gerald C. Nelson et al., Int’l Food Policy Research Inst., Climate Change: Impact on Agriculture and Costs of Adaptation 4 (2009), available at http://www.ifpri.org/ sites/default/files/publications/pr21.pdf.

[44] See U.S. Global Change Research Program, supra note 1, at 11 (“[S]ociety won’t be adapting to a new steady state but rather to a rapidly moving target. Climate will be continually changing, moving at a relatively rapid rate, outside the range to which society has adapted in the past.”).

[45] Although the science and economics of climate change acknowledge this uneven distribution of effects and corresponding costs and benefits, most legal scholarship on climate change emphasizes only the bad effects. For a discussion of the policy complexities raised by the distribution of human costs and benefits associated with climate change, arguing that prevailing domestic mitigation policy proposals do not adequately take the benefits into account, see Johnston, supra note 17, at 38–41. It is probable that some other species will also enjoy benefits from climate change. See, e.g., Post et al., supra note 42, at 1355 (discussing the potential benefits of a warming climate for reindeer). As discussed infra Part III.G, I believe it would be folly to attempt to design mitigation or adaptation policy around any sort of cost‑benefit analysis of the relative harms and benefits of climate change. Nevertheless, where benefits do accrue to humans or other species, I see no point in ignoring them when designing adaptation strategies.

[46] See Rosina M. Bierbaum & Robert B. Zoellick, Development and Climate Change, 326 Sci. 771, 771 (2009) (arguing that “[p]lanning for the future based on the climate of the past will erode development gains, deepen vulnerabilities, and increase inequities” and noting the authors are Dean of the School of Natural Resources and Environment at the University of Michigan and President of the World Bank, respectively).

[47] The International Institute for Environment and Development recently released a review and assessment of global climate change adaptation cost estimates, which not surprisingly are expected to differ from sector to sector and from region to region and to vary widely based on assumptions about timing, intensity, and technique of mitigation and adaptation strategies.
See Martin Parry et al., Assessing the Costs of Adaptation to Climate Change: A Review of the UNFCC and Other Recent Estimates (2009), available at http://www.iied.org/pubs/pdfs/ 11501IIED.pdf. The report concludes that prior estimates of $49–$171 billion global investment per year through 2030 for necessary adaptation initiatives underestimates likely funding needs by a factor of two to three. See id. at 8–14. In another recent study, the World Bank estimates that developing nations face an adaptation price tag of $75–$100 billion annually through 2050. See World Bank, The Costs to Developing Countries of Adapting to Climate Change: New Methods and Estimates: Executive Summary: Consultative Draft (2009), available at http://siteresources.worldbank.org/INTCC/Resources/Executivesummary.pdf. The European Environment Agency has also provided a useful report on the complexity of estimating adaptation costs. See European Env’t Agency, Climate Change: The Cost of Inaction and the Cost of Adaptation § 3, at 22–35 (2007) (reviewing the main methodological issues).

[48] I discuss in Parts II and III several contexts in which adaptation will take the form of physical alteration of land and other resources, thus raising the potential for direct and indirect environmental impacts. Zinn’s evaluation of the extreme “no mitigation” policy scenario dwells significantly on this effect. See Zinn, supra note 18.

[49] U.S. Envtl. Prot. Agency, Glossary of Climate Change Terms, http://www.epa.gov/ climatechange/glossary.html (last visited Apr. 18, 2010) (“Various types of adaptation can be distinguished, including . . . private and public adaptation, and autonomous and planned adaptation.”). Public adaptation is generally associated with planned adaptation, and private adaptation with autonomous adaptation. See John M. Antle, Res. for the Future, Agriculture and the Food System: Adaptation to Climate Change 4 (2009), available at http://www.rff.org/rff/documents/RFF-Rpt-Adaptation-Antle.pdf (“Many . . . adaptations at the farm level and in the broader food system and economy are made without government involvement and are referred to as autonomous adaptation . . . . Other adaptations that involve government intervention are referred to as planned adaptations.”).

[50] See Intergovernmental Panel on Climate Change, supra note 2, at 720.

[51] See id; Camacho, supra note 18, at 15; Feldman & Kahan, supra note 26, at 67; U.S. Envtl. Prot. Agency, supra note 49 (“Various types of adaptation can be distinguished, including anticipatory and reactive adaptation . . . .”).

[52] See Intergovernmental Panel on Climate Change, supra note 2, at 721.

[53] Id.

[54] U.S. Fish & Wildlife Serv., supra note 31, at 11 (emphasis omitted).

[55] Intergovernmental Panel on Climate Change, supra note 2, at 721; see also Camacho, supra note 18, at 16.

[56] See Deschênes & Greenstone, supra note 34, at 354.

[57] Id.

[58] See Burton, supra note 19, at 90.

[59] See id.

[60] See id.

[61] See id.

[62] See id.

[63] Camacho, supra note 18, at 21–22.

[64] Id. at 23.

[65] See id. at 23–24. Camacho’s focus is on procedural adaptation strategies, particularly adaptive management, which are taken up infra Part III.H.

[66] See Intergovernmental Panel on Climate Change, supra note 2, at 727–28.

[67] See U.S. Global Change Research Program, supra note 1, at 152.

[68] See Intergovernmental Panel on Climate Change, supra note 2, at 720 (“Adaptation to climate change takes place through adjustments to reduce vulnerability or enhance resilience in response to observed or expected changes in climate and associated extreme weather events.”); John Handmer & Stephen Dovers, A Typology of Resilience: Rethinking Institutions for Sustainable Development, in Adaptation to Climate Change, supra note 4, at 187, 196; Nathan E. Hultman, Worth More Than Good Advice: Lessons of Hurricane Katrina for Development in a Changing Climate, 11 Geo. Pub. Pol’y Rev. 47, 49–50 (2006).

[69] See Jonathan Ensore & Rachel Berger, Understanding Climate Change Adaptation: Lessons from Community-Based Approaches 13–16 (2009) (describing types of climate change hazards and impacts, and how vulnerabilities can inform adaptation strategies); P. Mick Kelly & W. Neil Adger, Theory and Practice in Assessing Vulnerability to Climate Change and Facilitating Adaptation, in Adaptation to Climate Change, supra note 4, at 161, 167–74.

[70] See Ensore & Berger, supra note 69, at 17–25; Handmer & Dovers, supra note 68, at
187, 190–204.

[71] Blending the two strategies together is often described under the label of “adaptive capacity.” See, e.g., Intergovernmental Panel on Climate Change, supra note 2, at 729; Brian H. Hurd, Challenges of Adapting to a Changing Climate, 26 UCLA J. Envtl. L. & Pol’y 77 (2008).

[72] Fla. Stat. Ann. § 258.397(1) (West 2009).

[73] For an overview of the variety of climate change impacts Florida’s coastal areas are likely to face, see Natural Res. Def. Council, Feeling the Heat in Florida: Global Warming on the Local Level (2001), available at http://www.nrdc.org/globalwarming/florida/florida.pdf. The legal implications of this extensive array of problems are explored in Kelley M. Jancaitis, Florida on the Coast of Climate Change: Responding to Rising Seas, 31 Environs Envtl. L. & Pol’y J. 157 (2008).

[74] The resist mode of adaptation has also been referred to as “hard resilience.” See Marcus Moench, Adapting to Climate Change and the Risks Associated with Other Natural Hazards: Methods for Moving from Concepts to Action, in Adaptation to Climate Change, supra note 4, at 249, 256–72.

[75] In its most basic form, the transform mode of adaptation can be thought of as little more than a coping strategy, an approach many people in least developed nations will have no choice but to adopt. See Susanna Davies, Are Coping Strategies a Cop-Out?, in Adaptation to Climate Change, supra note 4, at 99. As described in the text, however, the transform mode of adaptation could involve concerted measures to adapt to climate change while pursuing economic and social improvement. Id. at 110–11.

[76] These are among the risk minimization measures being recommended to South Carolina. See S.C. Dep’t of Health & Envtl. Control, Adapting to Shoreline Change: A Foundation for Improved Management and Planning in South Carolina 20–52 (draft 2009).

[77] See Intergovernmental Panel on Climate Change, supra note 2, at 736–37.

[78] See Post et al., supra note 42, at 1355–56 (discussing Arctic species).

[79] Summarizing studies by various international aid organizations, the Asian Development Bank estimates 50 million environmentally displaced people by 2010 and over 200 million by 2050. See Asian Dev. Bank, Climate Change and Migration in Asia and the Pacific: Executive Summary 2 (draft 2009).

[80] See Elizabeth Burleson, Climate Change Displacement to Refuge, 25 J. Envtl. L. & Litig. (forthcoming 2010) (manuscript at 1–2), available at http://ssrn.com/abstract=1470486 (follow “One-Click Download” hyperlink); Jane McAdam, Environmental Migration Governance 1 (Univ. of New S. Wales Faculty of Law Research Series, Working Paper No. 1, 2009), available at http://ssrn.com/abstract=1412002 (follow “One-Click Download” hyperlink).

[81] See generally 1 Frank P. Grad, Treatise on Environmental Law § 1.02, at 1-8 to -13 (2009) (describing pollution control and conservation of natural resources as two of the major branches of environmental law).

[82] Endangered Species Act of 1973, 16 U.S.C. §§ 1531–1544 (2006).

[83] Id. § 1532(5)(A).

[84] See Ruhl, supra note 26, at 35–37.

[85] See Intergovernmental Panel on Climate Change, supra note 6, at 57.

[86] See Norman Meyers, Environmental Refuges in a Globally Warmed World, 43 BioScience 752, 752–58 (1993).

[87] See Intergovernmental Panel on Climate Change, IPCC Technical Paper V: Climate Change and Biodiversity 3–4 (2002), available at http://www.ipcc.ch/pdf/technical-papers/ climate-changes-biodiversity-en.pdf.

[88] See id. at 42–43.

[89] See id. at 43.

[90] See id. at 36.

[91] The Environmental Protection Agency has suggested that “important progress has been made in identifying climate change effects on invasive species, but . . . our understanding of effects on specific species and interactions of other stressors needs to be improved.” Effects of Climate Change on Aquatic Invasive Species and Implications for Management and Research, 72 Fed. Reg. 45,046, 45,047 (Aug 10, 2007). Most invasive species introductions are human induced. Peter M. Vitousek et al., Biological Invasions as Global Environmental Change, 84 Am. Scientist 468, 468 (1996).

[92] See discussion infra Part III.F.

[93] See generally Intergovernmental Panel on Climate Change, supra note 6, at 56 (“[A]dditional adaptation measures will be required at regional and local levels to reduce the adverse impacts of projected climate change and variability, regardless of the scale of mitigation undertaken over the next two to three decades.”).

[94] See generally A. Dan Tarlock, The Nonequilibrium Paradigm in Ecology and the Partial Unraveling of Environmental Law, 27 Loy. L.A. L. Rev. 1121 (1994) (discussing the broad objectives of pollution risk remediation and biodiversity protection and the overall paradigm shift in the scientific justification for environmental law).

[95] See Fred P. Bosselman & A. Dan Tarlock, The Influence of Ecological Science on American Law: An Introduction, 69 Chi.-Kent L. Rev. 847 (1994).

[96] See Reed F. Noss, Some Principles of Conservation Biology, as They Apply to Environmental Law, 69 Chi.-Kent L. Rev. 893, 893 (1994) (“Among the new paradigms in ecology, none is more revolutionary than the idea that nature is not delicately balanced in equilibrium, but rather is dynamic, often unpredictable, and perhaps even chaotic.”); see also Bryan Norton, Change, Constancy, and Creativity: The New Ecology and Some Old Problems, 7 Duke Envtl. L. & Pol’y F. 49 (1996); Jonathan Baert Wiener, Law and the New Ecology: Evolution, Categories, and Consequences, 22 Ecology L.Q. 325 (1995).

[97] P.C.D. Milly et al., Stationarity Is Dead: Whither Water Management, 319 Sci. 573, 573 (2008).

[98] Id. (citations omitted).

[99] See Bosselman & Tarlock, supra note 95; Holly Doremus, The Endangered Species Act: Static Law Meets Dynamic World, Wash. U. J.L. & Pol’y (forthcoming 2010), available at http://ssrn.com/abstract=1444164 (follow “One-Click Download” hyperlink); J.B. Ruhl, Thinking of Environmental Law as a Complex Adaptive System: How to Clean Up the Environment by Making a Mess of Environmental Law, 34 Hous. L. Rev. 933 (1997); Tarlock, supra note 94; Jonathan Baert Wiener, Beyond the Balance of Nature, 7 Duke Envtl. L. & Pol’y F. 1 (1996).

[100] 16 U.S.C. §§ 1131–1136 (2006).

[101] National Wildlife Refuge System Administration Act of 1966, 16 U.S.C. §§ 668dd–668ee (2006).

[102] See Craig, supra note 18, at 32–40 (examining “environmental and natural resources law’s most basic paradigms of regulation and management: preservation and restoration”); Doremus, supra note 99 (manuscript at 25–30) (describing conservation policy as relying on “[t]he triumvirate of harvest regulation, restrictions on commerce, and reserve creation”); Annecoos Wiersema, A Train Without Tracks: Rethinking the Place of Law and Goals in Environmental and Natural Resources Law, 38 Envtl. L. 1239, 1249 (2008) (“The traditional belief by lawyers in the balance of nature has led to laws that focused on individual species and setting aside sites of habitat without more.”).

[103] See generally Bosselman & Tarlock, supra note 95 (discussing the evolution of various ecological science paradigms during the last century).

[104] See R. Edward Grumbine, What Is Ecosystem Management?, 8 Conservation Biology 27 (1994) (advocating management of ecosystems for their “native” properties); Bruce Pardy, Ecosystem Management in Question: A Reply to Ruhl, 23 Pace Envtl. L. Rev. 209, 213–14 (2005) (proposing management of ecosystems for “natural” conditions). For arguments against retaining these conceptions of “nature” as the policy driver in environmental law, see J.B. Ruhl, The Myth of What Is Inevitable Under Ecosystem Management: A Response to Pardy, 21 Pace Envtl. L. Rev. 315 (2005); J.B. Ruhl, The Pardy-Ruhl Dialogue on Ecosystem Management, Part IV: Narrowing and Sharpening the Questions, 24 Pace Envtl. L. Rev. 25 (2007); Wiener, supra note 99.

[105] See J.B. Ruhl, Compensatory Mitigation in the Climate Change Era—Business as Usual or Time for a Change?, Nat’l Wetlands Newsl., July–Aug. 2009, at 28, 28 (discussing the premises of habitat mitigation programs and their poor fit with climate change).

[106] See supra note 32 and accompanying text.

[107] See U.S. Global Change Research Program, supra note 1, at 11 (“Climate will be continually changing, moving at a relatively rapid rate, outside the range to which society has adapted in the past. The precise amounts and timing of these changes will not be known with certainty.”).

[108] U.S. Fish & Wildlife Serv., supra note 31, at 7.

[109] Milly et al., supra note 97, at 573.

[110] See Noss, supra note 96, at 893 (“[C]lassical preservationist approaches to conservation, to the extent they attempt to hold nature static, do not reflect realities of nature.”).

[111] The U.S. Fish and Wildlife Service warns that “the original purposes for which some of our National Wildlife Refuges have been established may change or become obsolete.” U.S. Fish & Wildlife Serv., supra note 31, at 9.

[112] This is a major premise of Robin Craig’s development of principles for implementing adaptation policies. See Craig, supra note 18, at 32–40.

[113] U.S. Climate Change Sci. Program & the Subcomm. on Global Change Research, Preliminary Review of Adaptation Options for Climate-Sensitive Ecosystems and   Resources 1–6 (2008), available at http://oaspub.epa.gov/eims/eimscomm.getfile?p_ download_id=474224.

[114] See Kathy J. Wilis & Shonil A. Bhagwat, Biodiversity and Climate Change, 326 Sci. 806, 807 (2009) (discussing the challenges of resources management as we “see species turnover, migrations, and novel communities”).

[115] As Professor Debra Donahue suggested in comments on an early version of the Article, restoration techniques developed under the stationarity premise of natural states will remain useful as a means of reducing nonclimate stresses within ecological contexts. The U.S. Fish & Wildlife Service has made this a priority of its climate change adaptation strategy. See U.S. Fish & Wildlife Serv., supra note 31, at 22. Similarly, grazing law expert Joe Feller suggests that drier conditions in the West will make it necessary to reduce livestock grazing on federal public lands in order to put them in a position to be useful for other adaptation uses. See Joseph Feller, Climate Change and Livestock Grazing on Western Rangelands, in Climate Change: A Reader (William Rodgers et al. eds.) (forthcoming 2010) (manuscript at 14–17, on file with author).

[116] See Ruhl, supra note 26, at 35–37 (discussing this use of the critical habitat program of the ESA).

[117] Even further, serious consideration will need to be given to more active measures to help species adapt, such as through “assisted migration,” which involves the intentional relocation of organisms to an area in which their species has never existed. See Alejandro E. Camacho, Assisted Migration: Redefining Nature and Natural Resources Law Under Climate Change, 27 Yale J. on Reg. (forthcoming 2010), available at http://ssrn.com/abstract=1495370 (follow “One-Click Download” hyperlink), (arguing that “contemporary natural resource law’s fidelity to historic baselines, protecting preexisting biota, and shielding nature from human activity is increasingly untenable in light of climate change”).

[118] See Elisa Barbour & Lara Kueppers, Pub. Policy Inst. of Cal., Conservation and Management of Ecological Systems in a Changing California 16 (2008), available at http://www.ppic.org/content/pubs/report/R_1108EBR.pdf (“[M]aintaining an ecosystem that is resistant or resilient to fire and invasive species might supplant a goal of maintaining a particular species list in a given site.”). For legal commentary on this topic, see Craig, supra note 18, at 46–48 (recognizing the need for resilience-based management); Doremus, supra note 99 (manuscript at 48) (arguing that effective ecosystem resilience management cannot be based on biodiversity metrics); Glicksman, supra note 26, at 881–84 (emphasizing the need for ecosystem level management for resilience); James L. Olmsted, Climate Surfing: A Conceptual Guide to Drafting Conservation Agreements in the Age of Global Warming, 23 St. John’s J. Legal Comment. 765 passim (2008) (emphasizing biodiversity management); and Noss, supra note 96, at 904 (“Maintaining viable ecosystems is usually more efficient, economical, and effective than a species-by-species approach.” (emphasis omitted)). European scholars have suggested the same for European Union policy. See An Cliquet et al., Adaptation to Climate Change: Legal Challenges for Protected Areas, 5 Utrecht L. Rev. 158, 174–75 (2009), available at http://ssrn.com/abstract=1440152 (follow “One-Click Download” hyperlink).

[119] See Ahmed Djoghlaf, Climate Change and Biodiversity in Polar Regions, 8 Sustainable Dev. L. & Pol’y 14, 16 (2008) (“[C]onservation and sustainable use of biodiversity is an essential element of any strategy to adapt to climate change.”); see also Jeffrey D. Sachs et al., Biodiversity Conservation and the Millennium Development Goals, 325 Sci. 1502 (2009) (discussing the importance of biodiversity management to human well-being); W.J. Sutherland et al., One Hundred Questions of Importance to the Conservation of Global Biological Diversity, 23 Conservation Biology 557, 561 (2009) (discussing the important research questions for managing on a biodiversity basis in the climate change era); Matt Walpole et al., Tracking Progress Toward the 2010 Biodiversity Target and Beyond, 325 Sci. 1503 (2009) (discussing biodiversity management indicators).

[120] See Ass’n of British Insurers, Assessing the Risks of Climate Change: Financial Implications 3, 5 (2009), available at http://www.abi.org.uk/Media/Releases/2009/11/45222.pdf [hereinafter ABI, Financial Implications] (examining the flow-through impact on insurance prices and the impact on insurance capital requirements); Ass’n of British Insurers, The Financial Risks of Climate Change 5–8 (2009), available at http://www.metoffice.gov.uk/ insurance/abi-report.html [hereinafter ABI, Financial Risks] (estimating necessary insurance premium increases and insurance losses due to increased flood and wind damage); The Geneva Ass’n, The Insurance Industry and Climate Change – Contribution to the Global Debate 56–57 (2009), available at http://www.genevaassociation.org/PDF/Geneva_Reports/Geneva_ report%5B2%5D.pdf (identifying as key adaptations for the insurance industry storms and flooding, agricultural issues, water availability, heat issues, and health issues); Tim Lenton et al., Major Tipping Points in the Earth’s Climate System and Consequences for the Insurance Sector 4 (2009) (providing a report commissioned by Allianz, a global financial company); Carolyn Kousky & Roger M. Cooke, Climate Change and Risk Management: Challenges for Insurance, Adaptation, and Loss Estimation 6 (Res. for the Future, Discussion Paper No. 09-03-REV, 2009), available at http://www.rff.org/RFF/Documents/RFF-DP-09-03.pdf. Legal commentators have begun to explore the complex issues climate change will present for the insurance and financial industries. See Richenda Connell et al., Evaluating the Private Sector Perspective on the Financial Risks of Climate Change, 15 Hastings W.-N.W. J. Envtl. L. & Pol’y 133 (2009); J. Wylie Donald & Craig W. Davis, Carbon Dioxide: Harmless, Ubiquitous and Certainly Not a “Pollutant” Under a Liability Policy’s Absolute Pollution Exclusion, 39 Seton Hall L. Rev. 107 (2009); Michael G. Faure, Commentary, Insurability of Damage Caused by Climate Change, 155 U. Pa. L. Rev. 1875 (2007); Sean B. Hecht, Climate Change and the Transformation of Risk: Insurance Matters, 55 UCLA L. Rev. 1559 (2008); Howard C. Kunreuther & Erwann O. Michel‑Kerjan, Climate Change, Insurability of Large-Scale Disasters, and the Emerging Liability Challenge, 155 U. Pa. L. Rev. 1795 (2007); Evan Mills, The Role of U.S. Insurance Regulators in Responding to Climate Change, 26 UCLA J. Envtl. L. & Pol’y 129 (2008); Alberto Monti, Climate Change and Weather-Related Disasters: What Role for Insurance, Reinsurance and Financial Sectors?, 15 Hastings W.-N.W. J. Envtl. L. & Pol’y 151 (2009); Christina Ross et al., Limiting Liability in the Greenhouse: Insurance Risk-Management Strategies in the Context of Global Climate Change, 43 Stan. J. Int’l L. 251 (2007).

[121] See, e.g., ABI, Financial Implications, supra note 120, at 3, 5 (examining the flow-through impact on insurance prices and the impact on insurance capital requirements); ABI, Financial Risks, supra note 120, at 5–8 (estimating necessary insurance premium increases and insurance losses due to increased flood and wind damage); The Geneva Ass’n, supra note 120, at 56–57 (identifying as key adaptations for the insurance industry storms and flooding, agricultural issues, water availability, heat issues, and health issues).

[122] Suraje Dessai et al., Defining and Experiencing Dangerous Climate Change, 64 Climate Change 11, 14–15 (2004); Ross et al., supra note 120.

[123] See Feldman & Kahan, supra note 26 (providing a broad survey of federal and state adaptation policies); Alice Kaswan, The Domestic Response to Global Climate Change: What Role for Federal, State, and Litigation Initiatives?, 42 U.S.F. L. Rev. 39 (2007) (summarizing existing and developing statutory and regulatory responses to climate change).

[124] For the related question of who should bear the costs of implementing adaptation measures, see Farber, supra note 18; Daniel A. Farber, Apportioning Climate Change Costs, 26 UCLA J. Envtl. L. & Pol’y 21 (2008).

[125] See generally Antonio Mascarenhas, Oceanographic Validity of Buffer Zones for the East Coast of India: A Hydrometeorological Perspective, 86 Current Sci. 399, 399, 404 (2004) (discussing “the protective value of coastal landforms” and acknowledging the need for “mandatory buffer zones”).

[126] See, e.g., Lucas v. S.C. Coastal Council, 505 U.S. 1003, 1007–08 (1992) (examining public regulation of coastal property development).

[127] Mascarenhas, supra note 125, at 404.

[128] Lucas, 505 U.S. at 1030.

[129] Id. at 1031.

[130] See, e.g., Michael C. Blumm & Lucas Ritchie, Lucas’s Unlikely Legacy: The Rise of Background Principles as Categorical Takings Defenses, 29 Harv. Envtl. L. Rev. 321 (2005) (surveying different bases for moving the common law under this principle); J.B. Ruhl, The “Background Principles” of Natural Capital and Ecosystem Services—Did Lucas Open Pandora’s Box?, 22 J. Land Use & Envtl. L. 525 (2007) (exploring the new knowledge of ecosystem services as a basis for influencing common law doctrine).

