United States Court of Appeals
FOR THE DISTRICT OF COLUMBIA CIRCUIT
Argued October 17, 2008 Decided April 17, 2009
No. 07-1247
CENTER FOR BIOLOGICAL DIVERSITY,
PETITIONER
v.
UNITED STATES DEPARTMENT OF THE INTERIOR,
RESPONDENT
AMERICAN PETROLEUM INSTITUTE,
INTERVENOR
Consolidated with 07-1344
On Petitions for Review of an
Order of the Department of Interior
William J. Snape III argued the cause for petitioner Center
for Biological Diversity. On the briefs were Matthew Vespa,
Andrea A. Treece, Miyoko Sakashita, and Brendan R.
Cummings.
Peter H. Van Tuyn argued the cause and filed the briefs for
petitioners Native Village of Point Hope, et al. James B.
Dougherty entered an appearance.
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Janis M. Searles was on the brief for amici curiae Ocean
Conservancy, et al. in support of petitioners.
Deborah A. Sivas was on the brief for amici curiae W.
Michael Hanemann and Charles Kolstad in support of
petitioners.
Sambhav N. Sankar, Attorney, U.S. Department of Justice,
argued the cause for respondent. With him on the brief was
Ryan D. Nelson, Deputy Assistant Attorney General. Katherine
W. Hazard, Attorney, entered an appearance.
Steven J. Rosenbaum argued the cause for intervenor. With
him on the brief were Theodore L. Garrett, Mark W. Mosier,
and Erik G. Milito.
Before: SENTELLE, Chief Judge, and GINSBURG and
ROGERS, Circuit Judges.
Opinion for the Court filed by Chief Judge SENTELLE.
Concurring opinion filed by Circuit Judge ROGERS.
SENTELLE, Chief Judge: In August 2005, the United States
Department of Interior (Interior) began the formal administrative
process to expand leasing areas within the Outer Continental
Shelf (OCS) for offshore oil and gas development between 2007
and 2012. This new five-year Leasing Program included an
expansion of previous lease offerings in the Beaufort, Bering,
and Chukchi Seas off the coast of Alaska. Petitioners filed
independent petitions for review challenging the approval by the
Secretary of the Interior (Secretary) of this Leasing Program on
various grounds. Specifically, Petitioners argue that: (1) the
Leasing Program violates both the Outer Continental Shelf
Lands Act (OCSLA), 43 U.S.C. §§ 1331-1356a, and the
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National Environmental Policy Act of 1969 (NEPA), 42 U.S.C.
§§ 4321-4370f, because Interior failed to take into consideration
both the effects of climate change on OCS areas and the Leasing
Program’s effects on climate change (the climate change
claims); (2) the Leasing Program also violates both OCSLA and
NEPA because Interior approved the Program without
conducting sufficient biological baseline research for the three
Alaskan seas, and further failed to provide a research plan
detailing how it would obtain this baseline data before the next
stage of the Program; (3) Interior violated the Endangered
Species Act of 1973 (ESA), 16 U.S.C. §§ 1531-1544, by failing
to consult with either the U.S. Fish and Wildlife Service (Fish
and Wildlife) or the National Marine Fisheries Service (NMFS)
about potential harm to endangered species in the OCS planning
areas before it adopted the Leasing Program; and (4) the Leasing
Program violates OCSLA because it irrationally relied on an
insufficient study by the National Oceanographic and
Atmospheric Administration (the NOAA study) in assessing the
environmental sensitivity of the OCS planning areas in the
Leasing Program. We hold that Petitioners’ NEPA-based
climate change claim, Petitioners’ NEPA baseline data claim,
and Petitioners’ ESA claim are not yet ripe for review. We
therefore dismiss the petition with respect to these claims.
Nevertheless, we conclude that Petitioners’ remaining
OCSLA-based challenges are all justiciable. Of these three
remaining claims, Petitioners’ OCSLA-based climate change
claims and their OCSLA-rooted baseline data challenge
ultimately lack merit and must fail. However, we find
meritorious Petitioners’ challenge to the Leasing Program on
grounds that the Program’s environmental sensitivity rankings
are irrational. Accordingly, we vacate the Leasing Program, and
remand the Program to the Secretary for reconsideration in
accordance with this opinion.
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I. BACKGROUND
A. Introduction
The Outer Continental Shelf is an area of submerged lands,
subsoil, and seabed that lies between the outer seaward reaches
of a state’s jurisdiction and that of the United States. 43 U.S.C.
§ 1331(a). The OCS generally extends from 3 miles to 200
miles off the United States coast. This action concerns a
Leasing Program approved by Interior that includes a potential
expansion of previous lease offerings in the Beaufort, Bering,
and Chukchi Seas off the coast of Alaska. Each of these seas is
home to a number of species of wildlife. For instance, the
Beaufort and Chukchi Seas are home to two polar bear
populations. The North Pacific right whale, an endangered
marine mammal, is known to inhabit the Bering Sea. Bowhead
whales are also known to feed and migrate through each of these
seas. In addition, a number of other species of whale, seals, the
Pacific walrus, and various seabirds are indigenous to these seas.
Three petitioners—Center for Biological Diversity, Alaska
Wilderness League, and Pacific Environment—are non-profit
activist organizations whose members have been working to
preserve and protect the waters and living environments off the
coast of Alaska. The remaining petitioner—the Native Village
of Point Hope, Alaska—is a federally recognized tribal
government whose members use the Chukchi Sea coast for
subsistence hunting, fishing, whaling, and gathering, as well as
cultural and religious activities.
B. Outer Continental Shelf Lands Act
OCSLA establishes a procedural framework under which
Interior may lease areas of the OCS for purposes of exploring
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and developing the oil and gas deposits of the OCS’s submerged
lands. See 43 U.S.C. §§ 1334, 1337; see also California v. Watt,
(Watt I), 668 F.2d 1290, 1295-1300 (D.C. Cir. 1981). In order
to ensure “the expeditious but orderly development of OCS
resources,” Watt I, 668 F.2d at 1297, OCSLA provides that
Interior undertake a four-stage process in order to develop an
offshore oil well. See Sec’y of the Interior v. California, 464
U.S. 312, 337 (1984). As we noted in Watt I, the leasing
program’s four-stage process is “pyramidic in structure,
proceeding from broad-based planning to an increasingly
narrower focus as actual development grows more imminent.”
Watt I, 668 F.2d at 1297. This multi-tiered approach was
designed “to forestall premature litigation regarding adverse
environmental effects that . . . will flow, if at all, only from the
latter stages of OCS exploration and production.” Sec’y of
Interior, 464 U.S. at 341.
First, during the preparation stage, Interior creates a leasing
program by preparing a five-year schedule of proposed lease
sales. 43 U.S.C. § 1344. At this stage, “prospective lease
purchasers acquire no rights to explore, produce, or develop”
any of the areas listed in the leasing program. Sec’y of Interior,
464 U.S. at 338. Second, during the lease-sale stage, Interior
solicits bids and issues leases for particular offshore leasing
areas. 43 U.S.C. § 1337(a). Third, during the exploration stage,
Interior reviews and determines whether to approve the lessees’
more extensive exploration plans. 43 U.S.C. § 1340. Interior
allows this exploration stage to proceed only if it finds that the
lessees’ exploration plan “will not be unduly harmful to aquatic
life in the area, result in pollution, create hazardous or unsafe
conditions, unreasonably interfere with other uses of the area, or
disturb any site, structure, or object of historical or archeological
significance.” 43 U.S.C. § 1340(g)(3). Fourth and final is the
development and production stage. During this stage, Interior
and those affected state and local governments review an
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additional and more detailed plan from the lessee. 43 U.S.C. §
1351. If Interior finds that the plan would “probably cause
serious harm or damage . . . to the marine, coastal or human
environments,” then the plan, and consequently the leasing
program, may be terminated. 43 U.S.C. § 1351(h)(1)(D)(i).