[131] See Gretchen C. Daily, Introduction: What Are Ecosystem Services?, in Nature’s Services: Societal Dependence on Natural Ecosystems 1, 7–8 (Gretchen C. Daily ed., 1997). Most recently, the United Nations’s Millennium Ecosystem Assessment published a global survey of the production and delivery of ecosystem services. See Walter V. Reid et al., Millennium Ecosystem Assessment, Ecosystems And Human Well-Being: Synthesis (2005), available at http://www.millenniumassessment.org/documents/document.356.aspx.pdf. For a more detailed history, including coverage of the emergence of the ecosystem services concept in legal literature, see James Salzman, A Field of Green? The Past and Future of Ecosystem Services, 21 J. Land Use & Envtl. L. 133 (2006).

[132] See J.B. Ruhl, Making Nuisance Ecological, 58 Case W. Res. L. Rev. 753 (2008); J.B. Ruhl & James Salzman, Ecosystem Services and the Public Trust Doctrine: Working Change from Within, 15 S.E. Envtl. L.J. 223, 230–37 (2007).

[133] Other commentators have identified the potential for the needs of climate change adaptation to profoundly influence the development of common law property rights. See, e.g., Robin Kundis Craig, Adapting to Climate Change: The Potential Role of State Common Law Public Trust Doctrines, 34 Vt. L. Rev. (forthcoming 2010), available at http://ssrn.com/ abstract=1431663 (follow “One-Click Download” hyperlink) [hereinafter Craig, Adapting to Climate Change]; Craig, supra note 18, at 61–63; Michael Hiatt, Come Hell or High Water: Reexamining the Takings Clause in a Climate Changed Future, 18 Duke Envtl. L. & Pol’y F. 371 (2008); Carol M. Rose, Big Roads, Big Rights: Varieties of Public Infrastructure and Their Impact on Environmental Resources, 50 Ariz. L. Rev. 409 (2008); Ruhl, supra note 132, at 776 n.83; Ruhl & Salzman, supra note 132, at 230–31; Gregory Sergienko, Property Law and Climate Change, Nat. Resources & Env’t, Winter 2008, at 25. For a similar theme involving water rights, see infra Part III.C.

[134] See Sara C. Bronin, Modern Lights, 80 U. Colo. L. Rev. 881, 884–85 (2009) (proposing a solar energy rights regime similar to water law); Sara C. Bronin, Solar Rights, 89 B.U. L. Rev. 1217 (2009) (exploring likely rights conflicts under existing solar energy access rights).

[135] See Troy Rule, A Downwind View of the Cathedral: Using Rule Four to Allocate Wind Rights, 46 San Diego L. Rev. 207 (2009) (examining property rights disputes emerging due to competition for wind energy).

[136] See Alexandra Klass & Elizabeth J. Wilson, Climate Change, Carbon Sequestration, and Property Rights, 2010 U. Ill. L. Rev. (forthcoming), available at http://ssrn.com/abstract=1371755 (follow “One-Click Download” hyperlink).

[137] For example, although the beach renourishment project at issue in Stop the Beach Renourishment, Inc. v. Florida Department of Environmental Protection, No. 08-1151 (U.S. Dec. 2, 2009), was not designed as a climate change adaptation measure, the case is representative of the property disputes likely to arise as communities take measures to enhance coastal technological and natural resources to defend against storm surge. See Transcript of Oral Argument at 3, Stop the Beach Renourishment, No. 08-1151 (on file with author). The case arises out of the Florida Supreme Court’s decision in Walton County v. Stop the Beach Renourishment, Inc., 998 So. 2d 1102 (Fla. 2008), cert. granted, 129 S. Ct. 2792 (2009) (No. 08-1151), in which the court found a state beach renourishment statute that fixed property boundaries for littoral property owners did not constitute a taking of property without just compensation. Id. at 1121. For an in-depth discussion of the case, see Donna R. Christie, Of Beaches, Boundaries and SOBs, 25 J. Land Use & Envtl. L. (forthcoming 2009), available at http://ssrn.com/abstract=1483348 (follow “One‑Click Download” hyperlink).

[138] Although several such pieces of litigation have overcome motions to dismiss on a variety of grounds, none has advanced to the merits of the public nuisance, private nuisance, trespass, negligence, unjust enrichment, fraudulent misrepresentation, or civil conspiracy claims. See Comer v. Murphy Oil USA, 585 F.3d 855, 860 (5th Cir. 2009) (reversing lower court’s granting of motion to dismiss), reh’g granted en banc, No. 07-60756, 2010 WL 685796 (5th Cir. Feb. 26, 2010); Connecticut v. Am. Elec. Power Co., 582 F.3d 309, 315 (2d Cir. 2009) (reversing lower court’s granting of motion to dismiss); Native Vill. of Kivalina v. Exxon Mobil Corp., No. C 08-1138 SBA, 2009 WL 3326113, at *1 (N.D. Cal. Sept. 30, 2009) (granting motion to dismiss). For legal commentary on the use of common law principles in mitigation litigation, see Daniel Farber, Basic Compensation for Victims of Climate Change, 38 Envtl. L. Rep. (Envtl. Law Inst.) 10,521 (2008); Daniel A. Farber, Tort Law in the Era of Climate Change, Katrina, and 9/11: Exploring Liability for Extraordinary Risks, 43 Val. U. L. Rev. 1075 (2009); David A. Grossman, Warming Up to a Not-So-Radical Idea: Tort-Based Climate Change Litigation, 28 Colum. J. Envtl. L. 1 (2003); Hilary Sigman, Legal Liability as Climate Change Policy, 155 U. Pa. L. Rev. 1953 (2007).

[139] See Grossman, supra note 138, at 53.

[140] See Ruhl & Salzman, supra note 132, at 225.

[141] Lucas, 505 U.S. 1003, 1029–30 (1992).

[142] See James L. Huffman, Beware of Greens in Praise of the Common Law, 58 Case W. Res. L. Rev. 813, 813 (2008) (describing the use of the common law to protect natural capital “as a Trojan horse—a gift to free marketeers and property rights supporters that is not what it appears to be”).

[143] Tarlock’s work during the 1990s forged the discipline of climate change adaptation law by focusing on international and domestic legal regimes for allocation of water resources. See A. Dan Tarlock, How Well Can International Water Allocation Regimes Adapt to Global Climate Change?, 15 J. Land Use & Envtl. L. 423 (2000); Tarlock, supra note 3; A. Dan Tarlock, Western Water Law, Global Warming, and Growth Limitations, 24 Loy. L.A. L. Rev. 979 (1991).

[144] This includes, for example, proposals to adopt a Netherlands-style land-use system for coastal areas. See Damien Leonard, Raising the Levee: Dutch Land Use Law as a Model for U.S. Adaptation to Climate Change, 21 Geo. Int’l Envtl. L. Rev. 543 (2009).

[145] Craig Anthony (Tony) Arnold, Is Wet Growth Smarter Than Smart Growth?: The Fragmentation and Integration of Land Use and Water, 35 Envtl. L. Rep. (Envtl. Law Inst.) 10,152, 10,154 (2005); see also Christine A. Klein et al., Modernizing Water Law: The Example of Florida, 61 Fla. L. Rev. 403, 448–57 (2009) (“[In planning for the future, a critical challenge for states] lies in providing appropriate links between land use planning (typically at the local level) and water resource planning (typically at the state level).”).

[146] See, e.g., Jody Freeman & Daniel A. Farber, Modular Environmental Regulation, 54 Duke L.J. 795 (2005) (discussing the Bay-Delta watershed in northern California); Holly Doremus & A. Dan Tarlock, Fish, Farms, and the Clash of Cultures in the Klamath Basin, 30 Ecology L.Q. 279, 306–16 (2003); Wiersema, supra note 102, at 1265–82 (discussing the Chesapeake Bay).

[147] See Cal. Natural Res. Agency, supra note 31, at 79–92; U.S. Global Change Research Program, supra note 1, at 41–52.

[148] Milly et al., supra note 97, at 573 (citations omitted).

[149] See Robin Kundis Craig, Water Supply, Desalination, Climate Change, and Energy Policy, 23 Pac. McGeorge Global Bus. & Dev. L.J. (forthcoming 2010), available at http://ssrn.com/abstract=1418675 (follow “One-Click Download” hyperlink) (desalination); Noah D. Hall & Bret B. Stuntz, Climate Change and Great Lakes Water Resources: Avoiding Future Conflicts with Conservation, 31 Hamline L. Rev. 639 (2008) (conservation); Klein et al., supra note 145, at 457–67 (examining the demands for reform of water transfer law).

[150] A growing number of water law scholars have argued that climate change adaptation will demand fundamental reforms of domestic water-allocation law and water property rights. See Adell Amos, Freshwater Conservation in the Context of Energy and Climate Policy: Assessing Progress and Identifying Challenges in Oregon and the Western United States, 12 U. Denv. Water L. Rev. 1 (2008); John T. Andrews et al., California Water Management: Subject to Change, 14 Hastings W.-Nw. J. Envtl. L. & Pol’y 1463 (2008); Robin Kundis Craig, Adapting Water Law to Public Necessity: Reframing Climate Change as Emergency Response and Preparedness, 11 Vt. J. Envtl. L. (forthcoming 2010), available at http://ssrn.com/abstract=1528963 (follow “One-Click Download” hyperlink); Joseph W. Dellapenna, Adapting Riparian Rights to the Twenty-First Century, 106 W. Va. L. Rev. 539 (2004); Joseph W. Dellapenna, Climate Disruption, the Washington Consensus, and Water Law Reform, 81 Temp. L. Rev. 383 (2008); Joseph W. Dellapenna, Developing Suitable Water Allocation Law for Pennsylvania, 17 Vill. Envtl. L.J. 1 (2006); Holly Doremus & Michael Hanemann, The Challenges of Dynamic Water Management in the American West, 26 UCLA J. Envtl. L. & Pol’y 55 (2007); Brian E. Gray, Global Climate Change: Water Supply Risks and Water Management Opportunities, 14 Hastings W.-Nw. J. Envtl. L. & Pol’y 1453 (2008); Noah D. Hall et al., Climate Change and Freshwater Resources, Nat. Resources & Env’t, Winter 2008, at 30; Kathleen A. Miller, Climate Change and Water in the West: Complexities, Uncertainties and Strategies for Adaptation, 27 J. Land Resources & Envtl. L. 87 (2007); A. Dan Tarlock, Water Law Reform in West Virginia: The Broader Context, 106 W. Va. L. Rev. 495 (2004). Some of these changes in domestic law will be driven by adaptation pressures put on cross-border water regimes the United States has established with and Mexico and Canada. See Kibel, supra note 2, passim.

[151] See Robert W. Adler, Climate Change and the Hegemony of State Water Law, 29 Stan. Envtl. L.J. 1, 40–45 (2010) (examining the potential interstate and interregional conflicts); Klein et al., supra note 145, at 448 (“Surprisingly fierce conflicts have developed as rapidly urbanizing regions of the states seek to capture water resources of wetter, slower-growing areas.”). Water law experts believe these interjurisdictional conflicts will put stress on settled patterns of water law federalism, most likely leading to an increased federal role supplanting traditional state dominance. See Adler, supra, at 49–60; Robin Kundis Craig, Adapting Water Federalism to Climate Change Impacts: Energy Policy, Food Security, and the Allocation of Water Resources, 5 Envtl. & Energy L. & Pol’y J. (forthcoming 2011), available at http://ssrn.com/abstract=1555944 (follow “One Click Download” hyperlink).

[152] See Nat’l Drought Mitigation Ctr., What Is Drought? Drought and Climate Change, http://drought.unl.edu/whatis/cchange.htm (last visited Apr. 18, 2010) (pointing out that some regions might experience beneficial gains in agricultural production resulting from adequate precipitation).

[153] See Jonathan H. Adler, Water Marketing as an Adaptive Response to the Threat of Climate Change, 31 Hamline L. Rev. 729 (2008) (discussing greater use of water markets to resolve allocation questions); Craig, Adapting to Climate Change, supra note 133 (exploring how public trust doctrines can be used to adapt water rights law for climate change).

[154] Arnold, supra note 145, at 10,152.

[155] See Catherine J. LaCroix, Land Use and Climate Change: Is It Time for a National Land Use Policy?, 35 Ecology L. Currents 124 (2008).

[156] See Leonard, supra note 144.

[157] See Jessica A. Bacher, Yielding to the Rising Sea: The Land Use Challenge, 38 Real Est. L.J. 96 (2009).

[158] As with water allocation law, a growing number of land-use scholars argue for fundamental reform of land-use law to respond to the needs of climate change adaptation. See John R. Nolon & Jessica A. Bacher, Climate Change, Zoning and Transportation Policy,
36 Real Est. L.J. 211, 213 (2007); Porras, supra note 18, at 595; Heike Schroeder & Harriet Bulkeley, Global Cities and the Governance of Climate Change: What Is the Rule of Law in Cities?, 36 Fordham Urb. L.J. 313, 321 (2009).

[159] See World Bank, supra note 47, passim.

[160] See Simon Caney, Cosmopolitan Justice, Rights and Global Climate Change, 19 Canadian J.L. & Jurisprudence 255 (2006); John H. Knox, Climate Change and Human Rights Law, 50 Va. J. Int’l L. 163, 165 (2009); John H. Knox, Linking Human Rights and Climate Change at the United Nations, 33 Harv. Envtl. L. Rev. 477 (2009); Siobhén McInerney-Lankford, Climate Change and Human Rights: An Introduction to Legal Issues, 33 Harv. Envtl. L. Rev. 431 (2009); Stephen Tully, The Contribution of Human Rights as an Additional Perspective on Climate Change Impacts Within the Pacific, 5 N.Z. J. Pub. & Int’l L. 169 (2007).

[161] Sumudu Atapattu, Global Climate Change: Can Human Rights (and Human Beings) Survive This Onslaught?, 20 Colo. J. Int’l Envtl. L. & Pol’y 35, 66 (2008); Edward Cameron, The Human Dimension of Global Climate Change, 15 Hastings W.-Nw. J. Envtl. L. & Pol’y 1, 14 (2009); Daniel H. Cole, Climate Change, Adaptation, and Development, 26 UCLA J. Envtl. L. & Pol’y 1, 3 (2008); Mark A. Drumbl, Poverty, Wealth, and Obligation in International Environmental Law, 76 Tul. L. Rev. 843 (2002); Daniel A. Farber, The Case for Climate Compensation: Justice for Climate Change Victims in a Complex World, 2008 Utah L. Rev. 377, 413 (2008); Paul G. Harris, The European Union and Environmental Change: Sharing the Burdens of Global Warming, 17 Colo. J. Int’l Envtl. L. & Pol’y 309, 326 (2006); Paul L. Joffe, Conscience and Interest: Law, Rights, and Politics in the Struggle to Confront Climate Change and the New Poverty, 6 Rutgers J.L. & Pub. Pol’y 269, 270 (2009); Marc Limon, Human Rights and Climate Change: Constructing a Case for Political Action, 33 Harv. Envtl. L. Rev. 439, 455 (2009); Ann Prouty, The Clean Development Mechanism and Its Implications for Climate Justice, 32 Colum. J. Envtl. L. 513, 539 (2009); Edith Brown Weiss, Climate Change, Intergenerational Equity and International Law, 9 Vt. J. Envtl. L. 615, 627 (2008).

[162] See William C. Burns, Global Warming—The United Nations Framework Convention on Climate Change and the Future of Small Island States, 6 Dick. J. Envtl. L. & Pol’y 147, 175 (1997); John Crump, Snow, Sand, Ice, and Sun: Climate Change and Equity in the Arctic and Small Island Developing States, 8 Sustainable Dev. L. & Pol’y 8 (2008); Alexander Gillespie, Small Island States in the Face of Climatic Change: The End of the Line in International Environmental Responsibility, 22 UCLA J. Envtl. L. & Pol’y 107, 121–22 (2004); Susan Glazebrook, Human Rights and the Environment, 40 Victoria U. Wellington L. Rev. 293, 342 (2009).

[163] See Randall S. Abate, Climate Change, the United States, and the Impacts of Arctic Melting: A Case Study in the Need for Enforceable International Environmental Human Rights, 43A Stan. J. Int’l L. 3, 71–72 (2007); James D. Ford, Supporting Adaptation: A Priority for Action on Climate Change for Canadian Inuit, 8 Sustainable Dev. L. & Pol’y 25 (2008); Donald M. Goldberg & Tracy Badua, Do People Have Standing? Indigenous Peoples, Global Warming, and Human Rights, 11 Barry L. Rev. 59, 61 (2008); Jesse Hohmann, Igloo as Icon: A Human Rights Approach to Climate Change for the Inuit?, 18 Transnat’l L. & Contemp. Probs. 295 (2009); Margueritte E. Middaugh, Linking Global Warming to Inuit Human Rights, 8 San Diego Int’l L.J. 179, 207 (2006); E. Rania Rampersad, Indigenous Adaptation to Climate Change: Preserving Sustainable Relationships Through an Environmental Stewardship Claim & Trust Fund Remedy, 21 Geo. Int’l Envtl. L. Rev. 591, 613 (2009); Rebecca Tsosie, Indigenous People and Environmental Justice: The Impact of Climate Change, 78 U. Colo. L. Rev. 1625, 1676 (2007); Erika Zimmerman, Comment, Valuing Traditional Ecological Knowledge: Incorporating the Experiences of Indigenous People into Global Climate Change Policies, 13 N.Y.U. Envtl. L.J. 803, 846 (2005).

[164] See Ben Saul & Jane McAdam, An Insecure Climate for Human Security? Climate-Induced Displacement and International Law, in Human Security and Non-Citizens (Alice Edwards & Carla Ferstman eds., forthcoming 2010), available at http://ssrn.com/abstract=1292605 (follow “One-Click Download” hyperlink); McAdam, supra note 80 (manuscript at 27); Kara K. Moberg, Comment, Extending Refugee Definitions to Cover Environmentally Displaced Persons Displaces Necessary Protection, 94 Iowa L. Rev. 1107, 1113 (2009).

[165] For an overview, see Int’l Human Rights Law Clinic, Univ. of Cal. Berkeley Sch. of Law, Protecting People and the Planet: A Proposal to Address the Human Rights Impacts of Climate Change Policy (2009), available at http://www.law.berkeley.edu/files/IHRLC/ Protecting_People_and_the_Planet.pdf (proposing a process to address the human rights impacts of climate change policy).

[166] For background on environmental justice, see Clifford Rechtschaffen et al., Environmental Justice: Law, Policy & Regulation (2d ed. 2009); The Law of Environmental Justice: Theories and Procedures to Address Disproportionate Risks (Michael B. Gerrard & Sheila R. Foster eds., 2d ed. 2008).

[167] For background on disaster policy and disaster justice, see Daniel A. Farber et al., Disaster Law and Policy (2d ed. 2009).

[168] See Cong. Black Caucus Found., African Americans and Climate Change: An Unequal Burden (2004), available at http://www.rprogress.org/publications/2004/CBCF_REPORT_F.pdf.

[169] See, e.g., Maxine Burkett, Just Solutions to Climate Change: A Climate Justice Proposal for a Domestic Clean Development Mechanism, 56 Buff. L. Rev. 169 (2008); Jacqueline P. Hand, Global Climate Change: A Serious Threat to Native American Lands and Culture, 38 Envtl. L. Rep. (Envtl. Law Inst.) 10,329 (2008); Alice Kaswan, Environmental Justice and Domestic Climate Change Policy, 38 Envtl. L. Rep. (Envtl. Law Inst.) 10,287 (2008) [hereinafter Kaswan, Domestic Climate Change Policy]; Alice Kaswan, Reconciling Justice and Efficiency: Integrating Environmental Justice into Domestic Cap-And-Trade Programs for Controlling Greenhouse Gases, in Ethics, Energy, And Climate Change (Denis G. Arnold ed., forthcoming 2010), available at http://ssrn.com/abstract=1442165 (follow “One-Click Download” hyperlink); Robert R.M. Verchick, Adaptation, Economics, and Justice, in Economic Thought and U.S. Climate Change Policy (David Driesen ed., forthcoming 2010) (on file with author); Robert R.M. Verchick, Adaptive Justice, in Climate Change: A Reader, supra note 115. For a discussion of how some prominent figures in the religious evangelical community have begun to portray climate change as a human rights issue, see John Copeland Nagle, The Evangelical Debate over Climate Change, 5 U. St. Thomas L.J. 53 (2008).

[170] Kaswan, Domestic Climate Change Policy, supra note 169, at 10,288.

[171] See U.S. Global Change Research Program, supra note 1, passim.

[172] See Rachel Morello-Frosch et al., The Climate Gap: Inequalities in How Climate Change Hurts Americans & How to Close the Gap (2009), available at http://college.usc.edu/ pere/documents/The_Climate_Gap_Full_Report_FINAL.pdf.

[173] See id. at 7–18.

[174] Kaswan, Domestic Climate Change Policy, supra note 169, at 10,289 (footnotes omitted).

[175] For some discussion of the latter, see Stephen T. Del Percio, Linking the Environment and Human Rights: A Global Perspective, 29 Wm. & Mary Envtl. L. & Pol’y Rev. at v (2005); Monique Hardin, The Human Right to a Healthy and Safe Environment: The Right of Displaced Hurricane Katrina Survivors to Return Home with Dignity and Justice, 101 Am. Soc’y Int’l L. Proc. 85 (2007); Barry E. Hill et al., Human Rights and the Environment: A Synopsis and Some Predictions, 16 Geo. Int’l Envtl. L. Rev. 359 (2004); Dinah Shelton, Human Rights and the Environment: What Specific Environmental Rights Have Been Recognized?, 35 Denv. J. Int’l L. & Pol’y 129 (2006).

[176] See Cal. Natural Res. Agency, supra note 31, at 39. See generally Jonathan M. Samet, Adapting to Climate Change: Public Health 7–10 (2009), available at http://www.rff.org/RFF/ Documents/RFF-Rpt-Adaptation-Samet.pdf (discussing the health consequences of heat waves).

[177] See Cal. Natural Res. Agency, supra note 31, at 37.

[178] See id. at 70. See generally David Kling & James N. Sanchirico, Res. for the Future, An Adaptation Portfolio for the United States Coastal and Marine Environment 7 (2009) (discussing the problems caused by “elevated and more frequent extreme sea levels”).

[179] See Cal. Natural Res. Agency, supra note 31, at 82. See generally Alan P. Covich, Emerging Climate Change Impacts on Freshwater Resources: A Perspective on Transformed Watersheds (2009), available at http://www.rff.org/rff/documents/RFF-Rpt-Adaptation-Covich.pdf (discussing socioeconomic and biotic adaptation strategies designed to protect freshwater resources).

[180] See Cal. Natural Res. Agency, supra note 31, at 96. See generally Antle, supra note 49 (discussing the effects climate change will have on the agriculture industry and how, through political planning and support, farmers and ranchers will be able to adjust to climate change and continue with sustainable operations).

[181] See Cal. Natural Res. Agency, supra note 31, at 111.

[182] See id. at 123. See generally James E. Neumann & Jason C. Price, Adapting to Climate Change: The Public Policy Response: Public Infrastructure (2009), available at http://www.rff.org/rff/documents/RFF-Rpt-Adaptation-NeumannPrice.pdf (assessing the threats that climate change poses for public infrastructure and discussing how to respond to those threats).

[183] Carolyn Kousky et al., Responding to Threats of Climate Change
Mega-Catastrophes (Res. for the Future, Discussion Paper No. 09-45-REV, 2009), available at http://www.rff.org/documents/RFF-DP-09-45.pdf.

[184] See id. at 4; see also David E. Adelman, The Challenge of Abrupt Climate Change for U.S. Environmental Regulation, 58 Emory L.J. 379 (2008).

[185] Kousky et al., supra note 183, at 4. The Central Intelligence Agency has established the Center on Climate Change and National Security to study “the national security impact of phenomena such as desertification, rising sea levels, population shifts, and heightened competition for natural resources.” Press Release, Cent. Intelligence Agency, CIA Opens Center on Climate Change and National Security (Sept. 25, 2009), https://www.cia.gov/ news‑information/press-releases-statements/center-on-climate-change-and-national-security.html (last visited Apr. 18, 2010).

[186] See Kousky et al., supra note 183, at 12 (stating that in addition to drastic emissions reduction and geoengineering, the third option for managing catastrophe risks will be “various large-scale adaptation measures that would reduce the consequences of mega-catastrophes or short-circuit the cascading of more localized disasters”).

[187] See Baldwin, supra note 18, at 782 (“Unwavering faith in technology to defeat the effects of climate change induces society to discount too heavily the possibility of catastrophe, so that when disaster does occur, communities that are unprepared to face the challenge will inevitably suffer the greatest losses. Understanding this tendency, communities must embrace the benefits of technology in adaptation and recognize that it represents part of the solution—and not the only mechanism—for combating the impacts of climate change.” (footnote omitted)).

[188] See, e.g., Michael Perry, Coastal Homes Face Huge Losses from Rising Sea, Reuters, Sept. 3, 2009, http://www.reuters.com/article/idUSTRE58209B20090903 (last visited Apr. 18, 2010). See generally Baldwin, supra note 18, at 783 (discussing societal tendency to cling to “industrial, commercial, and residential activities” poorly suited to the areas they are located in).

[189] See, e.g., Irish Acad. of Eng’g, Ireland at Risk: Critical Infrastructure (2009).

[190] See United Nations Dev. Programme, A Climate Risk Management Approach to Disaster Reduction and Adaptation to Climate Change, in Adaptation to Climate Change, supra note 4, at 229, 230.

[191] See Cal. Natural Res. Agency, supra note 31.

[192] The first comprehensive impacts study designed to guide national policy for climate change catastrophes and crises, among other climate change problems, is from 2009. See U.S. Global Change Research Program, supra note 1.

[193] Leonard, supra note 144, at 557–58 (footnotes omitted). For other legal commentary on this theme, which focuses in particular on water crises, see Joseph W. Dellapenna, International Water Law in a Climate of Disruption, 17 Mich. St. J. Int’l L. 43 (2008); Gabriel Eckstein, Water Scarcity, Conflict, and Security in a Climate Change World: Challenges and Opportunities for International Law and Policy (Tex. Tech Univ. Sch. of Law Legal Studies Working Paper Group, Paper No. 2009-01), available at http://ssrn.com/abstract=1425796 (follow “One-Click Download” hyperlink); Charles W. Gould, The Right to Housing Recovery After Natural Disasters, 22 Harv. Hum. Rts. J. 169 (2009); A. Dan Tarlock, Water Scarcity, Fear Mitigation, and International Water Law, 31 Hamline L. Rev. 703 (2008); Lindsay F. Wiley, Adaptation to the Health Consequences of Climate Change as a Potential Influence on Public Health Law and Policy: From Preparedness to Resilience, 15 Widener L. Rev. (forthcoming 2010), available at http://ssrn.com/absract=1474844 (follow “One-Click Download” hyperlink). For an overview of existing disaster law and policy, see Farber et al., supra note 167.

[194] The wait-and-see reactive adaptation orientation is not generally regarded as an effective risk management strategy for climate change. See United Nations Dev. Programme, supra note 190, at 247 (“Any approach to risk management and adaptation should be essentially prospective or anticipatory, and promoted in the very short term.”).

[195] Id.

[196] This is a very real probability. See U.S. Envtl. Prot. Agency, Climate Change and Florida 3 (1997) (“[W]arming and other climate changes may expand the habitat and infectivity of disease-carrying insects, increasing the potential for transmission of diseases such as malaria and dengue (‘break bone’) fever.”).

[197] See, e.g., Lisa Heinzerling & Frank Ackerman, Law and Economics for a Warming World, 1 Harv. L. & Pol’y Rev. 331, 359 (2007) (“A twenty-first-century war on climate change, if the
nation and the world should choose to fight it, will create a new round of technologies and industries . . . .”); War-Like Plan Needed to Tackle Climate Change, Summit Told, ABC News Online (Austl.), Apr. 17, 2007, http://www.abc.net.au/news/newsitems/200704/s1888593.htm (last visited Apr. 18, 2010) (“An American weather expert has told a water summit in Sydney that global warming is such an enormous problem [that] the world needs to go on a war footing to fight it.”).

[198] See Burton, supra note 19, at 94; Saleemul Huq & Hannah Reid, Mainstreaming Adaptation in Development, in Adaptation to Climate Change, supra note 4, at 313.

[199] Smithers & Smit, supra note 15, at 17.

[200] See generally U.S. Global Change Research Program, supra note 1, passim (discussing the political and geographical scales at which adaptation decisions must be made to address climate change).

[201] In addition to the numerous references to such work provided in supra Parts II.A–E, see, for example, Frederick M. Abbott, Innovation and Technology Transfer to Address Climate Change: Lessons from the Global Debate on Intellectual Property and Public Health (Int’l Ctr. for Trade & Sustainable Dev., Issue Paper No. 24, 2009), available at http://ictsd.org/ downloads/2009/07/innovation-and-technology-transfer-to-address-climate-change.pdf (focusing on pharmaceutical technology); Kevin L. Doran, Climate Change Risk Disclosure: A Sector by Sector Analysis of SEC 10-K Filings from 1995–2008, 34 N.C. J. Int’l L. & Com. Reg. (forthcoming 2010), available at http://ssrn.com/abstract=1416279 (follow “One-Click Download” hyperlink) (corporate disclosure policy); Ans Kolk & Jonatan Pinkse, Business and Climate Change: Key Challenges in the Face of Policy Uncertainty and Economic Recession, Mgmt. Online Rev., May 2009, available at http://ssrn.com/abstract=1433037 (follow “One-Click Download” hyperlink) (exploring the implications of the “economy-climate-policy nexus” on the business sector); Andrew Morris et al., Green Jobs Myths, 16 Mo. Envtl. L. & Pol’y Rev. 326 (2009) (exploring the implications of climate change policy in the employment sector); Perry E. Wallace, Global Climate Change and the Challenge to Modern American Corporate Governance, 55 SMU L. Rev. 493 (2002) (corporate law).

[202] See Brian Walker et al., Looming Global-Scale Failures and Missing Institutions,
325 Sci. 1345, 1345 (2009).

[203] Id.

[204] See Harro Van Asselt et al., Global Climate Change and the Fragmentation of International Law, 30 Law & Pol’y 423 (2008); Cinnamon Piñon Carlarne, Good Climate Governance: Only a Fragmented System of International Law Away?, 30 Law & Pol’y 450 (2008); Bonnie Docherty & Terry Giannini, Confronting a Rising Tide: A Proposal for a Convention on Climate Change Refugees, 33 Harv. Envtl. L. Rev. 349 (2009); Meinhard Doelle, Linking the Kyoto Protocol and Other Multilateral Environmental Agreements: From Fragmentation to Integration?, 14 J. Envtl. L. & Prac. 75 (2004); Ben Saul, Climate Change, Conflict and Security: International Law Challenges, 9 N.Z. Armed Forces L. Rev. 1 (2010), available at http://ssrn.com/abstract=1485175 (follow “One-Click Download” hyperlink) (examining security threats associated with climate change and how international environmental law can respond); Ben Saul, Climate Change, Resources Scarcity and Distributive Justice in International Law, in Reveling in the Wilds of Climate Law (R. Lyster ed., forthcoming 2010), available at http://ssrn.com/abstract=1484340 (follow “One-Click Download” hyperlink); Lindsay F. Wiley, Healthy Planet, Healthy People: Integrating Global Health into the International Response to Climate Change, J. Envtl. L. & Litig. (forthcoming 2010), available at http://ssrn.com/ abstract=1489564 (follow “One-Click Download” hyperlink).

[205] See supra note 1 and accompanying text.

[206] National Environmental Policy Act of 1969, 42 U.S.C. §§ 4321–4370 (2006). NEPA requires all federal agencies to “include in every recommendation or report on proposals for legislation and other major Federal actions significantly affecting the quality of the human environment, a detailed statement by the responsible official on—(i) the environmental impact of the proposed action, [and] (ii) any adverse environmental effects which cannot be avoided should the proposal be implemented.” Id. § 4332(2)(C). This provision also requires statements on alternative actions, short- and long-term implications, and “any irreversible and irretrievable commitments of resources.” Id. § 4332(2)(C)(iii)–(v). The Council on Environmental Quality (CEQ), responsible for issuing regulations implementing NEPA’s mandated environmental impact statement procedure for federal agencies, requires agencies to consider the impacts of direct effects, indirect effects, and cumulative impacts. The CEQ has defined direct effects as effects “which are caused by the action and occur at the same time and place,” 40 C.F.R. § 1508.8(a) (2009), indirect effects as effects “which are caused by the action and are later in time or farther removed in distance, but are still reasonably foreseeable,” id. § 1508.8(b), and cumulative impacts as

the impact on the environment which results from the incremental impact of the action when added to other past, present, and reasonably foreseeable future actions regardless of what agency (Federal or non-Federal) or person undertakes such other actions. Cumulative impacts can result from individually minor but collectively significant actions taking place over a period of time.

Id. § 1508.7.

[207] See, e.g., Cass R. Sunstein, The Cost-Benefit State: The Future of Regulatory Protection (2002).

[208] For critiques of using cost-benefit analysis in environmental and natural resources decision contexts, see Frank Ackerman & Lisa Heinzerling, Priceless: On Knowing the Price of Everything and the Value of Nothing (2004); Frank Ackerman & Lisa Heinzerling, Pricing the Priceless: Cost-Benefit Analysis of Environmental Protection, 150 U. Pa. L. Rev. 1553 (2002); David Driesen, Distributing the Costs of Environmental, Health and Safety Protection: The Feasibility Principle, Cost-Benefit Analysis, and Regulatory Reform, 32 B.C. Envtl. Aff. L. Rev. 1 (2005); David Driesen, Is Cost-Benefit Analysis Neutral?, 77 U. Colo. L. Rev. 335 (2006); Thomas O. McGarity, A Cost-Benefit State, 50 Admin. L. Rev. 7 (1998); Sidney A. Shapiro & Christopher H. Schroeder, Beyond Cost-Benefit Analysis: A Pragmatic Reorientation, 32 Harv. Envtl. L. Rev. 433 (2008).

[209] See Sidney A. Shapiro & Robert L. Glicksman, Risk Regulation at Risk: Restoring a Pragmatic Approach (2003); Sidney A. Shapiro & Robert L. Glicksman, The Missing Perspective, Envtl. F., Mar.–Apr. 2003, at 42, 43.

[210] 50 C.F.R. § 402.14(g)(3)–(4) (2009). The agency defines cumulative effects as “those effects of future State or private activities, not involving Federal activities, that are reasonably certain to occur within the action area.” Id. § 402.02.

[211] Federal Water Pollution Control Act, 33 U.S.C. §§ 1251–1387 (2006).

[212] Id. § 1334. Statutory policies allow the Corps to issue general permits for disposal of fill material in navigable waters covering classes of activities the agency determines “are similar in nature, will cause only minimal adverse environmental effects when performed separately, and will have only minimal cumulative adverse effect on the environment.” Id. § 1344(e)(1). Corps regulations for project-specific fill permits require the agency to conduct “an evaluation of the probable impacts, including cumulative impacts, of the proposed activity.” 33 C.F.R. § 320.4(a)(1) (2009).

[213] See supra Part II.

[214] See generally Daniel A. Farber, Probabilities Behaving Badly: Complexity Theory and Environmental Uncertainty, 37 U.C. Davis L. Rev. 145, 148–55 (2003) (discussing the problems with uncertainty in environmental law); Ruhl, supra note 99, at 954–67 (addressing the complexities inherent to environmental law and the environment).

[215] Council on Envtl. Quality, Considering Cumulative Effects Under the National Environmental Policy Act, at vi (1997).

[216] Id. at 38.

[217] See supra note 6.

[218] See U.S. Global Change Research Program, supra note 1, at 107–52 (providing regional studies for the United States).

[219] Id. at 154.

[220] Intergovernmental Panel on Climate Change, supra note 2, at 724.

[221] Id. at 727; see also European Env’t Agency, supra note 47, at 7 (“[T]here is currently very little quantified information on these costs, and further work is urgently needed to build the evidence base to facilitate informed, cost effective and proportionate adaptation in Europe.”).

[222] See Carolyn Kousky & Roger M. Cooke, The Unholy Trinity: Fat Tails, Tail Dependence, and Micro-Correlations (Res. for the Future, Discussion Paper No. 09-36-REV, 2009).

[223] Id. at 1; see also Kousky & Cooke, supra note 120, passim (applying these concepts specifically to climate change adaptation); Daniel A. Farber, Uncertainty (Feb. 18, 2010) (unpublished manuscript), available at http://ssrn.com/abstract=1555343 (follow “One Click Download” hyperlink) (describing analytic tools for assessing potential climate change catastrophic outcomes). Aggregated microcorrelations have been described as leading to the “Jenga effect,” named after the game in which players stack pieces into a tower and then remove them, one by one, stacking the removed pieces on the top of the tower. See Peter C. de Ruiter et al., Food Web and Ecology: Playing Jenga and Beyond, 309 Sci. 68, 68 (2005). With skilled players, the structure can stay standing for quite awhile, but at some point one more piece removed or stacked on top leads to a sudden crash of the entire structure. Food web dynamics exhibit this effect. Id.

[224] See Edward B. Barbier et al., Coastal Ecosystem-Based Management with Nonlinear Ecological Functions and Values, 319 Sci. 321 (2008) (examining the policy difficulties flowing from such nonlinearities).

[225] See Baldwin, supra note 18, at 771 (environmental impact assessments); Daniel A. Farber, Adaptation Planning and Climate Impact Assessments: Learning from NEPA’s Flaws, 39 Envtl. L. Rep. (Envtl. Law Inst.) 10,605 (2009) [hereinafter Farber, NEPA’s Flaws] (environmental impact assessments); Daniel A. Farber, Modeling Climate Change and Its Impacts: Law, Policy, and Science, 86 Tex. L. Rev. 1655 (2008); Robert L. Glicksman, Global Climate Change and the Risks to Coastal Areas from Hurricanes and Rising Sea Levels: The Costs of Doing Nothing, 52 Loy. L. Rev. 1127 (2006) (cost-benefit analysis); Douglas Kysar, Climate Change, Cultural Transformation, and Comprehensive Rationality, 31 B.C. Envtl. Aff. L. Rev. 555 (2004) (cost‑benefit analysis).

[226] Farber, NEPA’s Flaws, supra note 225, at 10,610.

[227] See id. at 10,607–14; see also Caleb W. Christopher, Success by a Thousand Cuts: The Use of Environmental Impact Assessment in Addressing Climate Change, 9 Vt. J. Envtl. L. 549, 592 (2008) (proposing adaptive approaches for NEPA in the climate change context). To be sure, there remains considerable value in retaining a front-end component of environmental assessments to anticipate climate change impacts, particularly to the extent doing so helps to increase public awareness and internalize consideration of climate change impacts in federal agencies and state, local, and private actors whose actions are subject to NEPA and its state law equivalents. See Michael B. Gerrard, Climate Change and the Environmental Impact Review Process, Nat. Resources & Env’t, Winter 2008, at 20 (surveying federal, state, and local assessment programs); Catherine J. LaCroix, SEPAs, Climate Change, and Corporate Responsibility: The Contribution of Local Government, 58 Case W. Res. L. Rev. 1289, 1291 (2008). Toward that end, in February 2010 the White House Council on Environmental Quality, which develops general regulations and guidance for implementation of NEPA, issued draft guidance on how to evaluate the effects of climate change and greenhouse gas emissions in NEPA assessments. See Memorandum from Nancy H. Sutley, Chair, Council on Envtl. Quality, to the Heads of Federal Departments and Agencies (Feb. 18, 2010), available at http://www.whitehouse.gov/sites/default/files/microsites/ceq/20100218-nepa-consideration-effects-ghg-draft-guidance.pdf (providing “Draft NEPA Guidance on Consideration of the Effects of Climate Change and Greenhouse Gas Emissions”). The overwhelming focus of the guidance, however, is on greenhouse gas emissions and evaluation of mitigation actions, with little attention to adaptation beyond stating the obvious that “[i]n cases where adaptation to the effects of climate change is important, the significant aspects of these changes should be identified in the agency’s final decision and adoption of a monitoring program should be considered.” Id. at 7.

[228] See Mary Jane Angelo, Stumbling Toward Success: A Story of Adaptive Law and Ecological Resilience, 87 Neb. L. Rev. 950, 955 & n.24 (2009).

[229] C.S. Holling et al., Adaptive Environmental Assessment and Management (C.S. Holling ed., 1978); see also Kai N. Lee & Jody Lawrence, Adaptive Management: Learning from the Columbia River Basin Fish and Wildlife Program, 16 Envtl. L. 431, 442 n.45 (1986) (tracing the term “adaptive management” to Holling’s book).

[230] See Holling et al., supra note 229, at 20, 47–48. For background on the adaptive management model, see Angelo, supra note 228; Holly Doremus, Adaptive Management, the Endangered Species Act, and the Institutional Challenges of “New Age” Environmental Protection, 41 Washburn L.J. 50 (2001); Bradley C. Karkkainen, Panarchy and Adaptive Change: Around the Loop and Back Again, 7 Minn. J.L. Sci. & Tech. 59 (2005); J.B. Ruhl, Regulation by Adaptive Management—Is It Possible?, 7 Minn. J.L. Sci. & Tech 21 (2005).

[231] See Holling et al., supra note 229, at 133, 135.

[232] See id. at 135.

[233] Panel on Adaptive Mgmt. for Res. Stewardship et al., Nat’l Research Council, Adaptive Management for Water Resources Project Planning 22 (2004).

[234] The National Research Council explains:

Adaptive management is not a “one size fits all” or a “cookbook” process, as experience with the concept and its related procedures to date is limited and evolving. There are multiple views and definitions regarding adaptive management, but elements that have been identified in theory and in practice are: management objectives that are regularly revisited and accordingly revised, a model(s) of the system being managed, a range of management options, monitoring and evaluating outcomes of management actions, mechanisms for incorporating learning into future decisions, and a collaborative structure for stakeholder participation and learning.

Id. at 2. For a thorough description of adaptive management theory and protocol, see id. at 19–32.

[235] Notice of Availability of a Final Addendum to the Handbook for Habitat Conservation Planning and Incidental Take Permitting Process, 65 Fed. Reg. 35,242, 35,252 (June 1, 2000).

[236] See Ronald D. Brunner & Tim W. Clark, A Practice-Based Approach to Ecosystem Management, 11 Conservation Biology 48 (1997); Anne E. Heissenbuttel, Ecosystem Management—Principles for Practical Application, 6 Ecological Applications 730 (1996); Paul  L. Ringold et al., Adaptive Monitoring Design for Ecosystem Management, 6 Ecological Applications 745 (1996). Indeed, the Ecological Society of America’s comprehensive study of ecosystem management treats the use of adaptive management methods as a given. See Norman L. Christensen et al., The Report of the Ecological Society of America Committee on the Scientific Basis for Ecosystem Management, 6 Ecological Applications 665 (1996).

[237] See Glicksman, supra note 26, passim. “The land management agencies, in the planning process as well as in other contexts, must rely heavily on the management technique known as adaptive management.” Id. at 868 (emphasis omitted).

[238] See Camacho, supra note 18, passim. Camacho calls for “an adaptive methodology for assessing and adjusting government decision making over time.” Id. at 64.

[239] See Craig, supra note 18 (manuscript at 65–67) (utilizing the heading “Be Serious About Using Adaptive Management—and Change Both Natural Resources and Administrative Laws to Allow for It”).

[240] See Carl Bruch, The End of Equilibrium, Envtl. F., Sept.–Oct. 2008, at 30, 32 (“Incorporating adaptive management into laws and institutions can enhance the capacity of governance systems and ecosystems to adapt to changing climatic conditions, to develop and deploy new technologies and techniques.”).

[241] Administrative law scholars have identified the need to reform administrative law at fundamental levels if adaptive management is going to work. See Ruhl, supra note 230, at 46–53. An underlying concern with this direction of change, however, is in retaining accountability, participation, and transparency in decision making. See David L. Markell, Slack in the Administrative State and Its Implications for Governance: The Issue of Accountability, 84 Or. L. Rev. 1 (2005); David Markell, The Role of Spotlighting Procedures to Promote Citizen Participation, Transparency, and Accountability: Lessons from the CEC’s Citizen Submissions Process, 45 Wake Forest L. Rev. (forthcoming 2010), available at http://papers.ssrn.com/sol3/ papers.cfm?abstract_id=1553125 (follow “One-Click Download” hyperlink); David L. Markell & Tom R. Tyler, Using Empirical Research to Design Government Participation Processes: A Case Study of Citizens’ Roles in Environmental Compliance and Enforcement, 57 Kan. L. Rev. 1 (2008).

[242] See Nancy B. Grimm, Global Change and the Ecology of Cities, 319 Sci. 756, 756 (2008).

[243] See Mark A. Cohen & Michael P. Vandenbergh, Consumption, Happiness, and Climate Change, 38 Envtl. L. Rep. (Envtl. Law Inst.) 10,834 (2008); Douglas A. Kysar & Michael P. Vandenbergh, Introduction: Climate Change and Consumption, 38 Envtl. L. Rep. (Envtl. Law Inst.) 10,825 (2008); Michael P. Vandenbergh et al., Individual Carbon Emissions: The Low‑Hanging Fruit, 55 UCLA L. Rev. 1701 (2008); Michael P. Vandenbergh & Anne C. Steinemann, The Carbon Neutral Individual, 82 N.Y.U. L. Rev. 1673 (2007); see also John Dernbach, Stabilizing and then Reducing U.S. Energy Consumption: Legal and Policy Tools for Efficiency and Conservation, 37 Envtl. L. Rep. (Envtl. Law Inst.) 10,003 (2007) (discussing the success of Energy Star consumer products and residential energy efficiency); Alice Kaswan, Climate Change, Consumption, and Cities, 36 Fordham Urb. L.J. 253, 255–68 (2009) (discussing per capita emissions and the need for change beyond the industrial sector); Albert C. Lin, Evangelizing Climate Change, 17 N.Y.U. Envtl. L.J. 1135 (2009) (exploring the problem of changing individual behaviors and attitudes relevant to global warming); Symposium, Climate Change and Consumption, 38 Envtl. L. Rep. (Envtl. Law Inst.) 10,825 (2008).

[244] According to the U.S. Geological Survey,

Excessive nutrients, in particular nitrogen and phosphorus, have resulted in the growth of large amounts of algae that decay and consume oxygen, thereby causing a zone of low dissolved oxygen or “hypoxic zone” in the Northern Gulf of Mexico. This can stress and cause death in bottom-dwelling organisms, threatening the economic and ecological health of one of the nation’s largest and most productive fisheries.

U.S. Geological Survey, U.S. Dep’t of the Interior, Mississippi River Basin and Gulf of Mexico Hypoxia, http://water.usgs.gov/nawqa/sparrow/gulf_findings/hypoxia.html (last visited Apr. 18, 2010). The most definitive study of the causes concludes that runoff from agricultural sources contributes 70% of the excess nutrients. See Richard B. Alexander et al., Differences in Phosphorous and Nitrogen Delivery to the Gulf of Mexico from the Mississippi River Basin, 42 Envtl. Sci. & Tech. 822, 822 (2008), available at http://pubs.acs.org/doi/pdf/10.1021/es0716103. Hypoxia from agricultural runoff and urban sewage is expanding exponentially throughout the world as well, affecting 400 estuarine systems covering over 245,000 square kilometers. See Robert J. Diaz & Rutger Rosenberg, Spreading Dead Zones and Consequences for Marine Ecosystems, 321 Sci. 926, 926 (2008). See generally Mindy Selman et al., Eutrophication and Hypoxia in Coastal Areas: A Global Assessment of the State of Knowledge (World Res. Inst., Policy Note No. 1, 2008), available at http://pdf.wri.org/eutrophication_and_hypoxia_ in_coastal_areas.pdf (providing an overview of eutrophication and hypoxia).

[245] See J.B. Ruhl & James Salzman, Massive Problems in the Administrative State: Strategies for Whittling Away, 98 Cal. L. Rev. (forthcoming 2010) (manuscript at 4, 7), available  at http://papers.ssrn.com/sol3/papers.cfm?abstract_id=1280896 (follow “One Click Download” hyperlink).