The Leasing Program at issue has only completed its first
stage—preparation of the five-year program under Section 18 of
OCSLA, 43 U.S.C. § 1344. Under Section 18, the Secretary is
required to prepare, periodically revise, and maintain “an oil and
gas leasing program” that consists of “a schedule of proposed
lease sales indicating, as precisely as possible, the size, timing,
and location of leasing activity which he determines will best
meet national energy needs for the five-year period following its
approval or reapproval.” 43 U.S.C. § 1344(a). The Secretary
must prepare and maintain a leasing program consistent with
several principles. First, the Secretary must ensure that a leasing
program is “conducted in a manner which considers economic,
social, and environmental values of the renewable and
nonrenewable resources contained in the [OCS], and the
potential impact of oil and gas exploration on other resource
values of the [OCS] and the marine, coastal, and human
environments.” 43 U.S.C. § 1344(a)(1). Second, the Secretary
must consider additional factors with respect to the timing and
location of exploration, development, and production of oil and
gas in particular OCS areas. These factors include, inter alia: a
region’s “existing information concerning the geographical,
geological, and ecological characteristics”; “an equitable sharing
of developmental benefits and environmental risks among the
various regions”; “the interest of potential oil and gas producers
in the development of oil and gas resources”; “the relative
environmental sensitivity and marine productivity of different
areas of the [OCS]”; and “relevant environmental and predictive
information for different areas of the [OCS].” 43 U.S.C. §§
1344(a)(2)(A), (B), (E), (G), (H). Next, Interior must ensure,
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“to the maximum extent practicable,” that the timing and
location of leasing occurs so as to “obtain a proper balance
between the potential for environmental damage, the potential
for the discovery of oil and gas, and the potential for adverse
impact on the coastal zone.” 43 U.S.C. § 1344(a)(3). Finally
Interior’s leasing activities must ensure that winning lessees
receive “fair market value for the lands leased and the rights
conveyed by the Federal Government.” 43 U.S.C. § 1344(a)(4).
Other provisions of OCSLA that are relevant to the leasing
process are Sections 18(b) and 20. See 43 U.S.C. §§ 1344(b),
1346. Section 18(b) of OCSLA calls for Interior to include
estimates of the appropriations and staff required to conduct and
prepare the leasing program, including appropriations and staff
estimates needed to conduct environmental studies and prepare
an Environmental Impact Statement (EIS). 43 U.S.C. §
1344(b)(3). Section 20 of OCSLA also provides that,
subsequent to a first lease in a given area, the Secretary “shall
conduct such additional studies to establish environmental
information as he deems necessary and shall monitor the human,
marine, and coastal environments of such area or region in a
manner designed to provide time-series and data trend
information.” 43 U.S.C. § 1346(b).
C. National Environmental Policy Act
NEPA’s requirements are essentially “procedural in
character,” and are designed to “ensure solicitude for the
environment through formal controls and thereby help realize
the substantive goal of environmental protection.” North Slope
Borough v. Andrus, 642 F.2d 589, 598 (D.C. Cir. 1980).
Ultimately, NEPA ensures that an agency’s approval of a project
is “a fully informed and well-considered decision.” Id. at 599
(quoting Vermont Yankee Nuclear Power Corp. v. Natural
Resources Def. Council, Inc., 435 U.S. 519, 558 (1978)). To
8
that end, the statute requires that each agency “assess the
environmental consequences of ‘major [f]ederal actions’ by
following certain procedures during the decision-making
process.” Nevada v. Dep’t of Energy, 457 F.3d 78, 87 (D.C. Cir.
2006) (quoting 42 U.S.C. § 4332(2)(C)). Before an agency may
approve a particular project, it must prepare a “detailed
statement . . . [on, inter alia,] the environmental impact of the
proposed action,” “any adverse environmental effects which
cannot be avoided should the proposal be implemented,” and
“alternatives to the proposed action.” 42 U.S.C. §§
4332(2)(C)(i)-(iii). When faced with a multi-stage, pyramidic
program such as the Leasing Program at issue here, NEPA’s
regulations allow an agency to conduct a tiered approach to
preparing an EIS. See 40 C.F.R. § 1508.28; see also Nevada,
457 F.3d at 91 & n.9. Under this approach, an agency may issue
a broader EIS at the earlier “need and site selection” stage of a
program, and issue subsequent, more detailed environmental
impact statements at the program’s later, more site-specific
stage. See 40 C.F.R. § 1508.28.
D. Endangered Species Act
The ESA is designed to ensure that endangered species are
protected from government action. Under the ESA, each federal
agency is required to ensure that any action undertaken by the
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 critical animal habitats.
16 U.S.C. § 1536(a)(2). If an agency concludes that its action
“may affect” a listed species or critical habitat, then the agency
must pursue either formal or informal consultation with the
NMFS or Fish and Wildlife. See 50 C.F.R. §§ 402.13, 402.14.
If the agency determines that its action will not affect any listed
species or critical habitat, however, then it is not required to
consult with NMFS or Fish and Wildlife. See Southwest Center
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for Biological Diversity v. U.S. Forest Serv., 100 F.3d 1443,
1447 (9th Cir. 1996).
E. Leasing Program
The Five-Year Leasing Program in this case was first
developed on August 24, 2005. 70 Fed. Reg. 49,669. After
developing and publishing a draft proposed plan, see 71 Fed.
Reg. 7064 (Feb. 10, 2006), and reviewing commentary to that
draft plan, Interior published a “Proposed Plan” and an
accompanying draft EIS. Finally, Interior published its
“Proposed Final Plan” in April 2007 along with its Final EIS for
the approval stage of the Leasing Program. This was submitted
to Congress and the President, and was later approved by the
Secretary of Interior. In total, the Leasing Program has
scheduled 21 potential lease-sales between July 1, 2007 and
June 30, 2012 in eight areas of the OCS. Four of those potential
leasing areas are in the Beaufort, Bering, and Chukchi Seas off
the Alaska coast. At the time the petitions challenging the
approval of the Leasing Program were brought before this court,
Interior had not yet conducted any lease-sales in these regions.
Since that time, however, Interior has approved one lease-sale
in the disputed Alaskan sea areas, Chukchi Sea Lease-Sale 193,
which occurred on February 6, 2008. Petitioner Point Hope and
others challenged this lease-sale in the federal district court for
the District of Alaska.
II. JURISDICTION
The federal judiciary’s role is limited to resolving cases and
controversies. U.S. Const. art. III, § 2; see also Allen v. Wright,
468 U.S. 737, 750 (1984). Accordingly, “before we reach the
merits of any claim, we must first assure ourselves that the
dispute lies within the constitutional and prudential boundaries
of our jurisdiction.” Util. Air Regulatory Group v. EPA, 320
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F.3d 272, 277 (D.C. Cir. 2003) (quoting La. Envtl. Action
Network v. Browner, 87 F.3d 1379, 1382 (D.C. Cir. 1996)).
Additionally, we must avoid “premature adjudication . . . and
also . . . protect the agencies from judicial interference until an
administrative decision has been formalized and its effects felt
in a concrete way by the challenging parties.” Abbott Labs. v.
Gardner, 387 U.S. 136, 148-49 (1967). We therefore must
determine whether Petitioners have standing to bring their
claims. We must also ensure that Petitioners’ claims are ripe for
review. For the following reasons, we hold that Petitioners’
three OCSLA-based claims are justiciable. We also hold that
Petitioners’ NEPA-based climate change and baseline data
challenges, and their ESA claim are not yet ripe for review.