[246] Bradley C. Karkkainen, “New Governance” in Legal Thought and in the World: Some Splitting as Antidote to Overzealous Lumping, 89 Minn. L. Rev. 471, 473 (2004). For a sweeping overview of New Governance theory, one which Karkkainen, supra note 230, reviews, see Orly Lobel, The Renew Deal: The Fall of Regulation and the Rise of Governance in Contemporary Legal Thought, 89 Minn. L. Rev. 342 (2004) [hereinafter Lobel, The Renew Deal]. For additional scholarship developing New Governance principles, see The Tools of Government: A Guide to the New Governance (Lester M. Salamon ed., 2002); Cristie L. Ford, New Governance, Compliance, and Principles-Based Securities Regulation, 45 Am. Bus. L.J. 1 (2008); Alana Klein, Judging as Nudging: New Governance Approaches for the Enforcement of Constitutional Social and Economic Rights, 39 Colum. Hum. Rts. L. Rev. 351 (2008); Orly Lobel, Setting the Agenda for New Governance Research, 89 Minn. L. Rev. 498 (2004); Lester M. Salamon, The New Governance and the Tools of Public Action: An Introduction, 28 Fordham Urb. L.J. 1611 (2001); Michael Waterstone, A New Vision of Public Enforcement, 92 Minn. L. Rev. 434 (2007).

[247] See Lobel, The Renew Deal, supra note 246, at 371–404.

[248] See J.B. Ruhl et al., Implementing the New Ecosystem Services Mandate of the Section 404 Compensatory Mitigation Program—A Catalyst for Advancing Science and Policy, 38 Stetson L. Rev. 251, 256–59 (2009) (summarizing critiques).

[249] Jessica B. Wilkinson et al., The Next Generation of Mitigation: Linking Current and Future Mitigation Programs with State Wildlife Action Plans and Other State and Regional Plans 43 (2009) (noting the authors are from The Nature Conservancy and the Environmental Law Institute).

[250] Id.

[251] Some New Governance measures will be rather straightforward, such as strengthening climate change risk disclosures by publicly traded companies under securities regulation. See Mark Latham, Environmental Liabilities and the Federal Securities Laws: A Proposal for Improved Disclosure of Climate Change-Related Risks, 39 Envtl. L. 647 (2009).

[252] See supra note 24.

[253] Farber, supra note 24, at 1.

[254] Henry N. Butler & Jonathan R. Macey, Externalities and the Matching Principle: The Case for Reallocating Environmental Regulatory Authority, 14 Yale L. & Pol’y Rev. 23, 53 (1996).

[255] See Hari M. Osofsky, Is Climate Change “International”? Litigation’s Diagonal Regulatory Role, 49 Va. J. Int’l L. 585, 587 (2009) (suggesting greater emphasis on connections between governance institutions at different scales).

[256] Governor’s Action Team on Energy & Climate Change, State of Fla., Phase 1 Report: Florida’s Energy and Climate Change Action Plan 55 (2007).

[257] Nev. Climate Change Advisory Comm., Final Report 14 (2008).

[258] See, e.g., Or. Dep’t of Energy, Climate Change in Oregon, http://www.oregon.gov/ ENERGY/GBLWRM/climhme.shtml (last visited Apr. 18, 2010).

[259] See, e.g., Lara Whitely Binder, Preparing for Climate Change in the U.S. Pacific Northwest, 15 Hastings W.-Nw. J. Envtl. L. & Pol’y 183 (2009); Alejandro E. Camacho, Climate Change and Regulatory Fragmentation in the Great Lakes Basin, 17 Mich. St. J. Int’l L. 139 (2008); Colin Crawford, Our Bandit Future? Cities, Shantytowns, and Climate Change Governance, 36 Fordham Urb. L.J. 211 (2009); John C. Dernbach, Toward a Climate Change Strategy for Pennsylvania, 12 Penn. St. Envtl. L. Rev. 181 (2004); Porras, supra note 18, at 591 (focusing on the role of cities).

[260] See Saul & McAdam, supra note 164, at 5–7.

[261] Some examples include Robin Kundis Craig, Climate Change, Regulatory Fragmentation, and Water Triage, 79 U. Colo. L. Rev. 825 (2008) (focusing on national policy for marine environment adaptation), and Leonard, supra note 144, at 560–62 (proposing a national land-use regime and infrastructure development for protection of coastal communities).

[262] See, e.g., Kirsten H. Engel, Harnessing the Benefits of Dynamic Federalism in Environmental Law, 56 Emory L.J. 159, 161 (2006).

[263] Id. at 176. As Kirsten Engel explains, “Alternatively named ‘empowerment federalism,’ ‘polyphonic federalism,’ ‘interactive federalism,’ ‘dynamic federalism,’ and even ‘vertical regulatory competition,’ this reconceptualization has come in the form of a cluster of theoretical proposals, all rejecting dual federalism and all emphasizing the benefits of overlapping federal and state power.” Id. (citations omitted). For additional scholarship developing Dynamic Federalism and related principles, see David E. Adelman & Kirsten H. Engel, Adaptive Federalism: The Case Against Reallocating Environmental Regulatory Authority, 92 Minn. L. Rev. 1796 (2008); Robert B. Ahdieh, From Federalism to Intersystemic Governance: The Changing Nature of Modern Jurisdiction, 57 Emory L.J. 1 (2007); Renee M. Jones, Dynamic Federalism: Competition, Cooperation and Securities Enforcement, 11 Conn. Ins. L.J. 107 (2005); Robert A. Schapiro, From Dualist Federalism to Interactive Federalism, 56 Emory L.J. 1 (2006); Robert A. Schapiro, Toward a Theory of Interactive Federalism, 91 Iowa L. Rev. 243 (2005) [hereinafter Schapiro, Toward Interactive Federalism]; Robert B. Ahdieh, Foreign Affairs, International Law, and the New Federalism: Lessons from Coordination (Emory Univ. Sch. of Law, Law & Econ. Working Paper Group, Paper No. 08-30, 2008), available at http://ssrn.com/abstract=1272967 (follow “One-Click Download” hyperlink).

[264] Benjamin K. Sovacool, The Best of Both Worlds: Environmental Federalism and the Need for Federal Action on Renewable Energy and Climate Change, 27 Stan. Envtl. L.J. 397, 448 (2008). Of course, overlap of authority can occur under dual federalism if federal and state authorities independently regulate the same problem, and under cooperative federalism when the federal government employs (or more accurately, coerces) state governments to implement federal standards. By contrast, overlap of authority under Dynamic Federalism is neither accidental nor coerced. Adelman and Engel explain that cooperative federalism

fares somewhat better with the dynamic school. The overlapping authority, although asymmetric, at least has the trappings of a dynamic system. Cooperative federalism nonetheless falls short from the point of view of the dynamic school. The federal laws and regulations are often, but not always, so comprehensive as to exclude for all practical purposes alternative approaches by the states.

Adelman & Engel, supra note 263, at 1812–13. Still, many commentators express faith in the ability of traditional cooperative federalism governance to respond effectively to climate change. See, e.g., Holly Doremus & W. Michael Hanemann, Of Babies and Bathwater: Why the Clean Air Act’s Cooperative Federalism Is Useful for Addressing Global Warming, 50 Ariz. L. Rev. 799 (2008).

[265] Engel, supra note 262, at 161.

[266] Adelman & Engel, supra note 263, at 1798.

[267] Id. at 1796.

[268] See id. at 1808; Schapiro, Toward Interactive Federalism, supra note 263, at 292–93; Sovacool, supra note 264, at 448–51.

[269] See Jacob E. Gersen, Overlapping and Underlapping Jurisdiction in Administrative Law, 2006 S. Ct. Rev. 201, 214.

[270] See Adelman & Engel, supra note 263, at 1817–18.

[271] See id. at 1809–10 (summarizing literature suggesting that overlapping authority can promote initiative at one governance scale and spark other scales to follow promising policy innovations).

[272] Transgovernmental Networks theory emphasizes the role of “networks of similarly‑situated technocrats” who work in many different governance units, and “conceive[s] of lawmaking as an organic enterprise, harnessing the technical expertise of bureaucrats who do not possess heady titles but nonetheless intimately understand the practical exigencies of their particular issue areas.” Janet Koven Levit, A Bottom-Up Approach to International Lawmaking: The Tale of Three Trade Finance Instruments, 30 Yale J. Int’l L. 125, 182 (2005). The seminal and still most comprehensive discussion of Transgovernmental Network theory is found in Anne-Marie Slaughter, A New World Order (2004). For additional scholarship developing Transgovernmental Network principles, see Neil Craik & Joseph DiMento, Environmental Cooperation in the (Partially) Disaggregated State: Lessons from the Security and Prosperity Partnership of North America, 8 Chi. J. Int’l L. 479, 484–92 (2008); Patrick X. Delaney, Transnational Corruption: Regulation Across Borders, 47 Va. J. Int’l L. 413 (2007); Jenia Iontcheva Turner, Transnational Networks and International Criminal Justice, 105 Mich. L. Rev. 985 (2007); Eleanor D. Kinney, The Emerging Field of International Administrative Law: Its Content and Potential, 54 Admin. L. Rev. 415, 425–27 (2002); Kal Raustiala, The Architecture of International Cooperation: Transgovernmental Networks and the Future of International Law, 43 Va. J. Int’l L. 1 (2002); Anne-Marie Slaughter, The Accountability of Government Networks, 8 Ind. J. Global Legal Stud. 347 (2001); Christopher Whytock, A Rational Design Theory of Transgovernmentalism: The Case of E.U.-U.S. Merger Review Cooperation, 23 B.U. Int’l L.J. 1 (2005).

[273] See Slaughter, supra note 272, at 18, 22–23.

[274] See id. at 19–22.

[275] See Freeman & Farber, supra note 146, at 899 (“It is intriguing to see the supposedly hierarchical world of domestic regulation evolving in a direction reminiscent of modern international relations.”).

[276] Grouping climate change mitigation with other large-scale massive problems, Jim Salzman and I have argued that the convergence of New Governance, Dynamic Federalism, and Transgovernmental Networks models fits well with the needs of mitigation policy. See Ruhl & Salzman, supra note 245 (manuscript at 8–9). We use coastal hypoxia as the primary example, however, and do not delve significantly into climate change adaptation. Id. (manuscript at
46–49); see also Markell, supra note 35 (manuscript at 16) (using New Governance theory to explore climate change mitigation).

[277] See, e.g., Glicksman, supra note 26, at 872–74 (exploring multiagency coordination for ecological management); Richard J. Lazarus, Super Wicked Problems and Climate Change: Restraining the Present to Liberate the Future, 94 Cornell L. Rev. 1153, 1156 (2009) (mentioning adaptation in connection with federal-state relations in climate change policy); Bradford C. Mank, Protecting the Environment for Future Generations: A Proposal for a “Republican” Superagency, 5 N.Y.U. Envtl. L.J. 444 (1996) (suggesting the role of a federal “Superagency” for, among other things, climate change adaptation); Carol M. Rose, Federalism and Climate Change: The Role of States in a Future Federal Regime—An Introduction, 50 Ariz. L. Rev. 673 (2008) (recognizing the role of state and local governments in adaptation policy); Jared Snyder & Jonathan Binder, The Changing Climate of Cooperative Federalism: The Dynamic Role of the States in a National Strategy to Combat Climate Change, 27 UCLA J. Envtl. L. & Pol’y 231 (2009) (containing scattered references to adaptation as a state and local concern).

[278] See Farber, supra note 24.

[279] See id. at 13 –19.

[280] See id. at 19–32.

[281] Id. at 33.

[282] Anna T. Moritz et al., Biodiversity Baking and Boiling: Endangered Species Act Turning Down the Heat, 44 Tulsa L. Rev. 205, 230 (2008).

[283] See J.B. Ruhl, Climbing Mount Mitigation: A Proposal for Legislative Suspension of Climate Change “Mitigation Litigation, 1 Wash. & Lee J. Energy, Climate & Env’t (forthcoming 2010) (on file with author).

[284] See Memorandum from Mark D. Myers, Dir., U.S. Geological Survey, to Dir., U.S. Fish & Wildlife Serv., and Solicitor, U.S. Dep’t of the Interior 1 (May 14, 2008), available at http://www.usgs.gov/global_change/docs/director_memo_14may08.pdf.

[285] I provide a detailed discussion of what I believe is the poor fit between the Endangered Species Act (ESA) and greenhouse gas emission reduction policy in Ruhl, supra note 26, at 39–49. See also Robert Meltz, Cong. Research Serv., Use of the Polar Bear Listing to Force Reduction of Greenhouse Gas Emissions: The Legal Arguments 3–5 (2008) (laying out the legal basis for both positions); Matthew Gerhart, Climate Change and the Endangered Species Act: The Difficulty of Proving Causation, 36 Ecology L.Q. 167, 171–82 (2009) (detailing the causation obstacles to using the ESA to regulate greenhouse gas emissions); John Kostyack & Dan Rohlf, Conserving Biodiversity in an Era of Global Warming: An Environmental Community Perspective, in Endangered Species Act: Law, Policy, and Perspectives 374, 388 (Donald C. Bauer & Wm. Robert Irvin eds., 2d ed. 2010) (concluding “such a use of the ESA has a number of inherent flaws” and “the Act simply cannot serve as a driver of GHG emissions reductions”). But see Ari N. Sommer, Taking the Pit Bull off the Leash: Siccing the Endangered Species Act on Climate Change, 36 B.C. Envtl. Aff. L. Rev. 273, 303–04, 307–08 (2009) (arguing that there is no significant obstacle to proving causation in a claim that greenhouse gas emissions cause injury to species in violation of the ESA).

[286] See Bruch, supra note 240, at 35 (noting in an outline of key issues in “[t]he transition to adaptation” that “[i]t is first necessary to build trust”). For a general exposition on the lack of trust between the interests working in environmental policy, see Douglas A. Kysar & James Salzman, Environmental Tribalism, 87 Minn. L. Rev. 1099 (2003) (exploring the contested nature of environmental law and policy).

[287] Cf. Cary Coglianese & Jocelyn D’Ambrosio, Policymaking Under Pressure: The Perils of Incremental Responses to Climate Change, 40 Conn. L. Rev. 1411 (2008) (describing the prevalence of incremental environmental policymaking and the inherent problems it presents, particularly in the climate change context).

[288] Farber, supra note 24, at 33.

[289] See In the Year 2049: What Will Environmental Protection Be Like 40 Years from Now?, Envtl. F., Nov.–Dec. 2009, at 46.

[290] John C. Cruden, Ten Reasons for Environmental Optimism, Envtl. F., Nov.–Dec. 2009, at 48, 48.

[291] Lee A. DeHihns, III, Looking at the Percentages of Possibility, Envtl. F., Nov.–Dec. 2009, at 48, 48.

[292] Paul E. Hagen, The End of the Environmental Profession, Envtl. F., Nov.–Dec. 2009, at 49, 49.

[293] Sara Kendall, The CFR Will Still Exist, but Markets Will Rule the Day, Envtl. F., Nov.–Dec. 2009, at 50, 50.

[294] See Michael B. Gerrard, Environmental Law in 2049: A Look Back, Envtl. F., Nov.–Dec. 2009, at 49, 49.

[295] James Gustave Speth, On One Hand, Danger, On the Other, Security, Envtl. F., Nov.–Dec. 2009, at 51, 51.

[296] Michael P. Vandenbergh, Two Scenarios Offer Contrasting Futures for Field, Envtl. F., Nov.–Dec. 2009, at 51, 51.

[297] Accord Bruch, supra note 240, at 35 (outlining the key elements of “adaptation law”); John C. Dernbach & Seema Kakade, Climate Change Law: An Introduction, 29 Energy L.J. 1, 2 (2008) (describing the emergence of “climate change law” as “the intersection of several areas of law, including environmental law, energy law, business law, and international law”); Jacqueline Peel, Climate Change Law: The Emergence of a New Legal Discipline, 32 Melb. U. L. Rev. 922, 924 (2008) (arguing that climate change law must be developed with an awareness of “the diverse disciplines (such as science, economics, and social science) that underpin conceptions of the climate change challenge”).

A Fish Tale: A Small Fish, The ESA, And Our Shared Future

ESSAY

A Fish Tale: A Small Fish, the ESA, and Our Shared Future

By

Dale D. Goble*

The objective of the Endangered Species Act is to “recover” imperiled species and thus to render the Act’s conservation tools unnecessary. To achieve this goal, the drafters of the Act crafted a linear process that begins with an assessment of the threats facing the species and moves through the elimination of those threats to the recovery and delisting of the species.

It has become increasingly apparent over the past decade that few species fit this model: most species face threats—altered habitats and competition with invasive species—that cannot be eliminated. These  species are “conservation reliant” because they will require ongoing conservation management. Conservation-reliant species can be recovered biologically through management actions at the relevant scale, but delisting such species is problematic because to do so will deprive the species of the management required to maintain its numbers and distribution. To date, a handful of conservation-reliant species have been delisted as recovered pursuant to management agreements that obligate a manager—a federal or state agency, a conservation organization, or a specially created management entity—to provide ongoing conservation management activities.

These developments are examined in part by using the Borax Lake chub—a small fish endemic to a highly alkaline lake in eastern Oregon—as a continuing example of both how the Act was intended to operate and how it might be re‑envisioned to achieve its recovery goals in a rapidly changing conservation landscape.

I.

The Borax Lake chub (Gila boraxobius) is a small fish (typically 1.3 to two inches in length) that is dark olive-green above and mostly silver below with a hint of purple iridescence.[1] It is an opportunistic omnivore, feeding on whatever comes its way: aquatic and terrestrial insects, spiders, mollusks and their eggs, aquatic worms, algae, and seeds.[2] The species reaches reproductive maturity within a single year.[3] Although it spawns primarily in the spring, breeding can occur throughout the year.[4]

The chub takes its name from the environment that created it: Borax Lake, a small (10.2-acre), shallow (less than three feet), highly mineralized, alkaline lake in the Alvord Basin of eastern Oregon’s high desert.[5] Borax Lake, which is fed by subterranean hot springs, is an unusual ecosystem, in part because it is a “perched” lake: Precipitation of minerals from the water over the millennia has raised the lake’s shoreline approximately thirty feet above the salt crust that covers the adjacent desert playa.[6] Water overflowing the lake’s southwest rim has created an extensive marsh that ends in the small, intermittent Lower Borax Lake.[7]

The springs flowing into the lake have temperatures between 95 and 104 degrees Fahrenheit (ºF).[8] The chub prefers water of 84ºF to 86ºF, and temperatures above 93ºF are potentially lethal.[9] The chubs therefore live around the shallow perimeter of the lake and in the wetlands at the lake’s outflow where the temperature is within their preferred range.[10] This further reduces the available habitat to only a fraction of the lake’s area and makes the species particularly vulnerable to decreases in water level.[11]

During the Pleistocene, the floor of the Alvord Basin was covered by Lake Alvord, a large pluvial lake that was the ancestral home of the chub.[12] The level of Lake Alvord has fluctuated greatly over at least the past 40,000 years.[13] Within the last 10,000 years it largely dried up, leaving only two intermittent remnants: Alvord Lake in Oregon and Continental Lake in Nevada.[14] The retreat of Lake Alvord restricted the lake’s fish to scattered populations in the few permanent springs and creeks that remained.[15]

Prior to 1980, the Borax Lake chub had been considered a dwarfed population of the Alvord chub (Gila alvordensis), the species found elsewhere in the Alvord Basin.[16] Isolation from other populations of the Alvord chub, plus a combination of extreme environmental conditions, short generation times in the warm water, and the small number of founding individuals, led to a rapid differentiation of the population into what is now acknowledged to be a distinct, endemic species—the Borax Lake chub.[17]

II.

The purpose of the Endangered Species Act (ESA)[18] is to “conserve” species at risk of extinction and the ecosystems upon which these species depend.[19] This is more than a requirement simply to prevent extinction. “Conserve” is defined as the affirmative mandate to “use . . . all methods and procedures which are necessary to bring any [listed] species . . . to the point at which the measures provided pursuant to this [Act] are no longer necessary.”[20] Conservation, in other words, requires the recovery of listed species. To achieve this goal, the Act’s drafters crafted what they envisioned to be an orderly progression that moves from assessing the threats facing a species, through the elimination of those threats, to recovery and delisting.[21]

The threshold to this progression is a risk assessment. The federal agencies responsible for implementing the Act are required to determine whether a species is either endangered or threatened based on a set of enumerated threats.[22] The Act defines “endangered species” as “any species which is in danger of extinction throughout all or a significant portion of its range.”[23] The definition of “threatened species” differs only through the addition of an explicit temporal component: a threatened species is “any species which is likely to become an endangered species within the foreseeable future throughout all or a significant portion of its range.”[24] These standards are none too precise: The statutory definitions require the decision maker to determine whether a species is to be listed given its risk of extinction (i.e., “in danger of extinction, or likely to become so”[25]) over a temporal scale (i.e., now or “within the foreseeable future”[26]).

The species’s status as endangered, threatened, or insufficiently at risk to warrant listing is determined by assessing five threat factors: 1) habitat destruction or range curtailment, 2) overutilization, 3) disease or predation, 4) inadequate regulatory mechanisms, and 5) any “other natural or manmade factors.”[27] If the agency concludes that a species is either threatened or endangered, it is required to list the species.[28]

Listing triggers the ESA’s risk-management provisions.[29] These can be divided in to two functional groups. The first is extinction prevention, a group of tools—primarily restrictions on actions such as the prohibition on taking an endangered species—intended to protect a listed species from activities that threaten its continued existence.[30] The second group of risk-management provisions are recovery actions. These are a far more varied group of affirmative statutory tools intended to address the threats facing a species; they include mechanisms such as the authority to transplant populations or restore habitat.[31]

The drafters of the ESA appear to have assumed that recovery actions would eliminate the threats facing the species and that its population would rebound. When this occurred, the listing agency would initiate delisting, employing the same risk-assessment standards and procedures used in the decision to list the species.[32] The Act’s drafters also appear to have assumed that after delisting the species would thrive with only existing management, such as state fish and game laws.

Implementing the Act has proved more complex—as the tale of the Borax Lake chub demonstrates.

III.

In 1980, as the paper characterizing the chub as a new species was in the editorial process,[33] two activities around Borax Lake were imperiling the species’s continued existence. First, the rancher who owned the lake and the surrounding 160 acres cut channels into its perimeter to irrigate forage on his land.[34] In addition to lowering the lake level, the channels redirected the flow of water from the lake’s natural outflow, drying up the wetlands and Lower Borax Lake.[35] Second, the agency that managed the federal land adjacent to the lake, the Bureau of Land Management (BLM), began the process of issuing leases to permit the geothermal development of the Alvord Basin.[36]

In response to BLM’s proposal to lease 6789 acres surrounding Borax Lake for geothermal exploration and testing, the United States Fish and Wildlife Service (FWS) promulgated an emergency regulation listing the chub as an endangered species on May 28, 1980.[37] The agency’s rationale for listing the species focused on the threats to its habitat. The lake’s “position above the valley floor,” FWS noted, made it vulnerable to the irrigation diversions that both lowered the level of the lake and diverted water away from the natural outflow.[38] Geothermal exploration also threatened the species given the potential changes to the subsurface flow of water in the aquifer that fed the lake.[39] The listing was necessary, the agency concluded, to ensure that BLM considered “the welfare of this species during its deliberations” on both the leasing decision and the stipulations that would be included in any leases that it might eventually issue.[40]

With the listing of the species, the Act’s extinction prevention and recovery action provisions became applicable. The extinction prevention requirements came into play first given their prohibitory orientation.[41] The Act requires any federal agency whose actions are likely to affect a listed species to consult with the appropriate federal wildlife agency—in the case of the chub, FWS—to “insure” that the action “is not likely to jeopardize the continued existence of [the species] . . . or result in the destruction or adverse modification” of the species’s critical habitat.[42] Because the exploration activities permitted by proposed geothermal exploration leases could affect the chub, BLM requested formal consultation with FWS on July 3, 1980.[43] Following several exchanges of documents and a meeting in September that was attended by FWS, the United States Geological Survey, BLM, Anadarko Production Company, Getty Oil, several state agencies, two private utilities, “and various environmental and engineering consulting firms,”[44] FWS issued a biological opinion (BiOp) evaluating the risk the leasing action posed to the chub.[45] The BiOp concluded that granting “geothermal exploration leases, with present stipulations, for BLM Leasing Units 28, 33 and 34 is likely to jeopardize the continued existence of the Borax Lake chub and/or adversely modify its critical habitat.”[46]
“[T]he key issue of concern,” the BiOp noted, “is the likelihood that drilling activity might impact th[e] fault system” beneath the basin floor that is the source of both the thermal springs that feed the lake and the cold water aquifer that reduces the temperature of the springs to a range that the chub can withstand.[47]

When FWS issues a “jeopardy” opinion, the ESA requires the agency to provide “reasonable and prudent alternatives” to the action that would permit it to proceed without jeopardizing the species.[48] At the September meeting, the participants agreed that a half-mile buffer around the lake and the associated hot springs “would probably provide adequate protection to the aquifers.”[49] FWS therefore recommended that any leases include a half-mile buffer.[50] In addition, the agency proposed at least weekly monitoring of the quantity and quality of the water issuing from the springs within the buffer zone and a mandatory shutdown if any changes to either quality or quantity were detected.[51] BLM adopted these recommendations as stipulations on the leases it subsequently issued to Anadarko.[52]

An emergency listing is effective for only 240 days.[53] In mid-October 1980, FWS therefore initiated procedures to list the chub as endangered.[54] That listing was finalized nearly two years later on October 5, 1982.[55] In its decision, the agency concluded that irrigation diversions and potential geothermal development continued to be the most significant threats to the species.[56] Although no new diversions had been made since 1980, the original diversions remained a threat because there were no legal prohibitions on diverting water from the lake.[57] Similarly, the threat from drilling had been reduced by the stipulations but not eliminated.[58] Finally, the agency noted that the existing regulatory mechanisms were also inadequate: Although the species was on the Oregon endangered species list, the state had taken no steps either to protect its habitat or the water in the lake.[59]

With the listing of the chub, designation of its critical habitat, and the corralling of the immediate threats associated with geothermal leasing, conservation of the species entered a new phase.

IV.

As noted, the ESA seeks to do more than prevent extinction. The Act also requires all federal agencies to use their authorities to recover listed species.[60] To guide these conservation actions, the responsible federal wildlife agency is required to develop and implement a plan to recover the species.[61] Unlike the Act’s extinction-prevention provisions, recovery actions are intended to increase the viability of the species; recovery planning and implementation, in other words, is the element of the statutory scheme that details the types of actions necessary to accomplish the Act’s ultimate objective of conserving listed species and their ecosystems. As the FWS guidelines for recovery planning state, “Recovery is the process by which the decline of [a listed] species is arrested or reversed, and threats to its survival are neutralized, so that its long-term survival in nature can be ensured.”[62]

The recovery planning guidelines suggest that the plans be drafted by scientists who are familiar with the species.[63] Plans are required to analyze the threats facing the species and determine the actions necessary to remove or mitigate those threats to the point at which the risk to the species has been reduced to an acceptable level.[64] The development of a recovery plan thus requires an analysis of the species, its life history, and the threats it faces, and a determination of the actions necessary to mitigate those threats to the point at which the risk to the species has been diminished to an acceptable level.[65]

V.

It was a nongovernmental organization (NGO), The Nature Conservancy (TNC), that took the first steps to conserve the chub. In 1983, it acquired a ten-year lease of the 160 acres of private land that bounded the lake; the lease included a right of first refusal for the purchase of the property.[66] TNC, however, agreed to allow continued water diversions from the lake and cattle grazing on the surrounding land.[67] Shortly after acquiring the lease, the organization began steps to return the outflow of Borax Lake into its former, natural channel in order to rehydrate the wetlands and increase available habitat for the species.[68] This proved far more difficult than expected; work continued through 1985 before flows approximating the pre-1980 conditions were restored and the wetlands were again wet.[69]

Also in 1983, BLM designated the 520 acres of federal land around Borax Lake an Area of Critical Environmental Concern (ACEC).[70] An ACEC is the most restrictive land-use category under the Federal Land Policy and Management Act[71] short of wilderness designation. ACECs are parcels “where special management attention is required . . . to protect and prevent irreparable damage to important historic, cultural, or scenic values, fish and wildlife resources or other natural systems or processes.”[72] The management standards incorporated into the Borax Lake ACEC when it was designated are designed to control vehicular access to the lake.[73]

FWS did not finalize a recovery plan for the species until 1987.[74] As required by the guidelines, the plan described the chub, its habitat, and the threats it and its habitat faced.[75] The plan focused on three threats: the modification of the lake and its natural outflow as a result of irrigation diversions, the risk of altering subsurface water flows that would impact the lake as a result of geothermal development, and the negative impacts of off‑highway vehicle (OHV) use.[76] Since the threats facing the chub had not caused its population to decline, “maintenance of a certain number of individuals is not as relevant to the survival of the Borax Lake chub as is protection of the integrity of the aquifer and shoreline.”[77] The plan thus emphasized securing habitat protection: acquiring land and water rights,[78] restoring Lower Borax Lake and the intervening marshes, protecting the lake’s ecosystem (primarily through restriction of access), monitoring the status of that ecosystem, encouraging public support through education, and utilizing laws and regulations to protect the chub and its habitat.[79]

Completion of the recovery plan framed the tasks facing the entities acting to conserve the species. The federal land-management agency took steps both to ameliorate the immediate threats to the species from geothermal exploration and to ensure that the lands surrounding the lake would receive special attention.[80] In addition, a national conservation NGO took steps to acquire the lake and the private lands around it.[81] FWS concluded, however, that these actions were insufficient to justify either downlisting the species to threatened or delisting it.[82]

VI.

In 2003, FWS contracted with Southern Oregon University for a review of the progress being made to meet the chub’s recovery goals.[83] The resulting report noted, “Numerous recovery measures have been implemented during the past two decades that have improved the conservation status of the Borax Lake chub and protection of its habitat.”[84] These included the designation of critical habitat; BLM’s designation of the federal lands around Borax Lake as an ACEC; the TNC lease and subsequent purchase in 1993 of both the private parcel surrounding the lake and another, adjacent parcel; and the adoption of the Steens Mountain Cooperative Management and Protection Act of 2000.[85] The Steens Mountain Act withdrew the public lands (including the Alvord Basin Known Geothermal Resource Area) from mineral and geothermal development.[86] The report also noted, however, that all was not well: Gates on the access road to the lake were unlocked, and there was evidence of “significant recreational use,” including motorcycle and OHV damage to the salt crusts within the ACEC west of the lake[87] and disturbance to the lake bed from people wading in it.[88]

Table 1: Numerical Scores for Recovery Goals[89]

 

 1. Securing Land and Water Rights2. Restoring Lower Borax Lake and the Intervening Marshes

3. Protecting the Lake’s Ecosystem

4. Monitoring the Status of the Ecosystem

5. Encouraging Public Support Through Public Awareness

6. Using Laws and Regulation to Protect the Chub and Its Habitat

 

Overall Average:

 

Key:

0 = no implementation

1 = minor implementation

2 = approximately half implemented

3 = mostly implemented

4 = fully implemented

3.7

4.0

2.7

2.3

3.5

2.5

3.1

 

The report’s authors evaluated the status of the chub against two standards. First, they assigned a numerical value to reflect the degree of implementation of each of the 1987 recovery plan’s six goals (see Table 1).[90] In addition to the numerical evaluation, the report’s authors evaluated the chub’s status in relation to the ESA’s list of threat factors. The report noted that, although the original threats of diversions of water from the lake for irrigation and the geothermal development had been removed,[91] OHV and recreational use posed new threats, including “damage to soils, wetlands, and lake shoreline from off-highway vehicles, and impacts to water quality, lake substrates, and lake shorelines [from] wading, camping, and boating.”[92] Similarly, although disease and predation had not been a threat to the species in 1982, by 2003 “increased vehicle access and visitation [made] the introduction of non-native species an increasing concern.”[93] Finally, the report’s authors noted that the chub’s restricted range meant that it was “vulnerable to loss from a single disturbance,” which “could take the form of vandalism, introduction of non-native species, or collapse of the lake shoreline.”[94] Nonetheless, the report was broadly optimistic: “With acquisition of private lands including Borax Lake by The Nature Conservancy, careful management of the rest of the critical habitat by the BLM, and passage of the Steens Mountain legislation, the Borax Lake chub appears to be nearing recovery.”[95]

FWS convened an expert panel of eight scientists to evaluate the report.[96] The panel agreed that, despite the “[s]ubstantial” progress that had been made, “threats to the species and ecosystem remain.”[97] Given these threats—increased recreational use and the potential for the introduction of nonnative species—the panel concluded that the chub remained endangered and no change in listing status was warranted.[98] Echoing the report’s authors, the panel concluded, “Because of the restricted range of the Borax Lake chub to a single area, the species is vulnerable to catastrophic loss despite existing protection.”[99]

The recommendations of both the report’s authors and the expert panel neither to delist nor to reclassify the species raises a crucial issue: What is recovery?

VII.

The Act’s linear structure—a procedure that leads from listing through risk management (i.e., the extinction prevention and recovery action provisions) to delisting as a “secure, self‑sustaining wild population[] of species”[100]—suggests that its drafters assumed that the threats facing a species could be eliminated and, with the elimination of those threats, the species’s population would rebound so that it could be delisted and thrive without species-specific conservation management.[101] These assumptions have proved accurate for some species.

The Aleutian cackling goose (Branta hutchinsii leucopareia), for example, was listed as a result of population declines primarily caused by the introduction of foxes onto its nesting islands.[102] Removal of the foxes from these islands and hunting closures on the species’s wintering grounds in Oregon and California allowed the species’s population to climb from
790 individuals in 1975 to 36,978 in 2000.[103] This population increase met the species’s demographic recovery goals.[104] Indeed, the species is something of a poster child for recovery; its population has increased to the point that it has become an agricultural pest with its own depredation program.[105]

Other species have followed the same path to recovery. The American peregrine falcon (Falco peregrinus anatum), for example, was imperiled by exposure to organochlorine pesticides such as dichlorodiphenyltrichloroethane (DDT).[106] Following listing, the banning of DDT, and the implementation of an intensive reintroduction program, the species was reestablished in areas from which it had been extirpated.[107] Similarly, the gray whale (Eschrichtius robustus) and the American alligator (Alligator mississippiensis) had been hunted nearly to extinction;[108] following listing and prohibitions on taking the species, their populations recovered.[109]

But recovery is not exclusively a question of numbers. The demographic targets in recovery plans are in fact surrogates, a handy way to indirectly measure the actual goal.[110] Under the ESA, that goal is the amelioration or elimination of the threats that led to the species’s listing.[111] As FWS and the National Oceanic and Atmospheric Administration’s National Marine Fisheries Service have noted, “[R]ecovery is not attained until the threats to the species as analyzed under section 4(a)(1) of the Act have been removed.”[112] The goose’s dramatic population increase (nearly 4700%) is a handy measure of the elimination of the threat facing the species, but it is the elimination of the threat—predation by a nonnative species—rather than the population increase itself that is the actual legal requirement.

This raises a further point. The statutory list of threat factors contains two different types of threats. The first are those that directly drive a species’s demographics: habitat loss, overutilization, and disease or predation.[113] Ameliorating these threats on a scale that is biologically relevant to a species will generally lead to increased—or at least stabilized—population. This was the case with the goose: Foxes were removed from the islands on which it bred and the species’s population increased.[114] The second type of threat, on the other hand, focuses not on the drivers of extinction, but on the law that is available to ameliorate or eliminate those drivers: Are there adequate “existing regulatory mechanisms” to address the biological threats to the species?[115]

Although decisions to delist a species are governed by the same substantive, evidentiary, and procedural requirements as listing decisions,[116] the fact that delisting a species removes the ESA’s protections is significant. At delisting, the question of the adequacy of existing regulatory mechanisms focuses on whether the change in the species’s legal status from listed to delisted will place it at risk of extinction.[117] To delist a species, in other words, requires reasonable assurances that the delisting itself will not deprive the species of the species-specific protection it requires.

As noted, the goose is a weedy species that has become an agricultural nuisance.[118] To the extent that the species requires post-delisting protection, it is provided by a preexisting monitoring and management structure under the Migratory Bird Treaty Act (MBTA).[119] Falcons also thrive in anthropogenic landscapes, having taken up residence in most major U.S. cities where tall buildings substitute for traditional cliffs and pigeons are an abundant prey species.[120] The peregrine is also subject to a comprehensive monitoring and management system under the MBTA’s falconry provisions.[121] Similarly, the overharvesting that led to listing the gray whale and the American alligator is a threat that is being managed after delisting through traditional federal and state take prohibitions under existing monitoring and enforcement mechanisms.[122]

These species share at least three crucial characteristics: their decline was primarily a result of a specific, eliminable threat;[123] the risk management necessary to delist the species after its population recovered is provided by existing regulatory mechanisms that provides species-specific monitoring and management, often because the species is charismatic;[124] and—the factor that may have trumped the rest—the species are habitat generalists that can flourish in human-impacted environments.[125]

VIII.

Most species do not fit this pattern. They have not been pushed to the edge of extinction by an eliminable threat. Instead, the most common threats facing at-risk species are habitat degradation and the predation or competition of invasive species.[126] One study, for example, found that sixty percent of the listed species in the United States are imperiled by either disruption of natural fire disturbance regimes or the spread of nonnative species.[127] Such threats generally cannot be eliminated. A natural fire regime, for example, cannot be reintroduced into the scattered jack pine (Pinus banksiana) stands of the Midwest.[128] As a general rule, such threats can only be managed—rather than eliminated—because they require ongoing human intervention.[129]

Robbins’ cinquefoil (Potentilla robbinsiana), for example, is a long‑lived, dwarf member of the rose family.[130] Although never abundant, the  species had been reduced to a single site—Monroe Flats—in New Hampshire when it was listed in 1967.[131] This population was at risk of extinction because the Appalachian Trail crossed Monroe Flats and the species was literally being trampled into extinction by hikers.[132] Following listing, FWS prepared a recovery plan to address the threats the species faced by protecting the existing colony on Monroe Flats[133] and by establishing additional self-sustaining populations.[134] By 2002, FWS concluded that the species had met its demographic targets: The Monroe Flats colony’s population had increased more than 800% and there were three separate, additional populations.[135]

Although the cinquefoil’s population and distribution had achieved the point at which it was no longer demographically at risk in the foreseeable future, the threats it faced from trampling could not be eliminated short of closing a section of the Appalachian Trail. Ameliorating the threat of trampling thus differs from removing relatively large predators (foxes) from relatively small islands, or removing DDT from the market. Hikers will require continuing monitoring and management to keep them on the path.[136] FWS responded to this problem by creating a conservation management structure to provide ongoing risk management after the cinquefoil was delisted.[137]

Both the landowner (the United States Forest Service (USFS)) and a recreational organization (the Appalachian Mountain Club (AMC)) actively participated in recovering the species by providing “stewardship, enforcement, and educational resources on site.”[138] In preparation for delisting, FWS secured agreements with both entities to continue their monitoring and management activities.[139] AMC agreed to station a naturalist at the Lake of the Clouds Hut near Monroe Flats during the summer.[140] The naturalist provides educational outreach and, along with other staff at the hut, monitors the cinquefoil population for human impacts.[141]

FWS and USFS entered into a formal memorandum of understanding (MOU) that memorialized the agencies’ “long-term commitment to conservation of this important plant species.”[142] The short document (less  than 2.5 pages) did four important things. First, FWS agreed to maintain the Monroe Flats habitat, “vigorously protect[]” the species from take through human disturbance, train personnel, and provide educational and interpretational information to visitors to the forest.[143] Second, the MOU established an “Oversight Committee” composed of FWS and USFS representatives.[144] Third, the MOU directed the Committee to initiate a long‑term monitoring program to assess the species’s stability and recruitment.[145] Finally, the MOU established a process under which the Committee “render[s] opinions and recommendations” on any proposed activity that may affect the species or its habitat; these opinions and recommendations must be “considered” by USFS in making decisions on whether to proceed with the proposed activity.[146]

A second example is the Columbian white-tailed deer (Odocoileus virginianus leucurus). Originally common in the bottomlands of the Willamette, Umpqua, and lower Columbia River basins in western Oregon and southwestern Washington, by the early 1900s the species had been reduced to two disjunct populations: one along the lower Columbia River and the other in Douglas County in southern Oregon.[147] Like the goose, the species was listed as endangered in 1967.[148] By 2002, the Douglas County population had grown from an estimated 500 animals in 1970 to about
6070 animals.[149] Since the Columbia River population had not recovered, FWS  designated the two populations “distinct population segments” (DPSs)[150] and delisted the Douglas County DPS as recovered.[151]

Post-delisting risk management is more complicated for the deer. Like  many species at risk of extinction, the deer occurs in a fragmented matrix of public and private lands that are owned by multiple landowners.[152] Such landscapes present complex management problems that will often require a variety of regulatory mechanisms. Managing habitat in such landscapes is significantly different than removing a predator or a poison; even if lands are set aside permanently, addressing habitat loss requires ongoing monitoring and management if the land is to continue to meet the species’s needs. More importantly, there were no existing regulatory mechanisms (such as the MBTA[153]) that could be used to manage habitat for the deer.

FWS addressed this need for additional protection by requiring at least 5000 acres of “secure habitat” as a recovery goal.[154] The agency defined this requirement as “areas that are protected from adverse human activities . . . in the foreseeable future, and that are relatively safe from natural phenomena that would destroy their value to the subspecies.”[155] This standard has both a legal and a biological component: The habitat must be legally protected against adverse human actions, and it must continue to provide the biological requirements of the species.

The requisite legal security can be obtained, the agency concluded, through a variety of regulatory mechanisms that ranged from ownership to land-use controls.[156] At one end of the continuum is obtaining interests in land such as “easements, leases, acquisitions, donations, or trusts” by public entities or conservation NGOs.[157] At the other end of the continuum are use restrictions on privately-owned land imposed through instruments such as “zoning ordinances, land-use planning, parks and greenbelts, agreements, memoranda of understanding, and other mechanisms available to local jurisdictions.”[158]

The most significant recovery action was BLM’s acquisition of a 6581‑acre ranch as habitat for the deer.[159] Following the acquisition of the North Bank Habitat Management Area (NBHMA), BLM designated ninety‑five percent of the land as an ACEC.[160] In addition, Douglas County received a bequest of 1100 acres of ranch land that was to be managed “as a wildlife refuge and working ranch.”[161]

Simply setting aside habitat, however, is insufficient; there must also be legal assurances that that habitat will be managed so that it continues to meet the biological needs of the species. The management plan BLM adopted for the NBHMA “provides for the protection and enhancement of habitat for the Columbian white-tailed deer”;[162] it emphasizes “active management to maintain or enhance habitat [through] the use of prescribed fire, grazing, fertilization, seeding, planting forage plots and mowing.”[163] The plan includes both a monitoring and research program to ensure that the area continues to meet the species’s biological needs.[164] Both FWS and the Oregon Department of Fish and Wildlife are cooperating agencies on the management plan.[165]

The examples of post-delisting management agreements can be expanded. Eggert’s sunflower (Helianthus eggertii) is found on rolling to flat uplands in Alabama, Kentucky, and Tennessee, a barren habitat that “is disappearing from the south-central United States at a rapid rate.”[166] Given the threats the species faces—encroachment both by other plants and by commercial, residential, or industrial development—”[a]ctive management is required to ensure that Eggert’s sunflower continues to survive at all sites.”[167] Reasonable assurances that the necessary management was available came from a variety of management agreements: Two federal entities—Arnold Air Force Base and the National Park Service—signed Cooperative management agreements with FWS,[168] and two state agencies—the Kentucky Transportation Cabinet and the Tennessee Wildlife Resources Agency—signed management agreements to enhance and monitor populations on state lands that they manage.[169] The Nature Conservancy also entered into a management agreement.[170]

Hoover’s woolly-star (Eriastrum hooveri) is an annual herb in the phlox family that grows in the San Joaquin and Cuyama Valleys in California, an area that has undergone intense land conversion and urbanization; oil, gas, and agricultural development presented significant risks to the species when it was listed as threatened in 1990.[171] In response to the listing, approximately 286,000 acres containing four metapopulations were included in a variety of protected statuses: two BLM ACECs, the Carrizo Plain National Monument, four California Department of Fish and Game Ecological Reserves, and four privately owned mitigation sites.[172] Ongoing conservation management was secured through BLM designation of the plant as a “sensitive species,”[173] which requires that it be addressed in all National Environmental Policy Act[174] documents.[175] BLM also agreed to “ensure that actions they authorize, fund, or carry out do not contribute to the need to relist the species.”[176] The  combination of conservation management agreements led FWS to conclude that “management practices of, and commitments by, the U.S. Bureau of Land Management . . . , on whose land a substantial number of new populations have been found, will afford adequate protection to the species upon delisting.”[177]

As the cinquefoil, the deer, and the woolly-star demonstrate, there is no specifically targeted legal protection for most species other than the ESA.[178] Conserving such species requires the creation of specific management protocols. This is the irony of the ESA. It is a powerful statute that can bring species back from the brink of extinction—but its power often makes the Act irreplaceable. Other than the ESA itself, neither federal nor state law provides similar species-specific protection against threats that most species face—habitat degradation from human activities and competition from nonnative species.[179] For example, rats, mongooses, feral cats, and dogs cannot be removed from the Hawaiian Islands where they have endangered species such as the Hawaiian moorhen (Gallinula chloropus sandvicensis).[180] Unlike the recovery of the goose—which involved a relatively large predator (foxes) on relatively small and barren islands[181]—removal of the moorhen’s predators is impossible given the size of the Hawai’ian Islands. Conservation of species such as the moorhen requires continuing monitoring and management. Such species are conservation reliant.[182]

The cinquefoil, the deer, and the woolly-star are examples of conservation-reliant species that have been recovered and delisted despite their need for continuing conservation management. To date, however, such delistings have been ad hoc, the result of crafting individualized conservation management agreements.

IX.

The Borax Lake chub is an example of a conservation-reliant species and of the management issues such species present. The chub is neither at risk of extinction due to a threat that can be eliminated, nor is there an existing regulatory mechanism to monitor and manage the species if it were delisted. Instead, the chub remains at risk of extinction from habitat degradation caused by increased human recreational use and the potential for the introduction of nonnative species.[183] What might a conservation management agreement (CMA) for the chub look like?

In its consensus findings on the conservation status of the Borax Lake chub, the expert panel convened by FWS provided a detailed discussion of both the threats facing the species and the steps necessary to manage those threats.[184] The discussion offers a description of the components that would be required for a CMA for the species.

The panel focused on the four threats facing the species: recreation, nonnative species, groundwater withdrawals, and the species’s restricted range.[185] Its mitigation proposals take on a repetitive cadence: monitoring, access restrictions, and education.[186] Field visits to the lake had found gates unlocked, off-highway vehicle use within the critical habitat (with a resulting degradation of the area), and a lack of signs explaining the area’s sensitivity.[187] To determine the timing of use, types of visitors, and their impacts on the ecosystem, the panel proposed an extensive monitoring program that included quarterly site visits to monitor the physical integrity of the site; annual fish, invertebrate, and water quality monitoring; visitor use monitoring; and annual evaluation of the collected data.[188] The panel also recommended research to determine the risk to the lake’s ecosystem from potential groundwater development in the basin.[189] It advocated eliminating vehicle use of the area around the lake and boat access to the lake.[190] The  panel also proposed an educational program to inform visitors of “the unique and fragile features of the ecosystem” and minimize the threat of nonnative species.[191]

The panel’s discussion outlines what would be required for post‑delisting management: restrictions on vehicular access, an educational campaign to inform visitors of the site’s fragility, and a monitoring program sufficient to alert managers to any changes in the biotic or abiotic environment.[192] These actions are not dependent upon the ESA; as the
land-managing agency and the landowner, BLM and The Nature Conservancy (TNC) have the ability to control vehicular and individual access to the lake and its surroundings.[193] The agencies can also provide interpretative signage at the site. Finally, TNC and BLM have the expertise necessary to develop and implement a monitoring program.[194] A CMA could be drafted that would ensure that these actions were implemented, and that FWS would be kept apprised of the results of the monitoring program.

But, as the panel noted, although frequent monitoring can reduce the threats, the chub’s vulnerability “cannot be eliminated”[195]—a statement that could be made about most species which face threats that can at best be managed rather than eliminated.

X.

The Borax Lake chub is a window to the future. A recent conservative estimate placed the actual number of at-risk species in the United States at between 14,000 and 30,000 species—approximately seven to eighteen percent of the nation’s animals, plants, and fungi.[196] Given our species’s increasing numbers and appetites—which are reflected in and compounded by global climate change—even now-common species are likely to become endangered within the foreseeable future. If there is any hope to avoid a calamitous loss of biodiversity, it is no longer possible to simply let nature take its course. Conservation reliance and the need for ongoing conservation management is the new norm.

We have become nature and must accept the responsibilities that come with the role.