A. Climate Change Claims
Petitioners claim that Interior violated both OCSLA and
NEPA because Interior failed to consider both the economic and
environmental costs of the greenhouse gas emissions associated
with the Program and the effects of climate change on OCS
areas. In support of their claims, Petitioners advance two
different theories of standing. We address each in turn. We
hold that Petitioners lack standing on their substantive climate
change theory. We hold, however, that Petitioners have
standing to bring their climate change claims under their
procedural theory of standing.
1. Petitioners’ Substantive Theory of Standing
Under their substantive theory of standing, Petitioners argue
that Interior’s approval of the Program brings about climate
change, which in turn adversely affects the species and
ecosystems of those OCS areas, thereby threatening Petitioners’
enjoyment of the OCS areas and their inhabitants. In other
words, Petitioners contend that, absent Interior’s approval of the
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Program, the OCS areas at issue would not be subject to
environmental impacts allegedly brought about by climate
change associated with the burning of fossil fuels produced
under the Program.
To begin with, the Supreme Court’s recent decision in
Massachusetts v. EPA, 549 U.S. 497 (2007), does not govern
this issue. Its holding turned on the unique circumstances of that
case, which are not present here. In Massachusetts, a group of
private organizations petitioned the Environmental Protection
Agency (EPA) to begin regulating emissions of four greenhouse
gases, arguing that a rise in global temperatures and
climatological changes resulted from an increase in the
atmospheric concentration of greenhouse gases. After the EPA
denied the petition, the petitioners—joined by the
Commonwealth of Massachusetts—sought this Court’s review
of the EPA’s denial of their petition. The EPA maintained that
the petitioners lacked standing to bring such a petition because
the harm that they alleged—the effect of greenhouse gas
emissions on global warming—was widespread, and did not
individually affect any of the petitioners. Accordingly, the EPA
contended, petitioners failed to demonstrate a concrete and
particularized injury required to show standing under Article III.
After we upheld the EPA’s denial of the petition without
reaching a consensus on the standing issue, the Supreme Court
decided on review that the petitioners had standing to bring their
petition.
In its opinion, however, the Supreme Court made an effort
to note that its finding was based on the uniqueness of the case
before it. As the Court explained, it was “of considerable
relevance that the party seeking review . . . is a sovereign State
and not, as it was in Lujan v. Defenders of Wildlife, 504 U.S. 55
(1992), a private individual.” Massachusetts, 549 U.S. at 518.
The Court noted further that it was critical that Massachusetts
12
sought to assert its own rights as a state under the Clean Air Act,
and was not seeking to protect the rights of its citizens under the
Clean Air Act. Id. at 520 n.17. In light of these unique
circumstances, the Court afforded Massachusetts “special
solicitude” in the Court’s standing analysis due to
Massachusetts’s interests in ensuring the protection of the land
and air within its domain, and its “well-founded desire to
preserve its sovereign territory.” Id. at 519, 520. With respect
to Massachusetts’s injury, the Court found that Massachusetts
“owns a substantial portion of the state’s coastal property” that
had already been harmed by the EPA’s inaction, and that the
EPA’s failure to regulate these gases would cause additional
harm to its shoreline. Id. at 523. Though the Court found that
the risks of climate change were widely shared because global
sea levels had already begun to rise, it nevertheless concluded
that Massachusetts had shown a sufficiently particularized injury
because Massachusetts had alleged that its particular shoreline
had actually been diminished by the effects of climate change.
Id. In other words, by showing that climate change had
diminished part of its own shoreline, Massachusetts itself had
shown that it had been affected “in a personal and individual
way” by the EPA’s failure to regulate greenhouse gases.
Defenders of Wildlife, 504 U.S. at 560 n.1. Thus, Massachusetts
stands only for the limited proposition that, where a harm is
widely shared, a sovereign, suing in its individual interest, has
standing to sue where that sovereign’s individual interests are
harmed, wholly apart from the alleged general harm.
Assuming arguendo that Point Hope is a sovereign that
might be entitled to “special solicitude” under Massachusetts, it
is clear that Massachusetts does not govern this case. Point
Hope does not allege anywhere that it has suffered its own
individual harm apart from the general harm caused by climate
change, and its derivative effects on Point Hope’s members.
Point Hope does not allege that Interior’s acts will cause damage
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to, or otherwise adversely affect, any of its own territory. To the
contrary, each of Petitioners’ climate change claims are founded
on Interior’s Leasing Program actions and the effects of those
actions on the climate in general. Moreover, to the extent that
Petitioners allege that the Leasing Program caused any actual
harm to any territory, this harm is limited to areas of the
OCS—areas that are owned by the federal government, not by
a state or Native American tribe. Aside from these allegations
of generalized harm brought about by climate change,
Petitioners have not demonstrated that climate change would
directly cause any diminution of Point Hope’s territory any more
than anywhere else. Accordingly, without this necessary
element being present, we find that Massachusetts’s limited
holding does not extend to the standing analysis in this case.
Moreover, it is doubtful that Point Hope would be able to
assert a quasi-sovereign claim on behalf of its members against
the federal government, as Massachusetts had against the EPA.
Both the majority and dissenting opinions in Massachusetts
recognized the general rule that a sovereign is prohibited from
bringing an action to protect its citizens from the operation of
federal statutes. See Massachusetts, 549 U.S. at 520 n.17
(majority opinion); id. at 539 (Roberts, C.J., dissenting); see also
Massachusetts v. Mellon, 262 U.S. 447, 484-86 (1923). Here,
Point Hope does not allege any specific harm that it has suffered
individually as a result of Interior’s actions in approving the
Leasing Program. Instead, Point Hope is suing on behalf of its
members and their individual interests. As the Court has long
recognized, only the United States, and not the states, may
represent its citizens and ensure their protection under federal
law in federal matters. See Mellon, 262 U.S. at 485-86.
Outside of the very limited factual setting of Massachusetts,
the Supreme Court’s decision in Defenders of Wildlife sets forth
the test for standing. See Fla. Audubon Soc’y v. Bentsen, 94
14
F.3d 658 (D.C. Cir. 1996). In order for a petitioner to establish
standing, a petitioner must demonstrate that it has suffered a
concrete and particularized injury that is caused by, or fairly
traceable to, the act challenged in the litigation and redressable
by the court. Defenders of Wildlife, 504 U.S. at 560-61; Fla.
Audubon Soc’y, 94 F.3d at 663. In cases such as this, where the
petitioner is not the object of an alleged government action or
inaction, “standing is not precluded, but it is ordinarily
‘substantially more difficult’ to establish.” Defenders of
Wildlife, 504 U.S. at 562 (quoting Allen, 468 U.S. at 758). In
cases such as this, causation and redressability ordinarily hinge
on the actions of “independent actors not before the courts and
whose exercise of broad and legitimate discretion the courts
cannot presume either to control or to predict.” Defenders of
Wildlife, 504 U.S. at 562 (quoting ASARCO, Inc. v. Kadish, 490
U.S. 605, 615 (1989) (opinion of Kennedy, J.)). Accordingly,
the petitioner bears the burden of “adduc[ing] facts showing that
those [third-party] choices have been or will be made in such
manner as to produce causation and permit redressability of
injury.” Defenders of Wildlife, 504 U.S. at 562 (citing Warth v.
Seldin, 422 U.S. 490, 505 (1975)).
Petitioners’ substantive theory of standing fails because
Petitioners have not established either the injury or causation
element of standing. First, it is well-established that a party
must demonstrate that it has suffered an injury that affects it in
a “personal and individual way.” Defenders of Wildlife, 504
U.S. at 560 n.1. Standing analysis does not examine whether the
environment in general has suffered an injury. See Fla.
Audubon Soc’y, 94 F.3d at 665. And yet Petitioners’ substantive
argument focuses on just this type of injury: that climate change
might occur in the Arctic environment if the Leasing Program
is allowed to proceed. This type of injury is insufficient to
establish standing for two reasons. First, Petitioners’ alleged
injury runs afoul of the requirement that a justiciable injury must
15
be “actual or imminent, not conjectural or hypothetical.”
Defenders of Wildlife, 504 U.S. at 560 (internal quotation marks
omitted). “A threatened injury must be certainly impending to
constitute injury in fact.” Whitmore v. Arkansas, 495 U.S. 149,
158 (1990) (internal quotation marks omitted). Petitioners can
only aver that any significant adverse effects of climate change
“may” occur at some point in the future. This does not amount
to the actual, imminent, or “certainly impending” injury required
to establish standing. Second, climate change is a harm that is
shared by humanity at large, and the redress that Petitioners
seek—to prevent an increase in global temperature—is not
focused any more on these petitioners than it is on the remainder
of the world’s population. Therefore Petitioners’ alleged injury
is too generalized to establish standing.
Even if Petitioners were able to demonstrate an injury
sufficient for standing, their substantive theory would still fail
because Petitioners have failed to demonstrate a causal link
between the government action by Interior and Petitioners’
particularized injury. To properly establish causation, the injury
must be “‘fairly’ traceable to the challenged action.” Allen, 468
U.S. at 751. That is, the plaintiff must show that “it is
substantially probable . . . that the challenged acts of the
defendant, not of some absent third party, will cause the
particularized injury of the plaintiff.” Fla. Audubon Soc’y, 94
F.3d at 663 (citing Allen, 468 U.S. at 753 n.19). The more
attenuated or indirect the chain of causation between the
government’s conduct and the plaintiff’s injury, the less likely
the plaintiff will be able to establish a causal link sufficient for
standing. See Allen, 468 U.S. at 757-58.
In this case, Petitioners rely on too tenuous a causal link
between their allegations of climate change and Interior’s action
in the first stage of this Leasing Program. In order to reach the
conclusion that Petitioners are injured because of Interior’s
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alleged failure to consider the effects of climate change with
respect to the Leasing Program, Petitioners must argue that:
adoption of the Leasing Program will bring about drilling;
drilling, in turn, will bring about more oil; this oil will be
consumed; the consumption of this oil will result in additional
carbon dioxide being dispersed into the air; this carbon dioxide
will consequently cause climate change; this climate change will
adversely affect the animals and their habitat; therefore
Petitioners are injured by the adverse effects on the animals they
enjoy. Such a causal chain cannot adequately establish
causation because Petitioners rely on the speculation that various
different groups of actors not present in this case—namely, oil
companies, individuals using oil in their cars, cars actually
dispersing carbon dioxide—might act in a certain way in the
future. Moreover, Petitioners’ causal chain fails to take into
account that, at each successive stage of the Leasing Program,
the law requires that Interior conduct additional and more
detailed assessments of the Program’s potential effect on the
proposed leasing areas. See 43 U.S.C. §§ 1340(g)(3),
1351(h)(1)(D)(i). As mentioned previously, these additional
analyses could scuttle a leasing program if the environmental
effects of that program are found to be excessive. See supra
Section I.B. Petitioners therefore also do not have standing
because they cannot adequately establish causation.
Accordingly, Petitioners’ substantive theory of standing fails.
2. Petitioners’ Procedural Theory of Standing
Alternatively, Petitioners argue that they are injured by
Interior’s failure to comply with both OCSLA and NEPA
requirements. Specifically, Petitioners claim that Interior
violated both OCSLA and NEPA because Interior failed to
consider both the economic costs of the greenhouse gas
emissions associated with the Program and the effects of climate
change on OCS areas. As the Supreme Court noted in
17
Defenders of Wildlife, a plaintiff may have standing if it can
show that an agency failed to abide by a procedural requirement
that was “designed to protect some threatened concrete interest”
of the plaintiff. Defenders of Wildlife, 504 U.S. at 573 n.8. In
such cases, the omission of a procedural requirement does not,
by itself, give a party standing to sue. Fla. Audubon Soc’y, 94
F.3d at 664. Rather, “a procedural-rights plaintiff must show
not only that the defendant’s acts omitted some procedural
requirement, but also that it is substantially probable that the
procedural breach will cause the essential injury to the plaintiff’s
own interest.” Id. at 664-65. A plaintiff “must show that he is
not simply injured as is everyone else, lest the injury be too
general for court action, and suited instead for political redress.”
Id. at 667 n.4.
Petitioners may bring both their OCSLA- and NEPA-based
climate change claims under their procedural standing theory.
Petitioners have shown that they possess a threatened
particularized interest, namely their enjoyment of the indigenous
animals of the Alaskan areas listed in the Leasing Program. The
Supreme Court has noted that “the desire to use or observe an
animal species, even for purely esthetic purposes, is undeniably
a cognizable interest for purpose of standing.” Defenders of
Wildlife, 504 U.S. at 562-63. This interest, however, will not
suffice on its own “without any description of concrete plans, or
indeed even any specification of when” the plaintiff will be
deprived of the opportunity to observe the potentially harmed
species. Id. at 564. Petitioners’ affidavits demonstrate a
sufficiently immediate and definite interest in enjoyment of the
animals. Petitioners’ members have detailed in their affidavits
definitive dates in the near future. Second, Petitioners have
shown, solely for the sake of an Article III standing analysis,
that Interior’s adoption of an irrationally based Leasing Program
could cause a substantial increase in the risk to their enjoyment
of the animals affected by the offshore drilling, and that our
18
setting aside and remanding of the Leasing Program would
redress their harm.
B. NEPA Climate Change and Baseline Data Claims
We next consider the justiciability of Petitioners’ climate
change and baseline data claims under NEPA. Petitioners
contend that Interior failed to account for (1) the present and
future impact of climate change on the Program areas, and (2)
the impact on climate change of the additional consumption
caused by the Program. They also contend that Interior has
effectively conceded that there is insufficient data detailing the
baseline biological condition of the Beaufort, Bering, and
Chukchi Seas in the Leasing Program because Interior has
admitted that there are gaps in the baseline research for these
areas. Petitioners argue that Interior cannot adequately describe
the affected areas, as required by 40 C.F.R. § 1502.15, until it
conducts additional research to close these gaps, and completely
establish the baseline conditions. Interior’s failure to conduct
this research to close the baseline data gaps therefore violates
NEPA. In addition, Petitioners contend that Interior has violated
40 C.F.R. § 1502.22 because Interior has not disclosed to what
extent this baseline information is either unavailable or absent,
and has failed to provide this information, which is required to
assess the environmental condition of 40 C.F.R. § 1502.15.