 



* 2008–2009 Distinguished Environmental Law Scholar, Lewis and Clark School of Law; Margaret Wilson Schimke Distinguished Professor of Law, University of Idaho. My thanks to Lewis and Clark for a congenial environment within which to write, and to J. Michael Scott, Susan Kilgore, and Carmen Thomas-Morse for their close reading of the manuscript. This Essay was partially funded by a University of Idaho College of Law summer research stipend.

[1] The discussion of the biology of the species and the physical description of its habitat are based on Jack E. Williams, U.S. Fish & Wildlife Serv., U.S. Dep’t of the Interior, Recovery Plan for the Borax Lake Chub, Gila boraxobius 4 (1987), available at http://ecos.fws.gov/ docs/recovery_plan/060619.pdf; Endangered Status and Critical Habitat for Borax Lake Chub (Gila boraxobius), 47 Fed. Reg. 43,957, 43,957 (Oct. 5, 1982) (codified at 50 C.F.R. pt. 17); Proposed Endangered Status and Critical Habitat for Borax Lake Chub (Gila boraxobius), 45 Fed. Reg. 68,886, 68,886 (proposed Oct. 16, 1980) (to be codified at 50 C.F.R. pt. 17); Emergency Determination of Endangered Status and Critical Habitat for the Borax Lake Chub, 45 Fed. Reg. 35,821, 35,821 (May 28, 1980); U.S. Fish & Wildlife Serv., U.S. Dep’t of the Interior, Borax Lake Chub: Gila boraxobius, http://ecos.fws.gov/docs/life_histories/E027.html (last visited April 18, 2010); U.S. Geological Survey, U.S. Dep’t of the Interior, Status of Listed Species
and Recovery Plan Development: Borax Lake Chub: Gila boraxobius—Endangered, http://www.npwrc.usgs.gov/resource/wildlife/recoprog/states/species/gilabora.htm (last visited April 18, 2010).

[2] U.S. Fish & Wildlife Serv., supra note 1.

[3] Id.

[4] Id.

[5] Williams, supra note 1, at 6, 9; U.S. Fish & Wildlife Serv., supra note 1.

[6] 47 Fed. Reg. at 43,957; 45 Fed. Reg. at 68,886; 45 Fed. Reg. at 35,821; Williams, supra note 1, at 8; U.S. Fish & Wildlife Serv., supra note 1.

[7] 47 Fed. Reg. at 43,958; 45 Fed. Reg. at 68,886; 45 Fed. Reg. at 35,822; Williams, supra note 1, at 9.

[8] Williams, supra note 1, at 8–9; U.S. Fish & Wildlife Serv., supra note 1.

[9] Williams, supra note 1, at 17; U.S. Fish & Wildlife Serv., supra note 1.

[10] U.S. Fish & Wildlife Serv., supra note 1.

[11] Id.

[12] Williams, supra note 1, at 5–6.

[13] Id.

[14] Id. at 6.

[15] Id.

[16] Id. at 1, 3.

[17] Id. at 1, 6–8.

[18] Endangered Species Act of 1973, 16 U.S.C. §§ 1531–1544 (2006).

[19] Id. § 1531(b). For a more extended discussion of the ESA, see Dale D. Goble, The Endangered Species Act: What We Talk About When We Talk About Recovery, 49 Nat. Resources J. (forthcoming 2010) (on file with author).

[20] 16 U.S.C. § 1532(3) (2006).

[21] See J. Michael Scott et al., Introduction to 1 The Endangered Species Act at Thirty: Renewing the Conservation Promise 11 (Dale D. Goble et al. eds., 2006).

[22] The two agencies are the United States Fish and Wildlife Service (FWS) in the United States Department of the Interior, and the National Oceanic and Atmospheric Administration’s National Marine Fisheries Service (NOAA Fisheries) in the United States Department of Commerce. See
16 U.S.C. § 1532(15) (2006) (delegating implementation power to the Departments of Interior and Commerce); see also Craig N. Johnston et al., Legal Protection of the Environment 602 (2d ed. 2007) (discussing implementation of the ESA by FWS and NOAA Fisheries). FWS is the agency responsible for managing the chub. See 50 C.F.R. § 17.11 (2008). See generally id. § 17.2 (explaining relationship over management of listed species between the two agencies).

[23] 16 U.S.C. § 1532(6) (2006).

[24] Id. § 1532(20) (emphasis added).

[25] Id. § 1533(b)(1)(B)(ii).

[26] Id.; see Goble, supra note 19 (manuscript at 2). In developing guidance for listing and delisting species, the United States Fish and Wildlife Service has labeled these two components of risk as “magnitude” (either high or moderate to low) and “immediacy” (either imminent or nonimminent). Endangered and Threatened Species Listing and Recovery Priority Guidelines, 48 Fed. Reg. 43,098, 43,102–03 (Sept. 21, 1983). For a discussion on the vagueness in such standards, see generally Helen M. Regan et al., A Taxonomy and Treatment of Uncertainty for Ecology and Conservation Biology, 12 Ecological Applications 618, 621–22 (2002).

[27] 16 U.S.C. § 1533(a)(1)(A)–(E) (2006).

[28] Id. § 1533(c)(1).

[29] See, e.g., id. § 1536 (“All other Federal agencies shall, in consultation with and with the assistance of the Secretary, utilize their authorities in furtherance of the purposes of this chapter by carrying out programs for the conservation of endangered species and threatened species listed pursuant to section 1533 of this title.”); id. § 1533(f)(1) (“The Secretary shall develop and implement plans . . . for the conservation and survival of endangered species and threatened species listed pursuant to this section . . . .”).

[30] There are two primary extinction prevention tools: the consultation requirements of section 7 of the ESA, id. § 1536(a)–(d), and the take prohibition of section 9, id. § 1538(a)(1)–(2).

[31] Recovery actions are a much more heterogonous collection of tools than extinction prevention tools. Recovery actions include 1) recovery planning requirements, id. § 1533(f), 2) the broad delegation of power contained in the definition of “conservation,” which authorizes the use of “all activities associated with scientific resources management,” id. § 1532(3), 3) the authority to acquire lands and waters “by purchase, donation, or otherwise,” id. § 1534(a)(2), 4) the (under-enforced) affirmative obligation imposed on all federal agencies, id. § 1536(a)(1), 5) the authority to issue recovery permits, id. § 1539(a)(1)(A), 6) the experimental populations provision, id. § 1539(j), and 7) the obligation to designate critical habitat, id. § 1533(a)(3). The consultation mandate also has a recovery element because a proposed action’s impact on a species’s recovery is a basis for a jeopardy or adverse effect determination. See Gifford Pinchot Task Force v. U.S. Fish & Wildlife Serv., 378 F.3d 1059, 1069–70 (9th Cir. 2004) (“The agency’s controlling regulation on [destruction or adverse modification of] critical habitat thus offends the ESA because the ESA was enacted not merely to forestall the extinction of species (i.e., promote a species survival), but to allow a species to recover to the point where it may be delisted.”).

[32] As several courts have noted, “‘Since the same five statutory factors must be considered in delisting as in listing, the Court necessarily concludes that the FWS . . . must address each of the five statutory delisting factors and measure whether threats to the [species] have been ameliorated.’” Defenders of Wildlife v. Babbitt, 130 F. Supp. 2d 121, 133 (D.D.C. 2001) (quoting Fund for Animals v. Babbitt, 903 F. Supp. 96, 111 (D.D.C. 1995)); see also Nat’l Wildlife Fed’n v. Norton, 386 F. Supp. 2d 553, 558 (D. Vt. 2005).

[33] See Jack E. Williams & Carl E. Bond, Gila boraxobius, A New Species of Cyprinid Fish from Southeastern Oregon with a Comparison to G. alvordensis Hubbs and Miller, 93 Proc. Biological Soc’y Wash. 291 (1980).

[34] Proposed Endangered Status and Critical Habitat for Borax Lake Chub (Gila boraxobius), 45 Fed. Reg. 68,886, 68,886 (proposed Oct. 16, 1980) (to be codified at 50 C.F.R. pt. 17); Williams, supra note 1, at 18.

[35] 45 Fed. Reg. at 68,886.

[36] Emergency Determination of Endangered Status and Critical Habitat for the Borax Lake Chub, 45 Fed. Reg. 35,821, 35,822 (May 28, 1980) (codified at 50 C.F.R. pt. 17).

[37] Id. at 35,821. On the Secretary’s authority to make emergency listings, see Endangered Species Act of 1973, 16 U.S.C. § 1533(b)(7) (2006).

[38] 45 Fed. Reg. at 35,822.

[39] Id.

[40] Id. Geothermal exploration threatened to adversely modify the designated habitat through subsidence (from removing water from the aquifer) and alteration of the thermal springs’ flows. Id. at 35,822–23. Geothermal resource development—if it were to follow exploration—threatened additional adverse impacts. Id. Finally, the agency also designated 3840 acres of critical habitat surrounding the lake. Id. at 35,822.

[41] See supra note 30 and accompanying text.

[42] 16 U.S.C. § 1536(a)(2)–(3) (2006).

[43] Memorandum from L.A. Mehrhoff, Area Manager, U.S. Fish & Wildlife Serv., to State Dir., Bureau of Land Mgmt. 22 (Oct. 10, 1980) (regarding Formal Section 7 Consultation for BLM Geothermal Leasing Units 28, 33, and 34 near Borax Lake, Oregon).

[44] Id. at 22–23.

[45] Id. at 22.

[46] Id. at 23.

[47] Id. at 27.

[48] Endangered Species Act of 1973, 16 U.S.C. § 1536(b)(3)(A) (2006).

[49] Memorandum from L.A. Mehrhoff to State Dir., supra note 43, at 27.

[50] Id. at 28.

[51] Id. at 28–29.

[52] FWS relied upon inclusion of the stipulations in subsequently adjusting the boundaries of critical habitat to reduce the area from the 3840 acres designated in the emergency listing to 640 acres. Endangered Status and Critical Habitat for Borax Lake Chub (Gila boraxobius), 47 Fed. Reg. 43,957, 43,957–59 (Oct. 5, 1982) (codified at 50 C.F.R. pt. 17).

[53] 16 U.S.C. § 1533(b)(7) (2006).

[54] Proposed Endangered Status and Critical Habitat for Borax Lake Chub (Gila boraxobius), 45 Fed. Reg. 68,886, 68,886 (proposed Oct. 16, 1980) (to be codified at 50 C.F.R. pt. 17).

[55] 47 Fed. Reg. at 43,957. The listing came after Anadarko Production Company, the lessee of the BLM lease units, filed a plan of operation—the document that initiates the post-leasing, exploratory phase—for one of the leases in March 1982. See Williams, supra note 1, at 21.

[56] 47 Fed. Reg. at 43,958.

[57] See id.

[58] Id.

[59] Id.

[60] Endangered Species Act of 1973, 16 U.S.C. § 1536(a)(1) (2006).

[61] Id. § 1533(f). On recovery plans, see generally Dale D. Goble, Recovery, in Endangered Species Act: Law, Policy, and Perspectives 70, 79–85 (Donald C. Baur & Wm. Robert Irvin eds., 2d ed. 2010) (evaluating the statutory and case law on recovery planning).

[62] U.S. Fish & Wildlife Serv., U.S. Dep’t of the Interior, Policy and Guidelines for Planning and Coordinating Recovery of Endangered and Threatened Species 1 (1990), available at http://www.fws.gov/endangered/pdfs/recovery/90guide.pdf.

[63] Id. at 6, app. II, at II-1 to -2.

[64] The plan itself must contain three types of information. The first is a summary of what is known about the species, including its distribution, habitat, and life history, and the threat factors that prompted its listing. Id. app. I, at I-9 to -10. The second section contains the criteria for determining when the species is recovered. Id. app. I, at I-11 to -13. Finally, the plan details the actions required to address the threats to the species and an implementation schedule for the actions needed to meet the plan’s objectives. Id. app. I, at I-14 to -20.

[65] Recovery planning has been widely criticized. See generally Theodore C. Foin et al., Improving Recovery Planning for Threatened and Endangered Species: Comparative Analysis of Recovery Plans Can Contribute to More Effective Recovery Planning, 48 BioSci. 177, 177 (1998); Peter M. Kareiva, Applying Ecological Science to Recovery Planning, 12 Ecological Applications 629, 629 (2002); Douglas W. Schemske et al., Evaluating Approaches to the Conservation of Rare and Endangered Plants, 75 Ecology 584, 584 (1994); Timothy H. Tear
et al., Status and Prospects for Success of the Endangered Species Act: A Look at Recovery Plans, 262 Sci. 976, 976–77 (1993). Most critics agree, however, that “[r]ecovery teams usually work under the constraints of little money, conflicting interest groups, and little time in which to produce a recovery plan. . . . These problems are exacerbated by the limited information available for most listed species.” Foin et al., supra, at 178. See Julie K. Miller et al.,
The Endangered Species Act: Dollars and Sense, 52 BioSci. 163, 167–68 (2002), for a discussion on funding.

[66] Williams, supra note 1, at 22.

[67] Id.

[68] Id. at 23–25.

[69] Id.

[70] Burns District, Oregon; Areas of Critical Environmental Concern, 48 Fed. Reg. 30,202, 30,202 (June 30, 1983) (designating 520 acres as the Borax Lake ACEC).

[71] Federal Land Policy and Management Act of 1976, 43 U.S.C. §§ 1701–1784 (2006).

[72] Id. § 1702(a). As the BLM Manual notes, the designation thus “serves as a reminder that significant value(s) or resource(s) exist which must be accommodated when future management actions and land use proposals are considered near or within an ACEC.” Bureau of Land Mgmt., U.S. Dep’t of the Interior, Bureau of Land Management Manual Transmittal Sheet: 1613 – Areas of Critical Environmental Concern § 1613.02 (1988)
(on file with author).

[73] 48 Fed. Reg. at 30,202–03; Bureau of Land Mgmt., U.S. Dep’t of the Interior, Andrews Management Unit Record of Decision and Resource Management Plan 70–71 (2005) (describing management standards); see also Oregon; Off-Highway Vehicle Designation, 52 Fed. Reg. 5348, 5349 (Feb. 20, 1987) (designating the Alvord Desert ACEC as “limited to motorized vehicle use on designated, existing roads and trails”).

[74] Williams, supra note 1.

[75] Id. at 1–19.

[76] Id. at 18–19.

[77] Id. at 14.

[78] The plan called for permanent protection for both the 160-acre parcel surrounding Borax Lake and another 160-acre parcel north of the lake “by The Nature Conservancy or other appropriate Public Resource Agency,” and withdrawal of the Lake’s waters from appropriation under state water law. Id. at 27–28; see also id. at 33–34.

[79] Id. at 35–45.

[80] Id. at 19–22.

[81] Id. at 22.

[82] Id. at 30.

[83] The ESA requires that the Secretary of Interior review the status of all listed species
“at least once every five years.” Endangered Species Act of 1973, 16 U.S.C. § 1533(c)(2)(A) (2006). The chub’s status had been reviewed in 1987 and 1991. See Review of Species Listed in 1976, 1977, 1981, and 1982, 52 Fed. Reg. 25,523, 25,527 (July 7, 1987) (1987 review); 5-Year Review of Listed Species, 56 Fed. Reg. 56,882, 56,887 (Nov. 6, 1991) (1991 review). The 2003 independent review was in preparation for the next five-year review. Initiation of 5-Year Reviews of 70 Species in Idaho, Oregon, Washington, and Hawaii, and Guam, 71 Fed. Reg. 18,345, 18,346 (Apr. 11, 2006) (2006 review).

[84] Jack E. Williams & Catherine A. Macdonald, A Review of the Conservation Status of the Borax Lake Chub, an Endangered Species 2 (2003).

[85] Steens Mountain Cooperative Management and Protection Act of 2000, 16 U.S.C. §§ 460nnn-1 to -122 (2006).

[86] Id. § 460nnn-81(a)(2).

[87] Williams & Macdonald, supra note 84, at 7.

[88] Id. at 9.

[89] Id. at 10–12.

[90] Id.; see also id. at 27–32.

[91] TNC’s acquisition of the land, establishment of an instream water right by the state, and the withdrawal of the basin from geothermal development in the Steens Mountain Cooperative Management and Protection Act removed the threats cited in 1982. Id. at 10, 12–13.

[92] Id. at 13.

[93] Id.

[94] Id. at 14.

[95] Id. at 3.

[96] See id. app. B, at 33.

[97] Id. at 14.

[98] Id. at 14–15. Goldfish (Carassius auratus) have been introduced into another lake north of Borax Lake. Jack E. Williams et al., Prospects for Recovering Endemic Fishes Pursuant to the U.S. Endangered Species Act, Fisheries, June 2005, at 24, 26.

[99] Williams & Macdonald, supra note 84, at 15; see also id. at 19–21 (discussing the vulnerability of the chub).

[100] U.S. Fish & Wildlife Serv., U.S. Dep’t of the Interior, Policy and Guidelines for Planning and Coordinating Recovery of Endangered and Threatened Species 1 (1990), available at http://www.fws.gov/endangered/pdfs/Recovery/90guide.pdf.

[101] It was not until 1988—the last time the Act was amended—that even a modest provision for monitoring the status of delisted species was added. Endangered Species Act Amendments of 1988, Pub. L. No. 100-478, tit. I, § 1004, 102 Stat. 2306, 2307 (1988) (codified at 16 U.S.C. § 1533(g) (2006)).

[102] See Native Fish and Wildlife: Endangered Species, 32 Fed. Reg. 4001, 4001 (Mar. 11, 1967); Proposed Reclassification of the Aleutian Canada Goose from Endangered to Threatened,
54 Fed. Reg. 40,142, 40,142 (proposed Sept. 29, 1989). The species has recently been reclassified from the Aleutian Canada goose (Branta canadensis leucopareia) to the Aleutian cackling goose. See, e.g., U.S. Fish & Wildlife Serv., U.S. Dep’t of the Interior, Alaska Maritime National Wildlife Refuge: Area History: 1945 to Present, http://alaskamaritime.fws.gov/historyculture/ 1945-Present.htm (last visited Apr. 18, 2010).

[103] Final Rule to Remove the Aleutian Canada Goose from the Federal List of Endangered and Threatened Wildlife, 66 Fed. Reg. 15,643, 15,645 (Mar. 20, 2001).

[104] The recovery goals called for “at least 7,500 geese” and 50 nesting pairs in three geographic parts of its historic range. Aleutian Canada Goose Recovery Team, Aleutian Canada Goose Branta canadensis leucopareia Recovery Plan 22 (2d rev. 1991). In addition to the nearly 4680% population increase, the breeding range expanded from one to at least six islands. 66 Fed. Reg. at 15,645.

[105] See Anne Mini & Ron LeValley, Mad River Biologists, Aleutian Cackling Goose Agricultural Depredation Management Plan: Del Norte County 2005–2006, at 63 (2006), available at http://www.pcjv.org/california/pdfs/Del%20Norte%20Aleutian%20Plan%20_Final%209
-2006.pdf.

[106] See Final Rule to Remove the American Peregrine Falcon from the Federal List of Endangered and Threatened Wildlife, 64 Fed. Reg. 46,542, 46,554–55 (Aug. 25, 1999). In addition to eggshell thinning, organochlorine pesticides are directly toxic to pelicans. See Removal of the Brown Pelican in the Southeastern United States from the List of Endangered and Threatened Wildlife, 50 Fed. Reg. 4938, 4938 (Feb. 4, 1985) (codified at 50 C.F.R. pt. 17).

[107] The falcon had been “essentially extirpated” east of the Mississippi River and in the Great Plains states east of the Rocky Mountains; west of the 100th meridian, nesting had been reduced by at least two-thirds. 64 Fed. Reg. at 46,542–43. Four regional recovery plans, developed between 1982 and 1991, called for a minimum of 631 breeding pairs with specified distribution by states and regions. Id. at 46,543–48. When the species was delisted in 1999, there were at least 1650 breeding pairs broadly distributed across North America. Id. at 46,544–49. On the species’s recovery, see generally Return of the Peregrine: A North American Saga of Tenacity and Teamwork (Tom J. Cade & William Burnham eds., 2003) (describing the decline of the peregrine, legislation in response to that decline, and subsequent recovery).

[108] Endangered Fish and Wildlife; Gray Whale, 58 Fed. Reg. 3121, 3122, 3125 (Jan. 7, 1993); Reclassification of the American Alligator to Threatened Due to Similarity of Appearance Throughout the Remainder of Its Range, 52 Fed. Reg. 21,059, 21,059–61 (June 4, 1987) (codified at 50 C.F.R. pt. 17).

[109] See 52 Fed. Reg. at 21,061 tbl.1; Endangered Fish and Wildlife; Gray Whale, 56 Fed. Reg. 58,869, 58,870 (proposed Nov. 22, 1991) (to be codified at 50 C.F.R. pt. 222).

[110] See Dale D. Goble, What Are Slugs Good for? Ecosystem Services and the Conservation of Biodiversity, 22 J. Land Use & Envtl. L. 411, 413 (2007).

[111] Endangered Species Act of 1973, 16 U.S.C. § 1533(f) (2006).

[112] Interagency Cooperation—Endangered Species Act of 1973, as Amended; Final Rule, 51 Fed. Reg. 19,926, 19,935 (June 3, 1986) (codified at 50 C.F.R. pt. 402).

[113] 16 U.S.C. § 1533(a)(1)(A)–(C) (2006).

[114] Arctic Goose Joint Venture, Cackling Goose, http://www.agjv.ca/index.php?option=com_ content&task=view&id=16&itemid=56 (last visited Apr. 18, 2010) (outlining the current status and management of Aleutian cackling geese).

[115] 16 U.S.C. § 1533(a)(1)(D) (2006).

[116] See id. § 1533(a)(1); see also supra note 32.

[117] See 16 U.S.C. § 1533(b)(1)(B)(ii) (2006) (stating that the Secretary must consider whether a species is “in danger of extinction” during the delisting process).

[118] See supra note 105 and accompanying text.

[119] 16 U.S.C. §§ 703–711 (2006). The MBTA federalized the conservation of migratory birds:
It begins, for example, with a broad declaration that “it shall be unlawful . . . to take, . . . kill, possess, . . . sell, . . . ship, [or] export . . . any migratory bird.” Id. § 703(a). Federal protection extends to “any product . . . which . . . is composed in whole or part, of any such bird or any part, nest or egg thereof.” Id. The species’s status is monitored, and take is managed by the federal and state governments through the Pacific Flyway Council established under the MBTA. See id. § 704 (authorizing the Secretary of Interior to allow takes when appropriate and to issue regulations governing the same); id. § 708 (recognizing that states may impose stricter regulations for protection of migratory birds); Pac. Flyway Council, Coordinated Management, http://pacificflyway.gov/Index.asp (last visited Apr. 18, 2010). The Council represents the fish and game commissions of the western states and provinces. Id. It has prepared a management plan for the Aleutian Canada goose. See Subcomm. on the Cackling Canada Goose, Pac.  Flyway Study Comm., Pac. Flyway Council, U.S. Fish & Wildlife Serv., Pacific Flyway Management Plan for the Cackling Canada Goose (1999), available at http://pacificflyway.gov/Documents/Ccg_plan.pdf.

In addition, since the species nests on islands that are included within the Alaska Maritime National Wildlife Refuge, see U.S. Fish & Wildlife Serv., U.S. Dep’t of the Interior, Alaska Maritime National Wildlife Refuge, http://alaska.fws.gov/nwr/akmar/index.htm (last visited Apr. 18, 2010), FWS has the authority not only to remove foxes from additional islands in the Aleutian chain but also to take whatever additional management actions might be necessary. See National Wildlife Refuge System Administration Act of 1966, 16 U.S.C. §§ 668dd–668ee (2006); see also U.S. Fish & Wildlife Serv., U.S. Dep’t of the Interior, Wildlife: Alien/Invasive Species, http://alaska.fws.gov/nwr/akmar/wildlife-wildlands/wildlife/nonnative/alien.htm (last visited Apr. 18, 2010).

[120] On November 20, 2009, a Google search for “peregrine falcon camera” produced several thousand hits, the first ten of which were for cameras in an unidentified city in Pennsylvania; Jersey City, New Jersey; Buffalo, New York; Rochester, New York; Salt Lake City, Utah; Columbus, Ohio; Rochester, New York (a second pair); and Wall Street in New York City.

[121] See Migratory Bird Permits; Changes in the Regulations Governing Falconry, 73 Fed. Reg. 59,448 (Oct. 8, 2008) (to be codified at 50 C.F.R. pts. 21–22).