Here, Petitioners’ NEPA-based claims are not ripe due to
the multiple stage nature of the Leasing Program. This court’s
decision in Wyoming Outdoor Council v. United States Forest
Service, 165 F.3d 43 (D.C. Cir. 1999), is instructive here. In
Wyoming Outdoor Council, the court was faced with a NEPA
challenge to a multi-stage on-shore leasing program similar to
the Leasing Program at hand. The Wyoming Outdoor Council
petitioners argued that the Forest Service violated NEPA
because it approved an oil-and-gas leasing program without first
19
determining whether an adequate site-specific environmental
review had been performed. As here, the petitioners’ challenge
in Wyoming Outdoor Council was brought at the early stage of
the program that involved only “the identification and mapping
of areas that might be suitable for leasing.” Id. at 45. The court
dismissed the petitioners’ NEPA challenge as unripe, finding
that an agency’s NEPA obligations mature only once it reaches
a “critical stage of a decision which will result in ‘irreversible
and irretrievable commitments of resources’ to an action that
will affect the environment.” Id. at 49 (quoting Mobil Oil Corp.
v. FTC, 562 F.2d 170, 173 (2d Cir. 1977)). In the context of
multiple-stage leasing programs, we ultimately held that “the
point of irreversible and irretrievable commitment of resources
and the concomitant obligation to fully comply with NEPA do
not mature until leases are issued.” Wyoming Outdoor Council,
165 F.3d at 49.
Applying this reasoning here, Petitioners’ NEPA challenges
are not ripe for review. At the point that Petitioners filed their
petitions, Interior had only approved the Leasing Program at
issue. No lease-sales had yet occurred. The Leasing Program
here had therefore not yet reached that “critical stage” where an
“irreversible and irretrievable commitment of resources” has
occurred that will adversely affect the environment. See id.
Additionally, any harm that might befall Petitioners by
having to wait until the actual leasing stage to bring their claims
is outweighed by the harm to Interior (and other agencies).
Allowing a petitioner to bring such NEPA challenges to a
leasing program when no rights have yet been implicated, or
actions taken, would essentially create an additional procedural
requirement for all agencies adopting any segmented program.
This would impose too onerous an obligation, and would require
an agency to divert too many of its resources at too early a stage
in the decision-making process. By contrast, Petitioners suffer
20
little by having to wait until the leasing stage has commenced in
order to receive the information it requires. In the meantime, as
Interior points out, no drilling will have occurred, and
consequently, no harm will yet have occurred to the animals or
their environment.1
Petitioners argue, however, that the Supreme Court’s
decision in Ohio Forestry Association, Inc. v. Sierra Club, 523
U.S. 726 (1998), forestalls a conclusion that their NEPA
challenges are not ripe. Specifically, Petitioners point to the
Court’s statement that “a person with standing who is injured by
a failure to comply with the NEPA procedure may complain of
that failure at the time the failure takes place, for the claim can
1
Petitioners claim that Interior’s adoption of the Program
could result in further exploration and seismic testing by third parties
in the Program areas. Petitioners fail to point to any evidence that the
Program itself authorizes anyone to conduct seismic testing or engage
in any other activity detrimental to wildlife in the Program areas. Nor
does anything in the record suggest that seismic testing or other
exploration activities have been or will be conducted without being
separately authorized by the Secretary of Interior. Cf. 30 C.F.R. §
251.4 (requiring permit for geological and geophysical exploration,
including seismic testing and test drilling, of the OCS); Mineral Mgmt
Svc., Dep’t of the Interior, Recent G & G Permit Applications, Alaska
OCS Region, http://www.mms.gov/alaska/re/recentgg/recentgg.htm
(last visited Mar. 30, 2009). Moreover, the fact that Interior
conducted one lease-sale in the Chukchi Sea since the time these
petitions for review were filed does not make either Petitioners’ NEPA
claims or its ESA claim more ripe because Interior apparently
undertook the additional requisite steps under NEPA and ESA prior
to conducting that one lease-sale. See Chukchi Sea Planning Area Oil
and Gas Lease Sale 193 and Seismic Surveying Activities in the
Chukchi Sea, 72 Fed. Reg. 32,860 (June 14, 2007) (notice of
availability of a Final Environmental Impact Statement). Point Hope
and others have challenged the validity of this lease-sale in federal
court in Alaska, and it is not at issue here.
21
never get riper.” Id. at 737. Accordingly, Petitioners argue that
their NEPA claims are justiciable because, as the Court noted,
they cannot get any riper.
Ohio Forestry does not control. First, the case concerned
a claim that the Forest Service had violated the National Forest
Management Act of 1976 (NFMA), and whether that claim was
ripe for review. The quotation Petitioners rely on was therefore
dicta. See id. at 737. True, considered dicta of the Supreme
Court has long been regarded as forceful, even though it is not
binding. See Cohens v. Virginia, 19 U.S. (6 Wheat.) 264, 399
(1821). Nevertheless, in Ohio Forestry, the Court did not opine
that the obligation to conduct research under NEPA begins the
moment an OCSLA Leasing Program is adopted, as Petitioners
suggest. Ohio Forestry, 523 U.S. at 737. To the contrary, the
Supreme Court did not address when the obligation to provide
research under NEPA began. Id. The Court noted only that
NEPA claims do not get any riper than they are at the moment
a violation occurred. Id. It was not resolving the point at which
such a violation would occur. Id. Wyoming Outdoor Council,
by contrast, fills in this gap by stating that a NEPA obligation
commences once the agency reaches a “critical stage of a
decision”—specifically, the leasing stage. Wyoming Outdoor
Council, 165 F.3d at 49. It stands to reason that, applying Ohio
Forestry, Petitioners’ NEPA claims would not get any riper than
at the time NEPA’s obligation commenced and was disregarded.
That obligation has not yet occurred because Interior has only
reached the Leasing Program issuance stage, and has not yet
begun the leasing stage. Accordingly, Ohio Forestry does not
alter our analysis.
For these reasons, Petitioners’ NEPA claims are not ripe.
22
C. ESA Claim
When it approved the Leasing Program, Interior stated that
it did not need to engage in any consultation concerning the
Program’s impacts on threatened and endangered species at this
preliminary stage of the Program. Instead, Interior indicated
that it would comply with the ESA’s Section 7 requirements
once the Program reached its later stages. See 16 U.S.C. § 1536.
Petitioners argue that Interior’s failure to conduct such a
consultation at the approval stage of the Leasing Program
violates 16 U.S.C. § 1536(a)(2). Interior counters that
Petitioners’ Section 7 claim is unripe.
Section 7 of the ESA clearly sets forth that:
Each Federal agency shall, in consultation with [either
the Fisheries Service or the Fish and Wildlife Services],
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 . . . to be critical.
16 U.S.C. § 1536(a)(2). Accordingly, an agency must consult
with NMFS or Fish and Wildlife if the agency concludes that its
action “may affect” a listed species or critical habitat. See 50
C.F.R. §§ 402.13, 402.14.
In order to resolve the ripeness of Petitioners’ ESA claim,
our inquiry must therefore focus on whether an agency’s
approval of a leasing program “may affect” a listed species or
critical habitat. Petitioners argue that we should consider the
Leasing Program’s potential effect on endangered species as a
whole in resolving this issue. In other words, Petitioners
23
advocate a “but for” approach: if, because of events traceable to
the agency’s adoption of the multiple-stage leasing plan, it is
possible that an endangered species will be affected, then the
agency must consult with NMFS or Fish and Wildlife. Interior
advocates more of a “proximate cause” approach, viewing each
stage of the agency action as a separate intervening act, and
linking any effect on endangered species to that particular stage.
Our holding in North Slope Borough v. Andrus, 642 F.2d
589 (D.C. Cir. 1980), best informs the resolution of this issue.
In North Slope, representatives of environmental organizations
and native Alaskans sought to enjoin Interior from carrying out
a leasing program for oil and gas development in the Beaufort
Sea. Importantly, the leasing program in North Slope had
already reached the lease-sale stage; the program had been
approved by the Secretary, but no bids had been accepted, and
no leases had been executed. Id. at 593-94. Nevertheless, as in
this case, the North Slope petitioners argued that Interior’s
failure to consult with NMFS and Fish and Wildlife violated
Section 7 of the ESA. Assuming without deciding that a lease
sale and all subsequent program activities constituted “agency
action” under the ESA, we held that “satisfaction of the ESA
mandate that no endangered life be jeopardized must be
measured in view of the full contingent of OCSLA checks and
balances and all mitigating measures adopted in pursuance
thereof.” North Slope, 642 F.2d at 609. The segmented nature
of OCSLA Leasing Programs is such a mitigating measure
because it allows “graduated compliance with environmental
and endangered life standards, [thereby making] ESA
requirements more likely to be satisfied both in an ultimate and
a proximate sense.” Id. In other words, courts must consider
the ESA’s requirements in light of each particular leasing
program stage at issue because those stages are there by design.
24
Applying the reasoning in North Slope to the facts before
us, we conclude that Petitioners’ ESA claim is not yet ripe.
Given the multi-stage nature of leasing programs under OCSLA,
we must consider any environmental effects of a leasing
program on a stage-by-stage basis, and correspondingly evaluate
ESA’s obligations with respect to each particular stage of the
program. Regardless of whether there has been an agency
action under the ESA, the completion of the first stage of a
leasing program does not cause any harm to anything because it
does not require any action or infringe on the welfare of animals.
The welfare of animals is, by design, only implicated at later
stages of the program, each of which requires ESA consultation
and additional environmental review by Interior. See id. at 608-
09. In addition, at this initial stage, leasing programs may list
areas that Interior does not intend to lease. It is therefore not
certain, at least at this initial stage of the Leasing Program, that
any of the endangered species in the areas at issue may be
affected by the Program, as the proposed leases in these areas
might never come to pass. As a result, both this court and the
Secretary of the Interior “would benefit from postponing review
until the policy in question has sufficiently ‘crystallized’ by
taking on a more definite form.” Venetian Casino Resort, LLC
v. EEOC, 409 F.3d 359, 364 (D.C. Cir. 2005) (citing City of
Houston v. Dep't of Hous. & Urban Dev., 24 F.3d 1421, 1430-31
(D.C. Cir.1994)). Any hardship to Petitioners from delaying
review of their ESA claim until after Interior moves beyond this
initial stage of the Leasing Program is insufficient to outweigh
the institutional interests of the court and Interior.2 Petitioners’
ESA challenge at this initial stage of the Leasing Program is
therefore premature. See Atl. States Legal Found. v. EPA, 325
F.3d 281, 284-85 (D.C. Cir. 2003).
2
See note 1, supra.
25
D. OCSLA-based NOAA Study and Baseline Information
Claims
Finally, we conclude that we do have jurisdiction over both
of Petitioners’ remaining OCSLA-based claims. Specifically,
Petitioners argue that the Leasing Program violates OCSLA
because Interior approved the Program without conducting
sufficient biological baseline research. Petitioners also contend
that the Leasing Program violates Section 18(a)(2)(G) of
OCSLA because it relied on an insufficient NOAA study in
assessing the environmental sensitivity of the OCS planning
areas in the Leasing Program. See 43 U.S.C. § 1344(a)(2)(G).
First, as we did with Petitioners’ OCSLA-based climate
change claims, we conclude that Petitioners have standing to
bring these remaining two OCSLA-based claims. Petitioners
have shown that they possess a threatened particularized
interest, namely their enjoyment of the indigenous animals of
the Alaskan areas listed in the Leasing Program, and that they
have a sufficiently immediate and definite interest in enjoyment
of the animals. Second, Petitioners have also shown, solely for
the sake of Article III standing analysis, that Interior’s adoption
of an irrationally based Leasing Program could cause a
substantial increase in the risk to their enjoyment of the animals
affected by the offshore drilling, and that our setting aside and
remand of the Leasing Program would redress their harm. We
also conclude that both of these remaining OCSLA-based claims
are ripe for review, as both concern OCSLA requirements that
are implicated at the initial stage of a leasing program.
Accordingly, we may also proceed to the merits of these two
claims.
26
III. MERITS OF THE REMAINING
JUSTICIABLE CLAIMS
A. Standard of Review
This court utilizes a “hybrid” standard of review when
reviewing a leasing program for compliance with OCSLA. See
Watt I, 668 F.2d at 1300. Findings of ascertainable fact are
guided by the substantial evidence test. Id. at 1302. Under this
standard, evidence upon which a finding is made must be “more
than a scintilla,” but may be less than a preponderance of the
evidence. FPL Energy Maine Hydro LLC v. FERC, 287 F.3d
1151, 1160 (D.C. Cir. 2002). An agency’s policy judgments are
reviewed to ensure that “the decision is based on a consideration
of the relevant factors and whether there has been a clear error
of judgment.” Watt I, 668 F.2d at 1302. This court gives
substantial deference to the Secretary of Interior’s interpretation
of ambiguous provisions in OCSLA, so long as that
interpretation is a “permissible construction of the statute.” See
id. at 1302-03. However, a statutory interpretation that does not
effectuate Congress’ intent must fall. Id. at 1303.
B. OCSLA-based Climate Change Claims
Petitioners raise two distinct but related OCSLA-based
climate change claims. First, Petitioners argue that the Secretary
violated sections 18(a)(1) and (a)(3) of OCSLA by failing to
account for the environmental costs resulting from consumption
of the fossil fuels extracted from the OCS. Second, Petitioners
contend that Interior violated section 18(a)(2) of OCSLA
because Interior failed to adequately consider climate change
caused by consumption of these fossil fuels and the present and
future impact of climate change on OCS areas as section
18(a)(2)(H) requires. To the extent these claims concern
Interior’s alleged failure to consider the effects brought about by
27
consumption of oil and gas extracted under the Program, we
hold that OCSLA does not require Interior to consider the global
environmental impact of oil and gas consumption before
approving a Leasing Program. Therefore, OCSLA does not
require Interior to consider the further derivative environmental
impact that oil and gas consumption has on OCS areas.
Accordingly, Petitioners’ OCSLA climate change claims fail.
Contrary to Petitioners’ claims, the text of OCSLA does not
require Interior to consider the impact of consuming oil and gas
extracted under an offshore Leasing Program. Under Section
18(a) of OCSLA, Interior must prepare Leasing Programs so
that “the size, timing, and location of leasing activity . . . will
best meet national energy needs.” 43 U.S.C. § 1344(a). Section
18(a)(1) states further that Interior must consider the values of
resources “contained in the outer Continental Shelf,” as well as
“the potential impact of oil and gas exploration on other
resource values of the [OCS] and the marine, coastal and human
environments.” 43 U.S.C. § 1344(a)(1) (emphasis added).
Similarly, section 18(a)(3) states that “[t]he Secretary shall
select the timing and location of leasing . . . so as to obtain a
proper balance between the potential for environmental damage,
the potential for the discovery of oil and gas, and the potential
for adverse impact on the coastal zone.” 43 U.S.C. § 1344(a)(3).
We noted in Watt I that such a cost-benefit analysis of oil and
gas extraction under section 18(a)(3) is satisfactory when an
individual area’s potential benefits are weighed against its
potential costs. See Watt I, 668 F.2d at 1318. The Secretary
therefore need only consider the “potential for environmental
damage” on a localized area basis. And, under section 18(a)(2),
Interior is required to determine the impacts of “exploration,
development, and production” of oil and gas. As the statutory
language and our precedent show, Interior’s obligations under
OCSLA extend to assessing the relative impacts of production
and extraction of oil and gas on the localized areas in and around
28
where the drilling and extraction occurred. Interior need not
consider the impacts of the consumption of oil and gas after it
has been extracted from the OCS. OCSLA therefore concerns
the local environmental impact of leasing activities in the OCS
and does not authorize—much less require—Interior to consider
the environmental impact of post-exploration activities such as
consuming fossil fuels on either the world at large, or the
derivative impact of global fossil fuel consumption on OCS
areas.