[122] Gray whales are subject to monitoring by the International Whaling Commission under the Protocol to the International Convention for the Regulation of Whaling, Dec. 2, 1946, 62 Stat. 1716, 161 U.N.T.S. 72. Domestically, the species is protected under the Marine Mammal Protection Act of 1972, 16 U.S.C. §§ 1361–1421h (2006). In addition to state fish and game regulations, the alligator continues to be managed pursuant to three federal regulatory mechanisms: the Lacey Act of 1900, 16 U.S.C. § 701 (2006), and the Lacey Act Amendments of 1981, 16 U.S.C. §§ 3371–3378 (2006), which prohibit interstate shipment of wildlife taken contrary to state or federal law, id. §§ 701, 3371–3378; a special rule promulgated under the ESA’s similarity of appearance provisions (since the alligator is similar to other crocodilians, which still are listed), 50 C.F.R. § 17.42 (2004); and listing under Appendix I of Convention on International Trade in Endangered Species of Wild Fauna and Flora, app. I, Mar. 3, 1973,
27 U.S.T. 1087, 1118, 993 U.N.T.S. 243, 257, which prohibits international commerce in the species, id.

[123] See supra notes 102–09 and accompanying text.

[124] See supra notes 119, 121–22 and accompanying text.

[125] See, e.g., U.S. Fish & Wildlife Serv., U.S. Dep’t of the Interior, Peregrine Falcon (Falco peregrinus) (2006), available at http://myfwc.com/conservation/conservationyou_
living_w_wildlife_alligators.htm (stating that peregrine falcons “readily nest on manmade structures” in urban environments); U.S. Fish & Wildlife Serv., U.S. Dep’t of the Interior, Threatened and Endangered Species: Aleutian Canada Goose (Branta canadensis leucopareia) (1999), available at http://alaska.fws.gov/media/acg/fact.pdf (stating that the Aleutian Canada goose frequents agricultural pastures and grainfields during its migration); Fla. Fish & Wildlife Conservation Comm’n, American Alligator, http://www.fwc.state.fl.us/ Learning/Learn_AdultsFamilies_alligator.htm (last visited Apr. 18, 2010) (highlighting the encroachment of humans into the natural habitat of the American alligator); NatureServe Explorer, Comprehensive Report Species—Eschrichtius robustus, http://www.natureserve.org/
explorer/servlet/NatureServe?searchName=Eschrichtius+robustus (last visited Apr. 18, 2010) (stating that the gray whales’ habitat consists of coastal and shallow shelf waters).

[126] See David S. Wilcove et al., Leading Threats to Biodiversity: What’s Imperiling U.S. Species, in Precious Heritage: The Status of Biodiversity in the United States 239, 240 (Bruce A. Stein et al. eds., 2000); David S. Wilcove et al., Quantifying Threats to Imperiled Species in the United States: Assessing the Relative Importance of Habitat Destruction, Alien Species, Pollution, Overexploitation, and Disease, 48 BioSci. 607, 607–09 (1998).

[127] David S. Wilcove & Linus Y. Chen, Management Costs for Endangered Species, 12 Conservation Biology 1405, 1406 (1998).

[128] Carol I. Bocetti, Dale D. Goble & J. Michael Scott, Using Conservation-Management Agreements to Secure Post-Recovery Perpetuation of Conservation-Reliant Species: The Kirtland’s Warbler as a Case Study, BioSci. (forthcoming) (manuscript at 5) (explaining that one recovery strategy for Kirtland’s warbler (Dendroica kirtlandii) is habitat management that harvests and replants jack pines in a pattern that attempts to replicate their natural regeneration distribution after wildfires).

[129] J. Michael Scott et al., Conservation-Reliant Species and the Future of Conservation, Conservation Letters (forthcoming 2010) (manuscript at 10), available at http://www3.interscience.wiley.com/cgi-bin/fulltext/123263877/PDFSTART (reporting that 84% of the species listed under the ESA will require continuing conservation management even after the biological requirements for delisting have been achieved).

[130] Press Release, U.S. Fish & Wildlife Serv., Rare White Mountains Plant Recovers: Endangered Species Success Story (Aug. 28, 2002), http://www.fws.gov/news/newsreleases/ r5/C3314775-90A8-4608-9A5159013020D017.html (last visited Apr. 18, 2010).

[131] Determination of Potententilla robbinsiana to Be an Endangered Species, with Critical Habitat, 45 Fed. Reg. 61,944, 61,945 (Sept. 17, 1980) (codified at 50 C.F.R. pt. 17).

[132] Press Release, U.S. Fish & Wildlife Serv., supra note 130.

[133] Proposed Rule to Remove Potentilla robbinsiana (Robbins’ cinquefoil) from the Endangered and Threatened Plant List, 66 Fed. Reg. 30,860, 30,861 (proposed June 8, 2001) (to be codified at 50 C.F.R. pt. 17). To address this objective, the trail was rerouted away from the population, and a screen wall was constructed between the trail and the population and posted with “closed entry” signs. Id. at 30,861, 30,863. The plan also sought to expand the population into formerly occupied habitat that had been degraded by hikers. Id. at 30,861. Plants were also transplanted back into these areas after the trail had been rerouted. Removal of Potentilla robbinsiana (Robbins’ cinquefoil) from the Federal List of Endangered and Threatened Plants, 67 Fed. Reg. 54,968, 54,970 (Aug. 27, 2002) (codified at 50 C.F.R. pt. 17).

[134] 66 Fed. Reg. at 30,861. The plan originally called for four additional populations but was scaled back when it became apparent that there was not sufficient habitat. 67 Fed. Reg. at 54,969–70.

[135] 67 Fed. Reg. at 54,968–73. The four populations totaled nearly 15,000 individuals. Id.

[136] Id. at 54,972–73. For example, despite continuing monitoring and the presence of the Appalachian Mountain Club botanist during the summer of 1985, 86 of the 4286 hikers who hiked the section of the Trail at Monroe Flats trespassed into the walled-off critical habitat. Id. at 54,972. This two percent trespass rate was less than the five percent noncompliance standard established by the recovery plan. Id.

[137] Id. at 54,974.

[138] Id. at 54,970; see also id. at 54,968, 54,971–73.

[139] 66 Fed. Reg. at 30,861.

[140] 67 Fed. Reg. at 54,972–73.

[141] Id. at 54,973.

[142] Memorandum of Understanding Between U.S. Forest Serv. and U.S. Fish & Wildlife Serv. for the Conservation of the Robbins’ Cinquefoil (Potentilla robbinsiana) 2 (Dec. 2, 1994) (on file with author).

[143] Id. at 3.

[144] Id. at 1.

[145] Id.

[146] Id. at 1–2.

[147] Final Rule to Remove the Douglas County Distinct Population Segment of Columbian White-Tailed Deer from the Federal List of Endangered and Threatened Wildlife, 68 Fed. Reg.
43,647, 43,647 (July 24, 2003) (codified at 50 C.F.R. pt. 17).

[148] Native Fish and Wildlife; Endangered Species, 32 Fed. Reg. 4001, 4001 (Mar. 11, 1967).

[149] 68 Fed. Reg. at 43,647–48.

[150] One listable unit under the ESA’s definition of “species” is “any distinct population segment of any species of vertebrate fish or wildlife which interbreeds when mature.” Endangered Species Act of 1973, 16 U.S.C. § 1532(16) (2006). In 1996, the federal wildlife agencies issued a joint policy on the interpretation of DPS. Policy Regarding the Recognition of Distinct Vertebrate Population Segments Under the Endangered Species Act, 61 Fed. Reg.
4722, 4722 (Feb. 7, 1996). For the application of the policy to the deer, see Proposed Rule to Delist the Douglas County Population of Columbian White-Tailed Deer, 64 Fed. Reg.
25,263, 25,265 (proposed May 11, 1999) (to be codified at 50 C.F.R. pt. 17); see also Supplemental Proposed Rule to Remove the Douglas County Population of Columbian
White-Tailed Deer from the Federal List of Endangered and Threatened Species; Notice of a Public Hearing, 67 Fed. Reg. 42,217, 42,220 (proposed June 1, 2002) (to be codified at 50 C.F.R. pt. 17).

[151] 68 Fed. Reg. at 43,647.

[152] Id. at 43,652.

[153] Compare Subcomm. on the Cackling Canada Goose, supra note 119 (discussing the monitoring and management of the goose by the Pacific Flyway Council pursuant to the Migratory Bird Treaty Act, 16 U.S.C. §§ 703–711 (2006)), with 68 Fed. Reg. at 43,656–58 (discussing a management plan, developed by FWS for the Douglas County DPS, designed to detect changes in the status of the population).

[154] See 68 Fed. Reg. at 43,651.

[155] Id.

[156] See id.

[157] Id.

[158] Id. The security of these various tools may vary widely. Federal acquisition of land is probably the most secure; acquisition by private conservation organizations is also likely to be relatively secure (depending upon funding). Local politics, on the other hand, may be hostile to the conservation needs of the species or unwilling to expend the necessary funds. See generally Gregory M. Parkhurst & Jason F. Shogren, Evaluating Incentive Mechanisms for Conserving Habitat, 43 Nat. Resources J. 1093 (2003) (comparing tools utilized for habitat conservation plans across the federal, local, and private sectors).

[159] Roseburg Dist. Office, Bureau of Land Mgmt., U.S. Dep’t of the Interior, North Bank Habitat Management Area and Area of Critical Environmental Concern: Record of Decision: Habitat Management Plan and Monitoring Plan 23 (2001), available at http://www.blm.gov/or/districts/roseburg/plans/files/NBnkACEC.pdf.

[160] Id.

[161] 68 Fed. Reg. at 43,654. The county also adopted a Columbian White-Tailed Deer Habitat Protection Program that imposed land-use controls, including minimum lot sizes and set-back requirements designed to protect brushy riparian corridors. Id. at 43,654–55.

[162] Roseburg Dist. Office, supra note 159, at 9.

[163] Id. at 10.

[164] Id. at 37–38, 59–65. The Douglas County Parks Department also manages the bequest lands to provide habitat for the species consistent with the other objectives of the bequest. 68 Fed. Reg. at 43,654.

[165] Roseburg Dist. Office, supra note 159, at 1, 17.

[166] Determination of Threatened Status for Helianthus eggertii (Eggert’s Sunflower), 62 Fed. Reg. 27,973, 27,976 (May 22, 1997) (codified at 50 C.F.R. pt. 17).

[167] Id. at 27,975–76.

[168] Proposed Removal of Helianthus eggertii (Eggert’s Sunflower) from the Federal List of Endangered and Threatened Species and Determination that Designation of Critical Habitat is Not Prudent, 69 Fed. Reg. 17,627, 17,629, 17,633 (proposed Apr. 5, 2004) (to be codified at 50 C.F.R. pt. 17).

[169] Id. at 17,633.

[170] Id. at 17,629.

[171] Determination of Endangered or Threatened Status for Five Plants from the Southern San Joaquin Valley, 55 Fed. Reg. 29,361, 29,361–62 (July 19, 1990) (codified at 50 C.F.R. pt. 17).

[172] Removing Eriastrum hooveri (Hoover’s Woolly-Star) from the Federal List of Endangered and Threatened Species, 68 Fed. Reg. 57,829, 57,832 (Oct. 7, 2003) (codified at 50 C.F.R. pt. 17).

[173] Id. at 57,829.

[174] National Environmental Policy Act of 1969, 42 U.S.C. §§ 4321–4347 (2006).

[175] 68 Fed. Reg. at 57,832.

[176] Id.; see id. at 57,835–36. The quoted language mirrors the consultation standard in section 7 of the Act. See National Environmental Policy Act of 1969, 42 U.S.C. § 4321(2)(a) (2006). There is, however, no actual consultation and thus no independent evaluation of the potential impact of any proposed action on the species.

[177] 68 Fed. Reg. at 57,829.

[178] Holly Doremus, Delisting Endangered Species: An Aspirational Goal, Not a Realistic Expectation, 30 Envtl. L. Rep. (Envtl. Law Inst.) 10,434, 10,454 (2000); Holly Doremus & Joel E. Pagel, Why Listing May Be Forever: Perspectives on Delisting Under the U.S. Endangered Species Act, 15 Conservation Biology 1258, 1261 (2001); Williams et al., supra note 98, at 24. This is particularly true for plants and invertebrates, which are often entirely without legal protection. Doremus, supra, at 10,447–48.

[179] Although there are other, more broadly applicable statutes that protect habitat (e.g., the Federal Water Pollution Control Act, 33 U.S.C. §§ 1251–1387 (2006), state fish and game laws, and local zoning regulations), such statutes are unlikely to be sufficient to protect most listed species because such statutes only protect habitat in the process of advancing other objectives (such as assuring clean water) and thus do not provide assurances of ongoing management in the absence of the other objectives. Similarly, existing statutes on nonnative species (e.g., the Nonindigenous Aquatic Nuisance Prevention and Control Act of 1990, 16 U.S.C. §§ 4701–4751 (2006), and state noxious weed control programs) are insufficiently tailored to be of much assistance to individual conservation-reliant species.

[180] U.S. Fish & Wildlife Serv., U.S. Dep’t of the Interior, Draft Revised Recovery Plan for Hawaiian Waterbirds, Second Draft of Second Revision 44, 46–47 (2005), available at http://ecos.fws.gov/docs/recovery_plan/061213.pdf.

[181] Dale D. Goble, Recovery in a Cynical Time—With Apologies to Eric Arthur Blair, 82 Wash. L. Rev. 581, 587 (2007).

[182] See J. Michael Scott et al., Recovery of Imperiled Species Under the Endangered Species Act: The Need for a New Approach, 3 Frontiers Ecology & Env’t 383, 386 (2005).

[183] Williams & Macdonald, supra note 84, at 14–15; Williams et al., supra note 98, at 26.

[184] Williams & Macdonald, supra note 84, at 14–24.

[185] Id.

[186] Id.

[187] Id. at 16–17.

[188] Id. at 17, 22.

[189] Id. at 19.

[190] Id. at 18.

[191] Id.

[192] Id. at 16–22.

[193] There is a potential for some conflict between competing TNC objectives. On the one hand, the organization has a lengthy record of successful conservation management. Richard Brewer, Conservancy: The Land Trust Movement in America 186 (2003). On the other hand, the need to raise funds can lead it to advertising fragile areas such as Borax Lake. The TNC website, for example, has a stunning picture of mist rising from Borax Lake with a snow-capped Steens Mountain in the background; the lead paragraph is a discussion of “[w]hy [y]ou [s]hould [v]isit.” The Nature Conservancy, Borax Lake, http://nature.org/wherewework/northamerica/ states/oregon/preserves/art6794.html (last visited Apr. 18, 2010).

[194] See, e.g., Brewer, supra note 193, at 186, 204; Bureau of Land Mgmt., supra note 72, § 1613.02.

[195] Williams & Macdonald, supra note 84, at 20.

[196] David S. Wilcove & Lawrence L. Master, How Many Endangered Species Are There in the United States?, 3 Frontiers Ecology & Env’t 414, 416 (2005).

WildWest Institute v. Bull

WildWest Institute and Friends of the Bitterroot, Inc. (collectively WildWest) filed suit against the United States Forest Service (USFS), alleging the agency’s hazardous fuel reduction project for Montana and Idaho’s Bitterroot National Forest violated the National Environmental Policy Act (NEPA),[1] the National Forest Management Act (NFMA),[2] and the Healthy Forests Restoration Act (HFRA).[3] Following a Ninth Circuit opinion affirming denial of WildWest’s request for a preliminary injunction[4] and subsequent grant of summary judgment in favor of USFS by the United States District Court for the District of Montana, WildWest appealed to the Ninth Circuit. The Ninth Circuit affirmed the district court’s grant of summary judgment against WildWest, holding that USFS did not commit procedural or substantive violations in its record of decision (ROD) and accompanying final environmental impact statement (FEIS).

After Montana’s Middle East Fork area of the Bitterroot National Forest suffered severe damage as a result of wildfires in the summer of 2000, USFS, pursuant to its management role over national forests, developed the Middle East Fork Hazardous Fuel Reduction Project (Project). The Project’s purpose was to reduce fire threats in the region, restore fire-adapted ecosystems, and restore stands affected by a Douglas fir bark beetle epidemic by treating infested and at-risk forest lands. In compliance with HFRA, USFS studied, developed, and described the proposed agency action, a no-action alternative, and an additional action alternative proposed by WildWest.[5]

Following at least twelve public meetings, a forty-five day public comment period, and analyses of alternative plans, USFS announced the FEIS at a press conference. Several vocal opponents of the Project were excluded from the press conference. In the FEIS, USFS adopted a modified version of the agency’s alternative, which called for treatment of 4938 acres in the Middle East Fork area, including approximately 2983 acres of commercial treatments. In response to WildWest’s objections during the comment process, USFS made a number of changes to its proposed alternative before publication of its ROD, which resulted in 1534 acres from being dropped from treatment. Specifically, USFS decided not to treat old growth habitat or units with “greater than 15% detrimental soil reliance or units . . . projected to have greater than 15% disturbance after the treatments,” not to perform summer ground-based tractor harvest operations, and not treat stands where further field review was needed to corroborate determinations of the agency’s soil scientist.[6]

On appeal, WildWest argued USFS violated NEPA in three ways: 1) by irretrievably committing resources in favor of its preferred alternative before making its final decision, 2) by failing to engage in adequate public collaboration, and 3) by failing to discuss competing views of the agency’s own soil scientist in the FEIS. Wildwest also challenged USFS’s substantive decision, alleging the Project’s impact on soil productivity, old growth habitat, species viability, and watershed sedimentation violated NFMA and HFRA. The Ninth Circuit began by examining WildWest’s argument that USFS committed procedural violations. NEPA prohibits USFS from taking action that would limit its consideration of alternatives identified in the decision-making process, including “committing resources which would prejudice the selection of alternative plans.”[7] WildWest argued that USFS violated this requirement by prematurely marking trees in preparation for logging before issuance of the ROD and FEIS. The Ninth Circuit rejected this argument, holding that USFS’s pre-marking of trees did not irretrievably commit the agency to a particular course of action because the monetary expenditure involved was not so substantial that it limited such choice. Conceding that “a financial commitment can, in some instances, constitute an irretrievable commitment” of resources, the Ninth Circuit cautioned that Ninth Circuit “cases have focused on the commitment of natural resources, not necessarily the agency’s financial resources.”[8] In the instant case, the Ninth Circuit explained that USFS’s spending of $208,000 to pre-mark trees was not such a substantial financial commitment as to limit the choice of reasonable alternatives, as demonstrated by the fact that the ROD ultimately excluded 410 acres of pre-marked timber from treatment.

Second, the Ninth Circuit rejected the allegation that USFS had violated NEPA by failure to engage in adequate public collaboration. Under NEPA, USFS is required to involve the public in its decision-making process,[9] including the specific requirement that the agency must provide notice of public meetings.[10] The Ninth Circuit court rejected WildWest’s arguments that USFS acted improperly when it removed conservation proponents from a notice mailing list, failed to announce that a HFRA project would be discussed at the meeting, failed to indicate in the FEIS that it had received more than 11,000 public comments in opposition to the Project, and failed to give notice of when the FEIS would be announced. Explaining that NEPA does not specify a particular form of notice, the Court noted that USFS had, prior to holding two public meetings, taken several steps that provided notice, including publishing an announcement in a public newspaper, issuing a news release, and sending individual notices to interested members of the public, including WildWest. Further, the Ninth Circuit explained there is no NEPA requirement that USFS identify the number of public comments received, and that USFS did properly summarize the nature of the comments and specific substantive responses in the FEIS. Finally, the court rejected the assertion that USFS violated NEPA by holding a closed press conference to announce adoption of the FEIS, explaining that NEPA contains no requirement that agencies give notice of announcements of final decisions nor requires agencies to make those announcements a public event.

Third, the Ninth Circuit rejected WildWest’s assertion that USFS violated NEPA by disregarding the data and opinions of its own soils expert. NEPA requires that, in the FEIS, USFS discuss opposing views and indicate the agency’s response to the issues raised.[11] The court held that USFS did not disregard the soil expert’s findings, pointing to an acknowledgement and explanation of USFS’s disagreement with the expert’s conclusions in the FEIS.

Next, the Ninth Circuit addressed WildWest’s substantive NFMA and HFRA claims.[12] Under NFMA, USFS may harvest timber from national forests only where soil, slope, or watershed conditions will not be irreversibly damaged.[13] Additionally, NFMA directs USFS to perform continuous monitoring and assessment in the field to evaluate the effects its management plans have on the productivity of the land.[14] Because the Bitterroot National Forest Plan does not provide specific numeric soil standards, USFS applied its Region One Soil Quality Standards (R1-SQS), which provide that the cumulative detrimental impact of activities should be no more than fifteen percent of the activity area. WildWest asserted this technique violated NFMA’s substantive soil productivity requirements because the R1-SQSs are facially unreliable, and USFS failed to properly consider cumulative impacts in determining whether the project satisfied such a standard. The Ninth Circuit rejected the first assertion on grounds that WildWest failed to raise the challenge in the district court, and declined to exercise its discretion to consider the newly raised issue.[15] The Ninth Circuit similarly rejected WildWest’s second argument because the record showed USFS considered the cumulative impacts from past timber harvests and had concluded these activities did not reduce soil or site productivity in violation of soil quality standards.

The court also rejected WildWest’s various challenges to the Project’s management of old growth habitat. HFRA requires that USFS maintain or help restore old growth stands when undertaking fuel reduction projects.[16] Accordingly, the ROD accompanying the FEIS indicated that the Project would not treat old growth habitat. WildWest challenged the assertion, arguing that USFS’s classification was flawed because it was based on an analysis of “imminently dead” trees. The Ninth Circuit rejected this argument because the “imminently dead” standard applied to tree marking, not classification of old growth status; and USFS properly applied its selected methodology. The Ninth Circuit also rejected WildWest’s argument that the Project violated substantive old growth standards, in light of USFS’s conclusion that the Project does not treat old growth. Finally, the Ninth Circuit rejected WildWest’s argument that USFS is required to designate replacement habitat. Noting WildWest’s argument relied on a nonbinding district court case,[17] the Ninth Circuit concluded that, even assuming USFS is required to designate replacement habitat, USFS had satisfied that requirement by demonstrating the Project retains “the largest, healthiest and dominant residual trees” that may someday become old growth.[18]

Finally, the Ninth Circuit examined WildWest’s argument that USFS failed to consider the Project’s impact on population trends of management indicator species (MIS) such as the pileated woodpecker, northern goshawk, and black-backed woodpecker. Under NFMA, USFS is required to provide for diversity of plant and animal communities when managing national forests.[19] WildWest argued that the FEIS did not acknowledge the pileated woodpecker’s nesting preferences. The court disagreed, pointing out that the FEIS not only considered the pileated woodpecker’s habitat needs but also explained that prior forest management activities did not appear to have affected species viability. WildWest also asserted that USFS inadequately analyzed the Project’s impact on the northern goshawk by failing to conduct surveys to identify nest stands. The court also rejected this argument, concluding that USFS properly considered the goshawk’s habitat needs because the FEIS indicated USFS conducted surveys and took steps to avoid treatment within thirty acres of existing and potential goshawk nesting areas. Next, WildWest argued that USFS did not properly consider the Project’s impact on the black-backed woodpecker. The Ninth Circuit similarly rejected this argument, explaining that the record supported USFS’s conclusion that the Project would have no impact on black-backed woodpeckers or their habitat because the FEIS noted that other areas of the Bitterroot Forest contain ample habitat for black-backed woodpeckers while the Project area contained only minimal black-backed woodpecker habitat

In summary, the Ninth Circuit affirmed the decision of the district court, concluding the district court properly granted summary judgment in favor of USFS on all of the NEPA, NFMA, and HFRA claims asserted by WildWest.


[1] National Environmental Policy Act of 1969, 42 U.S.C. §§ 4321-4370e (2006).

[2] National Forest Management Act of 1976, 16 U.S.C. §§ 472a, 521b, 1600, 1611-1614 (2006)(amending Forest and Rangeland Renewable Resources Planning Act of 1974, Pub. L. No. 93-378, 88 Stat. 476 (1974)).

[3] Healthy Forest Restoration Act of 2003, 16 U.S.C. §§ 6501-6591 (2006).

[4] WildWest Inst. v. Bull (WildWest I), 472 F.3d 587 (9th Cir. 2006).

[5] 16 U.S.C. § 1614(c)(1) (2006) (requiring that USFS “study, develop, and describe the proposed agency action; the alternative of no action; and an additional action alternative . . . proposed during scoping or the collaborative process” when that final alternative “meets the purpose and needs of the project”).

[6] WildWest Inst. v. Bull (WildWest II), 547 F.3d 1162, 1167 (9th Cir. 2008).

[7] Id. at 1168 (internal citations omitted); see also 40 C.F.R. §§ 1502.2(f), 1506.1(a)(2)(2008).

[8] WildWest II, 547 F.3d at 1168; see also Friends of Se.’s Future v. Morrison, 153 F.3d 1059, 1064 (9th Cir. 1998) (holding no NEPA violation occurredwhen USFS had not, by virtue of developing tentative harvest schedule, irreversibly committed the “resources of Ushk Bay to logging”); Conner v. Burford, 848 F.2d 1441, 1449 (9th Cir. 1988) (affirming the district court’s finding of a NEPA violation when government sold oil and gas leases within a national forest without reserving the right to prevent surface-disturbing activity).

[9] 40 C.F.R. § 1500.2(d) (2008) (dictating that federal agencies “shall to the fullest extent possible . . . [e]ncourage and facilitate public involvement in decisions which affect the quality of the human environment”).

[10] Id. § 1506.6(b).

[11] Id. § 1502.9(b).

[12] The Ninth Circuit explained that its analysis of WildWest’s substantive claims was guided by the court’s recent decision in Lands Council v. McNair, 537 F.3d 981 (9th Cir. 2008) (en banc), noting that, under the Lands Council standard, the Ninth Circuit does not act as a reviewing body of scientists, but rather only reviews whether the agency “support[s] its conclusions that a project meets the requirements of the NFMA and relevant Forest Plan with studies that the agency in its expertise deems reliable.” Id. at 994.

[13] National Forest Management Act, 16 U.S.C. §1604(g)(3)(E)(i) (2006).

[14] Id. § 1604(g)(3)(C).

[15] See Cold Mountain v. Garber, 375 F.3d 884, 891 (9th Cir. 2004) (explaining that, while an issue raised for the first time on appeal is generally deemed waived, the appellate court has discretion to consider the raised issue when 1) review is necessary to prevent a miscarriage of justice, 2) the issue arises on appeal because of a change in the underlying law, or 3) the issue is purely legal and does not require a further developed factual record).

[16] Healthy Forest Restoration Act of 2003, 16 U.S.C. § 6512(e)(2) (2006).

[17] Lands Council v. Vaught, 198 F. Supp. 2d 1211, 1224 (E.D. Wash. 2002) (holding that to comply with the NFMA, USFS must demonstrate either that adequate old growth acreage exists in the forest to satisfy USFS’s old growth standards or that the timber slated to be harvested under the Project is not needed to fulfill old growth standards).The Ninth Circuit declined to review the merits of this district court decision.

[18] WildWest II, 547 F.3d 1162, 1174 (9th Cir. 2008).

[19] 16 U.S.C. § 1604(g)(3)(B) (2006).

League of Wilderness Defenders-Blue Mountains Biodiversity Project v. U.S. Forest Service

Two environmental groups, League of Wilderness Defenders-Blue Mountains Biodiversity Project and Cascadia Wildlands Project (collectively LOWD), sought declaratory and injunctive relief against the United States Forest Service (USFS) for a project that allowed commercial logging in the Ochoco National Forest. LOWD sued USFS pursuant to the Administrative Procedure Act (APA),[1] alleging that the Deep Creek Vegetation Management Project (Project) violated the National Environmental Policy Act (NEPA),[2] the National Forest Management Act (NFMA),[3] and the area’s Land and Resource Management Plan (LRMP). The United States District Court for the District of Oregon granted summary judgment to USFS. On appeal, the Ninth Circuit upheld the district court’s ruling on the NFMA claims, holding that USFS properly marked large-diameter trees to avoid unauthorized harvesting and adequately maintained connective habitat corridors in the Project’s planning area. However, the Ninth Circuit reversed the district court’s NEPA ruling and remanded the case to USFS to issue NEPA documentation that considered the effects of past timber sales in conjunction with the Project.

In 1999, after a USFS report, the Deep Creek Watershed Analysis (Watershed Analysis), recommended a mix of management actions to improve conditions in the Deep Creek watershed, USFS initiated NEPA documentation for the Project. In January 2004, USFS issued a final supplemental environmental impact statement (FSEIS) and a corresponding record of decision (ROD).[4] The ROD selected the Project alternative which allowed commercial timber harvesting, precommercial thinning, fuel-reduction treatments, new and temporary road construction, and road re-construction. In all, the Project allowed logging of 12.8 million board feet of timber, primarily through tractor logging. After USFS denied LOWD’s administrative appeal of the ROD, LOWD sued USFS in district court, alleging that the Project violated NEPA, NFMA, and the LMRP. The district court adopted the findings and recommendations of the magistrate judge, granted summary judgment to USFS, and dismissed LOWD’s suit. LOWD timely appealed.

The Ninth Circuit reviews a district court’s summary judgment ruling de novo.[5] Under the APA, the Ninth Circuit may set aside only actions that are “arbitrary, capricious, an abuse of discretion, or otherwise not in accordance with law.”[6] To violate this narrow standard, the agency must have made a “clear error of judgment.”[7]

The Ninth Circuit first examined LOWD’s allegation that USFS violated NEPA[8] by failing to adequately consider the cumulative effects of the Project because USFS considered cumulative effects in the aggregate. The Ninth Circuit rejected USFS’s argument that Department of Transportation v. Public Citizen[9] allowed USFS to consider the effects of past actions in the aggregate,[10] because in this case, unlike in Public Citizen, USFS possessed statutory authority to regulate the environmental consequences of the Project.[11] However, the Ninth Circuit concluded that a 2005 Council on Environmental Quality (CEQ) memorandum interpreting NEPA regulations, which the magistrate judge struck from the record, did grant USFS the authority to consider past effects in the aggregate. The Ninth Circuit ruled that the magistrate judge’s decision to strike the CEQ memorandum constituted an abuse of discretion. Further, the memorandum deserved deference under Auer v. Robbins,[12] even though USFS offered the memorandum to support its interpretation of NEPA regulations for the first time during summary judgment proceedings, because the memorandum’s interpretation was not “plainly erroneous or inconsistent” with the regulations and LOWD failed to offer evidence that the interpretation did not reflect CEQ’s “fair and considered judgment” on the cumulative effects issue.[13] The court also noted that although Ninth Circuit precedent required USFS to catalogue “relevant” past timber sales,[14] the court reasoned that it could not “tell [USFS] what specific evidence to include, [or] how specifically to present it.”[15]

Although the Ninth Circuit concluded that USFS’s analysis of cumulative impacts in aggregate form satisfied NEPA, the court held the Project’s FSEIS itself failed review for arbitrary and capriciousness. The Ninth Circuit explained the FSEIS failed review for being arbitrary and captricious. USFS had argued that the Watershed Analysis, which prompted the Project but had not been subject to NEPA review, considered the past effects of timber sales and supplemented the FSEIS’s specific mention of only one previous timber sale. Citing the Ninth Circuit’s previous decision in Kern v. Bureau of Land Management,[16] the court reasoned that USFS could not, under NEPA regulations,[17] tier the FSEIS to the Watershed Analysis because the Watershed Analysis was a non-NEPA document. Thus, the Ninth Circuit reversed the district court’s ruling and remanded the case to USFS to reissue NEPA documentation that included relevant information about past timber sales.

Next, the Ninth Circuit addressed LOWD’s claims that USFS failed to consider the impact of future timber sales as part of its cumulative effects analysis. The FSEIS expressly stated that USFS did not plan for any timber projects within the Deep Creek watershed for the foreseeable future, which distinguished the Project from others with multiple planned timber sales.[18] Thus, because USFS had no reason to discuss the effects of future timber sales to satisfy the cumulative effects standard, the Ninth Circuit affirmed the district court’s ruling.

The Ninth Circuit also rejected LOWD’s argument that USFS failed to consider past, present, and future grazing practices as part of NEPA’s cumulative effects analysis. First, the court ruled that the FSEIS adequately evaluated the cumulative effects of past grazing, because the FSEIS traced the detrimental impacts of grazing on the watershed through various eras of land management. Second, the court concluded the FSEIS considered present grazing practices in its cumulative effects analysis, because the USFS discussed grazing practices’ present effect on the watershed in several sections, including a section titled “Cumulative Effects on Range.” Finally, because the FSEIS explained that future grazing regimes and specific grazing allotments were to be considered under separate environmental analyses, the court reasoned that any discussion of future effects from grazing was impracticable. Thus, the Ninth Circuit affirmed the district court’s ruling that the FSEIS adequately considered the cumulative effects of grazing.

The Ninth Circuit then considered LOWD’s contention that the Project would violate NFMA and the Ochoco LRMP by allowing the logging of trees equal to or greater than twenty-one inches in diameter[19] and by failing to ensure agency personnel marked the trees.[20] Responding to the district court’s concerns about correct marking of trees, USFS produced declarations of two USFS employees. One employee described how she supervised the training and work of the marking crew, and the other employee conveyed how the timber sale contract described the tree marking and provided further protections against unauthorized harvest. Based on these declarations, the Ninth Circuit affirmed the district court’s decision that the marking complied with NFMA and with the requirements of the Ochoco LRMP.

Finally, the Ninth Circuit examined LOWD’s allegation that the Project failed to maintain connective habitat corridors in the planning area, in violation of NFMA and the Ochoco LRMP. The Ochoco LRMP’s standards allow harvesting within corridors that connect old growth habitats if the corridors, inter alia, maintain stands with canopy closures that are within the top one-third of site potential and stand widths remain at least 400 feet wide at their narrowest point.[21] LOWD interpreted the LRMP standards to require that all stands within a connective corridor must be in the top one-third of site potential. Under LOWD’s interpretation, because the FSEIS stated that 77% of the planning area did not contain canopy closures within the top one-third of site potential, none of the timber stands met the connectivity corridor requirements. In contrast, USFS interpreted the standards to apply to individual stands, not connective corridors as a whole, which would permit harvesting within a stand that met the canopy closure and width requirements, regardless of which corridor the stand was in.

The Ninth Circuit deemed USFS’s interpretation of the connectivity corridor requirements more persuasive than LOWD’s. Under the deferential standard of Auer v. Robbins,[22] USFS’s interpretation did not appear plainly erroneous or inconsistent because the LRMP’s standards referred to individual stands instead of “every stand or all stands” and allowed harvesting “within connectivity corridors” instead of “harvesting a connectivity corridor” or “harvesting connectivity corridors” generally.[23] The court also explained that the FSEIS relied on certified findings that the silvicultural treatments would ensure that the stands would remain within the top one-third of their site potential. Furthermore, the court observed that LOWD did not dispute that the Project would fulfill the Ochoco LRMP’s substantive requirement to maintain connective corridors. Thus, the Ninth Circuit affirmed the district court’s ruling that the Project did not violate the connective-corridor requirements of NFMA and the Ochoco LRMP.

In conclusion, the Ninth Circuit affirmed the district court’s grant of summary judgment to USFS on LOWD’s claims under NFMA and the Ochoco LRMP. The Ninth Circuit also affirmed that USFS’s consideration of the effects of grazing practices and present and future timber sales in the Deep Creek area satisfied NEPA’s requirement to adequately consider the Project’s cumulative effects. Although the court held USFS could analyze the effects of past timber sales in the aggregate, it concluded that USFS violated NEPA by tiering the FSEIS to a planning document that lacked NEPA analysis. Thus, the Ninth Circuit reversed the district court’s grant of summary judgment in favor of USFS and remanded the task of preparing NEPA-compliant documentation of the effects of past timber sales to the agency.


[1] 5 U.S.C. §§ 551-559, 701-706, 1305, 3105, 3344, 4301, 5335, 5362, 7521 (2006).

[2] National Environmental Policy Act of 1969, 42 U.S.C. §§ 4321-4370e (2006).

[3] National Forest Management Act of 1976, 16 U.S.C. §§ 472a, 521b, 1600, 1611-1614 (2006)(amending Forest and Rangeland Renewable Resources Planning Act of 1974, Pub. L. No. 93-378, 88 Stat. 476 (1974)).

[4] USFS initially released an FSEIS and ROD in September 2001. LOWD filed an administrative appeal against the ROD, which prompted USFS to withdraw the ROD for further analysis and public comment. League of Wilderness Defenders-Blue Mountains Biodiversity Project v. U.S. Forest Serv. (League of Wilderness Defenders), 549 F.3d 1211, 1214 (9th Cir. 2008).

[5] Nw. Envtl. Advocates v. Nat’l Marine Fisheries Serv., 460 F.3d 1125, 1132 (9th Cir. 2006).

[6] 5 U.S.C. § 706(2) (2006).

[7] Marsh v. Or. Natural Res. Council, 490 U.S. 360, 378 (1989)(quoting Citizens to Preserve Overton Park, Inc. v. Volpe, 401 U.S. 402, 416 (1971)).

[8] National Environmental Policy Act of 1969, 42 U.S.C. § 4332(2)(C) (2006); 40 C.F.R. § 1508.7 (2008).

[9] 541 U.S. 752 (2004).

[10] Id. at 769-70.

[11] See Or. Natural Res. Council Fund v. Brong, 492 F.3d 1120, 1134 n.20 (9th Cir. 2007).

[12] 519 U.S. 452, 461 (1997).

[13] League of Wilderness Defenders, 549 F.3d 1211, 1217-18 (9th Cir. 2008).

[14] Lands Council v. Powell, 395 F.3d 1019, 1028 (9th Cir. 2005).

[15] League of Wilderness Defenders, 549 F.3d at 1219.

[16]284 F.3d 1062, 1072-73 (9th Cir. 2002).

[17] 40 C.F.R. § 1508.28 (2008).

[18] See, e.g., Blue Mountain Biodiversity Project v. Blackwood, 161 F.3d 1208, 1214-16 (9th Cir. 1998) (holding NEPA analysis inadequate when Environmental Assessment failed to analyze multiple future salvage logging projects within the Tower Fire area).

[19] National Forest Management Act of 1976, 16 U.S.C. § 1604(i) (2006) (mandating consistency between site-specific projects and LRMPs). The Ochoco LRMP, as amended in 1993, proscribed “the logging of green trees larger than 21 inches at breast height.” League of Wilderness Defenders, 549 F.3d at 1221.

[20] 16 U.S.C. § 472a(g) (2006).

[21] League of Wilderness Defenders, 549 F.3d at 1222 (citing standard 6(d)(3)(a)(2) of the Ochoco LRMP).

[22] 519 U.S. 452, 461-62 (1997) (discussing how an agency’s interpretation of its own regulations is entitled to substantial deference).

[23] League of Wilderness Defenders, 549 F.3d at 1223.

Natural Resources Defense Council v. U.S. Environmental Protection Agency

The Natural Resources Defense Council, along with various environmental advocacy groups (collectively NRDC),[1] petitioned the Ninth Circuit for review of a stormwater discharge rule promulgated by the U.S. Environmental Protection Agency (EPA). The challenged rule exempted discharges of sediment from oil and gas construction activities from the permitting requirements of the Clean Water Act (CWA),[2] even if these activities contributed to violations of water quality standards. The Ninth Circuit held the rule was an impermissible interpretation of section 402(l)(2) of the CWA because it was arbitrary and capricious. The Ninth Circuit vacated the rule and remanded the rule to EPA for further proceedings.

The National Pollutant Discharge Elimination System (NPDES) under the CWA requires dischargers obtain permits for any discharge of a pollutant from a point source.[3] Relevant to the case before the court, section 402(l)(2) exempts the discharge of uncontaminated stormwater runoff from oil, gas, and mining operations from the NPDES permitting requirements.[4] Section 402(l)(2) also provides the EPA Administrator discretion to determine whether stormwater runoff at such sites is contaminated.[5] In interpreting section 402(l)(2) prior to 2005, EPA took the position that all construction activities associated with oil, gas, or mining operations were ineligible for the exemption because of the serious water quality impacts caused by stormwater discharges polluted with construction site sediment.[6]

In 2005, Congress passed the Energy Policy Act.[7] Section 323 of the Energy Policy Act amended the CWA by expressly incorporating construction activities that occur at oil and gas operation sites into the definition of “‘oil and gas exploration, production, processing, or treatment operations, or transmission facilities’ . . . thereby bringing such activities within the CWA section 402(l)(2) exemption from the NPDES permitting requirement.”[8] In response, EPA issued a notice of proposed rulemaking, indicating the agency would modify EPA’s NPDES stormwater permit regulations to change the definition of oil and gas operations and to modify the agency’s interpretation of section 402(l)(2).[9] Ultimately, EPA promulgated the challenged rule, which exempted stormwater discharges comprised solely of sediment from oil and gas construction activities from the permitting requirements, even if such discharges contributed to a violation of a water quality standard.[10] In 2006, NRDC petitioned the Ninth Circuit for direct review of EPA’s promulgated rule.

The Ninth Circuit began by determining it had jurisdiction to review the petition and that petitioners NRDC had standing to bring the petition under the doctrine of associational standing. Next, the court explained it would review EPA’s final rule under the Administrative Procedure Act (APA),[11] which authorizes the court to set aside agency action that is “arbitrary, capricious, an abuse of discretion, or otherwise not in accordance with law.”[12] Because petitioners challenged EPA’s interpretation of section 323 of the Energy Policy Act, the court applied the two-step approach first set out in Chevron U.S.A., Inc. v. Natural Resources Defense Council, Inc. (Chevron).[13]

The first step of the Chevron analysis required the court to determine whether “Congress, when it amended section 503(24) of the CWA, through section 323 of the Energy Policy Act, unambiguously intended to exempt from NPDES permitting requirements for oil and gas construction activities the discharge of storm water runoff contaminated solely with sediment.”[14] Explaining that neither CWA section 402(l) nor section 323 of the Energy Policy Act mention the term “sediment,” the court concluded a plain language analysis of the statute does not indicate Congress unambiguously intended to exempt stormwater discharges contaminated only with sediment from the NPDES permitting process. Similarly, the court concluded the legislative history of section 402(l)(2), which included the history of section 323 of the Energy Policy Act, did not unambiguously indicate whether Congress intended to exempt such discharges. Because the Ninth Circuit could not find evidence to show Congress intended to exempt stormwater discharges contaminated only by sediment, the court moved to step two of the Chevron test, which requires the court to determine if an agency’s interpretation is based on a permissible construction of the statute.[15]

Applying step two of Chevron, the Ninth Circuit held EPA’s interpretation of CWA section 402(l)(2), as amended by the Energy Policy Act, was an impermissible construction of the statute. EPA argued that “‘because sediment is the pollutant most commonly associated with construction activities,’ Congress must have meant to exempt all construction-related sediment when it made construction activities eligible for the exemption.”[16] However, the court concluded EPA’s interpretation of the amended section 402(l)(2) was arbitrary and capricious because the agency changed its position on what constitutes contamination.

In reaching a conclusion, the court determined that EPA did not adequately justify the reason for changing the agency’s position on the meaning of “contamination” under section 402(l)(2). In reviewing the statements made by EPA during the rulemaking process prior to the rulemaking under the Energy Policy Act, the court noted the agency previously recognized that stormwater polluted with sediment caused “serious water quality impacts”[17] and that oil and gas facilities had an obligation to apply for an NPDES permit for stormwater runoff contaminated only with sediment.[18] Because EPA’s change from its prior stance regarding the impact of stormwater discharge containing only sediment represented a “complete departure from its previous interpretation,” the court characterized EPA as having taken an “inconsistent and conflicting position” regarding whether NPDES permits were required for oil and gas construction activity runoff contaminated solely with sediment.[19] Consequently, the Ninth Circuit concluded that EPA’s regulation was arbitrary and capricious, and was therefore an impermissible construction of section 402(l)(2) of the CWA. In sum, the Ninth Circuit granted NRDC’s petition for review, vacated the challenged rule, and remanded the matter to EPA for further proceedings.

Judge Callahan dissented from the majority’s opinion. Although Judge Callahan agreed with the majority’s conclusion under Chevron step one, Judge Callahan disagreed with the majority’s conclusion that, under Chevron step two, the EPA rule was an impermissible interpretation of the statute. Pointing out that an “agency interpretation [that] contradicts a prior agency position is not fatal,”[20] Judge Callahan argued that EPA’s interpretation of the statute was a reasonable construction and that EPA included “a reasoned analysis” that adequately explained the agency’s reasons for the modification.[21] Additionally, Judge Callahan noted, “there appears to be no authority that would compel EPA to stay its hand until Congress specifically amended the ambiguous exemption” to expressly include “sediment.”[22] Therefore, Judge Callahan concluded EPA made a reasonable choice in adopting the revised interpretation and would have deferred to the agency’s decision.


[1] The other environmental groups involved were the Oil and Gas Accountability Project (OGAP), Amigos Bravos, and Powder River Basin Resource Council.

[2] Federal Water Pollution Control Act, 33 U.S.C. §§ 1251-1387 (2006).

[3] See id. § 1342.

[4] Under section 402(l) of the CWA,

[t]he Administrator shall not require a permit under this section . . . for discharges of stormwater runoff from mining operations or oil and gas exploration, production, processing, or treatment operations or transmission facilities, composed entirely of flows which are from conveyances or systems of conveyances (including but not limited to pipes, conduits, ditches, and channels) used for collecting and conveying precipitation runoff and which are not contaminated by contact with, or do not come into contact with, any overburden, raw material, intermediate products, finished product, byproduct, or waste products located on the site of such operations.

Id. (emphasis added).

[5] Natural Res. Def. Council v. U.S. Envtl. Prot. Agency (NRDC I), 966 F.2d 1292, 1307 (9th Cir. 1992).

[6] See National Pollutant Discharge Elimination System Permit Application Regulations for Storm Water Discharges, 55 Fed. Reg. 47,990, 48,033-34 (Nov. 16, 1990) (codified at 40 C.F.R. pts. 122-124).

[7] Pub. L. No. 109-58, § 323, 119 Stat. 694 (codified as amended at 33 U.S.C. § 1362(34)).

[8] Natural Res. Def. Council v. U.S. Envtl. Prot. Agency (NRDC II), 526 F.3d 591, 599 (9th Cir. 2008) (quoting section 323 of the Energy Policy Act).

[9] Amendments to the National Pollutant Discharge Elimination System (NPDES) Regulations for Storm Water Discharges Associated With Oil and Gas Exploration, Production, Processing, or Treatment Operations, or Transmission Facilities, 71 Fed. Reg. 894 (proposed Jan. 6, 2006) (codified at 40 C.F.R. pt. 122).According to EPA, “This proposed action would modify [NPDES] regulations to provide that certain storm water discharges from field activities, including construction, associated with oil and gas exploration, production, processing, or treatment operations, or transmission facilities would be exempt from [NPDES] permit requirements.” Id.

[10] Amendments to the National Pollutant Discharge Elimination System (NPDES) Regulations for Storm Water Discharges Associated With Oil and Gas Exploration, Production, Processing, or Treatment Operations or Transmission Facilities, 71 Fed. Reg. 33,628 (June 12, 2006) (codified at 40 C.F.R. pt. 122).

[11] 5 U.S.C. §§ 551-559, 701-06, 1305, 3105, 3344, 4301, 5335, 5362, 7521 (2006).

[12] Id. § 706(2)(A).

[13] 467 U.S. 837, 842-44 (1984).

[14] NRDC II, 526 F.3d 591, 603 (9th Cir. 2008); see also Chevron, 467 U.S. at 842-43.

[15] Chevron, 467 U.S. at 843.

[16] NRDC II, 526 F.3d at 606 (quoting Amendments to the National Pollutant Discharge Elimination System (NPDES) Regulations for Storm Water Discharges Associated With Oil and Gas Exploration, Production, Processing, or Treatment Operations, or Transmission Facilities, 71 Fed. Reg. 33,628, 33,634 (Jun. 12, 2006) (codified at 40 C.F.R. pt. 122)).

[17] National Pollutant Discharge Elimination System Permit Application Regulations for Storm Water Discharges, 55 Fed. Reg. 47,990, 48,033-34 (Nov. 16, 1990) (codified at 40 C.F.R. pts. 122, 123, 124).

[18] 40 C.F.R. § 122.26(c)(1)(iii)(C) (1990).

[19] NRDC II, 526 F.3d at 607.

[20] Smiley v. Citibank (S.D.), 517 U.S. 735, 742 (1996).

[21] NRDC II, 526 F.3d at 609.

[22] Id. at 610.