Moreover, Interior’s continuing duty to promulgate five-
year Leasing Programs under OCSLA renders Interior’s
consideration of the effects of oil and gas consumption
unnecessary. Petitioners argue that Interior’s consideration of
the environmental impacts of greenhouse emissions associated
with the Program might have altered Interior’s ultimate
decisions concerning the Program’s leasing activities, such that
the OCS areas at issue here might not have been included in the
Program. But Petitioners’ argument ignores the fact that
Interior’s decisions about the size and location of leasing areas
or the timing of oil and gas extraction do not affect the impact
that consuming oil and gas may have on climate change. That
environmental impact is the same regardless of where and how
the oil and gas are extracted. Therefore, even if, as Petitioners
assert, Interior were not to adopt the Program at issue here,
Interior’s continuing duty to promulgate Leasing Programs
would compel it to promulgate a different Leasing Program,
potentially approving oil and gas extraction from other areas of
the OCS. This extraction would presumably lead to the same
overall consumption effects as those under the current Program.
Petitioners’ consumption-related claims appear to stem
from the flawed premise that, before Interior approves an
offshore oil and gas Leasing Program, it must first consider
whether it should extract oil and gas from the OCS at all. But
29
Congress has already decided that the OCS should be used to
meet the nation’s need for energy. Indeed, OCSLA instructs
Interior to ensure that oil and gas are extracted from the OCS in
an expeditious manner that minimizes the local environmental
damage to the OCS. See 43 U.S.C. § 1344. Interior simply
lacks the discretion to consider any global effects that oil and
gas consumption may bring about. Interior was therefore correct
to point out in its EIS that the more expansive effect of oil and
gas consumption is a matter for the Congress to consider “when
decisions are made regarding the role of oil and gas generally,
including domestic production and imports, in the Nation’s
overall energy policy.” Consequently, it was unnecessary for
Interior to consider the climate change effects brought about by
the consumption of oil and gas—either as oil and gas
consumption affects the global environment generally or the
OCS areas specifically.
Interior’s decision to limit its inquiry to the effect of the
Program’s production activities on climate change is consistent
with its obligations under OCSLA, and was not error. Here,
there is no doubt that Interior considered the effects of the
Program’s production activities on climate change generally,
and the present and future impact of climate change on the local
OCS areas. In the EIS, which Interior incorporated by reference
in its Program approval, Interior estimated the total amount of
greenhouse gas emissions that would result from leasing,
exploration, and development in the OCS, and examined the
cumulative impact of these emissions on the global
environment. Interior also noted that potential impacts are
“most pronounced in [the] Arctic Subregion,” and could affect
the areas of Alaska in which Petitioners assert an interest.
Accordingly, Petitioners’ OCSLA-based climate change claims
fail.
30
C. OCSLA Baseline Information Claim
In their OCSLA baseline data claim, Petitioners contend
that Interior lacked sufficient baseline biological information for
the Chukchi, Beaufort, and Bering Seas to rationally approve the
Leasing Program. According to Petitioners, Section 20(b) of
OCSLA requires Interior to establish, update, and monitor
baseline information for OCS planning areas in a leasing
program. See 43 U.S.C. § 1346(b). Petitioners argue that,
despite this obligation, Interior has admitted that gaps exist in
the data for the Beaufort, Bering, and Chukchi Seas.
Notwithstanding the existence of these information gaps,
Interior has indicated that it will defer the gathering of this data
to fill these gaps until the Leasing Program reaches the later
stages. Though Petitioners concede that Interior is not required
to conduct all the comprehensive baseline research before
approving the Leasing Program, Petitioners nevertheless argue
that, in order for Interior to comply with OCSLA, Interior must
either conduct comprehensive baseline research to fill these
information gaps, or provide a research plan detailing how
Interior intends to obtain this information before the next
OCSLA stages. Petitioners argue that such a research plan is
implicitly required by Section 18(b)(3) of OCSLA, which sets
forth Interior’s obligation to provide appropriations and staffing
estimates for conducting environmental studies and preparing an
EIS. See 43 U.S.C. § 1344(b)(3). Interior’s failure to comply
with either requirement before approving the Leasing Program
has prevented Interior from fully considering Section 18(a)(2)’s
factors, which, in turn, has skewed Interior’s balancing of those
factors under Section 18(a)(3) of OCSLA. See 43 U.S.C. §§
1344(a)(2)-(3). As a result, Petitioners argue, the Leasing
Program lacks any rational support.
This argument is wholly without merit. Though Section
20(b) imposes a requirement to conduct additional studies to
31
establish environmental information for a particular area, this
obligation commences “[s]ubsequent to the leasing and
development” of that area. 43 U.S.C. § 1346(b) (emphasis
added). Where, as here, Interior has merely completed the
approval stage of a leasing program, Section 20(b)’s additional
research requirements are not yet implicated. Indeed,
Petitioners’ proper concession that Interior is not required to
complete its comprehensive baseline research prior to approving
the Leasing Program confirms this interpretation. In fact, this
concession undermines Petitioners’ argument that such research
is required at the initial program approval stage. Having made
such a concession, Petitioners cannot now credibly argue that
Section 20(b) of OCSLA somehow required Petitioners to
complete this research before the Leasing Program was
approved.
Even if Petitioners were able to rely on Section 20(b) to
support their claim that the Leasing Program was irrational due
to gaps in the baseline data, this argument would falter because,
based on the record, Interior relied on substantial baseline
evidence in approving the Leasing Program. As its final EIS
demonstrates, Interior considered and chronicled the geological,
biological, and environmental information of the Beaufort,
Bering, and Chukchi Seas, and many of their inhabitants. To be
sure, a review of areas as wide and diversely populated as these
Arctic seas will likely miss some of the seas’ myriad inhabitants.
These gaps in information, however, must be considered in
conjunction with the “pyramidic structure” of a five-year leasing
program. Watt I, 668 F.2d at 1297. At this early stage of the
Leasing Program, the existence of some gaps in the baseline
data for these three seas is not fatal to the Leasing Program.
This is also tempered by the fact that Interior has recognized that
such gaps exist and has indicated its intention to conduct
additional research to close them. North Slope, 642 F.2d at 613
(affirming the district court’s denial of petitioners’ OCSLA
32
claim that research was insufficient because Interior
acknowledged that “[m]ore research is necessary; the research
is being done”).
Petitioners are therefore left with their only remaining
argument: to comply with OCSLA, Interior must provide a
research plan detailing how it attempts to obtain the necessary
baseline information before the next stage of the Leasing
Program. However, OCSLA does not set forth a requirement
that Interior must provide such a plan for obtaining this baseline
data. Petitioners’ claim that Section 18(b)(3) implicitly sets
forth such a requirement is off the mark. Section 18(b)(3) states
that a leasing program “shall include estimates of the
appropriations and staff required to . . . conduct environmental
studies and prepare any environmental impact statement.” 43
U.S.C. § 1344(b)(3). In other words, Section 18(b)(3) simply
requires that Interior estimate how many staff and how much
money it needs to obtain environmental impact information. It
does not require that Interior set forth a research plan detailing
what exact environmental information Interior needs, or how or
when Interior plans on obtaining that information. Petitioners’
interpretation is therefore counter to the clear language of the
statute. Accordingly, Petitioners’ baseline data claim must fail.
D. NOAA Study Claim
Section 18(a)(2)(G) of OCSLA requires agencies to
consider “the relative environmental sensitivity of . . . different
areas of the outer Continental Shelf.” 43 U.S.C. §
1344(a)(2)(G). In its efforts to comply with this requirement,
Interior ranked the environmental sensitivity of various program
areas in terms of only one factor: the “physical characteristics”
of the shoreline of those areas. This ranking was based on
Interior’s use of the Environmental Sensitivity Index, developed
by NOAA, which considered the sensitivity of different
33
shoreline areas to oil spills, and ranked them on that basis. The
study ranked each area on a scale of 1 to 10 (with 10 being a
rating for an area most likely to be damaged long-term by oil
spills). Petitioners contend that Interior’s sole reliance on this
study to measure the environmental sensitivity of the potential
OCS leasing areas in the Leasing Program renders the Program
improper. Interior counters that this court has stated that Section
18(a)(2)(G) “provides no method by which environmental
sensitivity . . . [is] to be measured.” Watt I, 668 F.2d at 1311.
Accordingly, Interior argues that its adoption of the NOAA
shoreline study to determine environmental sensitivity of OCS
areas is a policy judgment that is entitled to substantial
deference.
Interior’s argument is not consistent with controlling
precedent. Our decisions in California v. Watt (Watt II), 712
F.2d 584 (D.C. Cir. 1983), and Watt I set forth the standard for
Interior’s compliance with Section 18(a)(2)(G). In Watt II, we
affirmed our holding in Watt I that all that is required for
compliance with Section 18(a)(2)(G) is “that the Secretary make
a good faith determination of the relative environmental
sensitivity . . . of the various regions based upon the best
‘existing information’ available to him.” Watt II, 712 F.2d at
596 (quoting Watt I, 668 F.2d at 1313)). Accordingly, the
Secretary was “free to choose any methodology ‘so long as it is
not irrational.’” Watt II, 712 F.2d at 596 (quoting Watt I, 668
F.2d at 1320). The Secretary’s decision is not irrational so long
as it is “based on a consideration of the relevant factors.” Watt
I, 668 F.2d at 1317.
Interior’s interpretation of Section 18(a)(2)(G) is irrational.
It was not based on a consideration of the relevant factors set
forth therein. Section 18(a)(2)(G) states clearly that an agency
must assess the environmental sensitivity of “different areas of
the outer Continental Shelf” in order to make its determination
34
of when and where to explore and develop additional areas for
oil. 43 U.S.C. § 1344(a)(2)(G) (emphasis added). Based on this
language alone, Interior’s use of the NOAA study runs afoul of
this provision because it assesses only the effects of oil spills on
shorelines. Interior provides no explanation for how the
environmental sensitivity of coastal shoreline areas can serve as
a substitute for the environmental sensitivity of OCS areas,
when the coastline and proposed leasing areas are so distant
from each other. This interpretation runs directly counter to the
statutory language.
Moreover, though Watt II and Watt I afforded Interior a
great deal of leeway in determining how to comply with Section
18(a)(2)(G), they did not give Interior carte blanche to wholly
disregard a statutory requirement out of convenience. The law
plainly requires that Interior examine and compare the
environmental sensitivity of different areas of the OCS. Though
the law allows Interior to consider the environmental sensitivity
of onshore areas to OCS development, it plainly does not allow
Interior to consider only onshore areas. Interior’s sole focus on
the environmental sensitivity of shoreline areas to OCS
development therefore falls short of what Section 18(a)(2)(G)
requires. Accordingly, Interior’s Section 18(a)(2)(G) analysis
is inadequate.
Our conclusion that Interior failed to properly conduct an
environmental sensitivity analysis under Section 18(a)(2)(G)
does not end our inquiry. We have consistently linked the
adequacy of Interior’s analysis under Section 18(a)(2) with its
analysis under Section 18(a)(3). See Watt II, 712 F.2d at 599 &
n.75; Watt I, 668 F.2d at 1318. Section 18(a)(3) requires that,
when preparing a leasing program, Interior select, “to the
maximum extent practicable,” the “timing and location of
leasing . . . so as to obtain a proper balance between the potential
for environmental damage, potential for the discovery of oil and
35
gas, and the potential for adverse impact on the coastal zone.”
43 U.S.C. § 1344(a)(3). In essence, these three elements are “a
condensation of the factors specified in section 18(a)(2).” Watt
I, 668 F.2d at 1315. Though Section 18(a)(3) does not define
specifically how Interior shall balance these three elements,
Watt I, 668 F.2d at 1315, it stands to reason that a flawed
consideration of Section 18(a)(2) factors hinders Interior’s
ability to obtain a proper balance of the factors under Section
18(a)(3). Interior’s failure to properly consider the
environmental sensitivity of different areas of the OCS—areas
beyond the Alaskan coastline—has therefore also hindered
Interior’s ability to comply with Section 18(a)(3)’s balancing
requirement.
Consequently, on remand, the Secretary must first conduct
a more complete comparative analysis of the environmental
sensitivity of different areas “of the outer Continental Shelf,” 43
U.S.C. § 1344(a)(2)(G) (emphasis added), and “must at least
attempt to identify those areas whose environment and marine
productivity are most and least sensitive to OCS activity.” Watt
I, 668 F.2d at 1313. Though Interior may ultimately conclude
as a result of this additional analysis that the shorelines of the
Beaufort, Bering, and Chukchi Seas are the areas that are most
sensitive to OCS development, such a conclusion cannot be
reached without considering the effects of development on areas
of the OCS in addition to the shoreline. Once Interior has
conducted its Section 18(a)(2)(G) analysis, Interior must then
determine whether its reconsideration of the environmental
sensitivity analysis warrants the exclusion of any proposed area
in the Leasing Program. See Watt I, 668 F.2d at 1314. Finally,
having reconsidered its Section 18(a)(2) analysis, Interior must
reassess the timing and location of the Leasing Program “so as
to obtain a proper balance between the potential for
environmental damage, the potential for the discovery of oil and
gas, and the potential for adverse impact on the coastal zone,” as
36
required by Section 18(a)(3). 43 U.S.C. § 1344(a)(3).
IV. RELIEF
Section 23(c)(6) of OCSLA provides that, on review, a
court of appeals “may affirm, vacate, or modify any order or
decision or may remand the proceedings to the Secretary for
such further action as it may direct.” 43 U.S.C. § 1349(c)(6).
Petitioners request that we vacate the Leasing Program and
remand the Program to Interior for additional reconsideration.
In light of Interior’s failure to properly consider the relative
environmental sensitivity and marine productivity of different
areas of the OCS under Section 18(a)(2)(G), and its derivative
failure to strike a proper balance incorporating environmental
and coastal zone factors under Section 18(a)(3), we grant the
relief requested. Therefore, we vacate the Leasing Program and
remand the Program to the Secretary for reconsideration in
accordance with this opinion.
So ordered.
ROGERS, Circuit Judge, concurring: I join the court’s
opinion, but I write separately to emphasize two points. First,
because the court holds petitioners have standing to bring their
climate change claims on their “procedural theory” of standing,
Op. at 16-18, it is unnecessary for the court to reach the question
whether petitioners would also have standing under their
“substantive theory” of standing, Op. at 10-16, see, e.g., U.S.
Telecom Ass’n v. FCC, 295 F.3d 1326, 1331 n.4 (D.C. Cir.
2002). Determining the precise scope of the holding on standing
in Massachusetts v. EPA, 549 U.S. 497 (2007), and whether the
Native Village of Point Hope has identified by affidavit
particularized harms to its culture and way of life from climate
change sufficient to establish Article III standing, for example,
remain for another day, see Gersman v. Group Health Ass'n,
Inc., 975 F.2d 886, 897 (D.C. Cir. 1992). Second, as this appeal
concerns only stage one of the Secretary’s 5-Year Leasing
Program (2007-2012) under OCSLA, the court has no occasion
to opine regarding the Secretary’s discretion to consider the
global effects of oil and gas consumption, Op. at 29, other than
to hold that the Secretary is not required by OCSLA to consider
such effects at stage one.