Wildearth Guardians v. Jewell ( 2019 )

UNITED STATES DISTRICT COURT
FOR THE DISTRICT OF COLUMBIA
WILDEARTH GUARDIANS, et al., :
:
Plaintiffs, :
: Civil Action No.: 16-1724 (RC)
v. :
: Re Document Nos.: 55, 60, 61, 62, 63,
ZINKE, et al., : 71
:
Defendants, :
:
WESTERN ENERGY ALLIANCE, et al., :
:
Defendant-Intervenors :
MEMORANDUM OPINION
GRANTING IN PART PLAINTIFFS’ MOTION FOR SUMMARY JUDGMENT;
DENYING DEFENDANTS’ CROSS-MOTIONS FOR SUMMARY JUDGMENT;
DENYING MOTION FOR LEAVE TO FILE AMICUS BRIEF
I. INTRODUCTION
Climate change, and humanity’s ability to combat it, are increasingly prominent topics of
public discourse. This case concerns the attention the government must give climate change
when taking action that may increase its effects. Two non-profit organizations, WildEarth
Guardians (“WildEarth”) and Physicians for Social Responsibility (together, “Plaintiffs”) assert
that the United States Bureau of Land Management (“BLM”) violated federal law by not
sufficiently considering climate change when authorizing oil and gas leasing on federal land in
Wyoming, Utah, and Colorado. Those states and two industry organizations with interests in the
leases—the Western Energy Alliance and Petroleum Association of Wyoming (“Western
Alliance”), and the American Petroleum Association of Wyoming (“American Petroleum”)—
(together with BLM, “Defendants”) have intervened as defendants. Another organization, the
New York University School of Law’s Institute for Policy Integrity (the “Institute”), seeks to file
an amicus curiae brief in support of Plaintiffs.
Before the Court are the parties’ cross-motions for summary judgment and the Institute’s
motion to file an amicus brief. Having reviewed the record and the relevant law, the Court
concludes that—withholding judgment on whether BLM’s leasing decisions were correct—BLM
did not sufficiently consider climate change when making those decisions. BLM summarized
the potential on-the-ground impacts of climate change in the state, the region, and across the
country. It failed, however, to provide the information necessary for the public and agency
decisionmakers to understand the degree to which the leasing decisions at issue would contribute
to those impacts. In short, BLM did not adequately quantify the climate change impacts of oil
and gas leasing. Thus, for the reasons explained more thoroughly below, the Court grants
Plaintiffs’ motion in part, denies Defendants’ motions, and denies the Institute’s motion. 1
II. BACKGROUND
A. Statutory and Regulatory Framework
1. Mineral Leasing Act
Under the Mineral Leasing Act (“MLA”), 30 U.S.C. §§ 181–287, the Secretary of the
Interior is responsible for managing and overseeing mineral development on public lands in a
manner that “safeguard[s] . . . the public welfare.” Id. § 187. Subject to this general mandate,
the MLA provides for the development of oil and gas resources on federal land. Id. § 226; see
also AR3379. It requires that “[l]ease sales shall be held for each State where eligible lands are
available [for oil and gas development] at least quarterly and more frequently if the Secretary of
the Interior determines such sales are necessary.” 30 U.S.C. § 226(b)(1)(A). However, while oil
1
The Institute’s core arguments have been adequately addressed in the parties’ briefs.
2
and gas leasing is mandatory, the Secretary has discretion to determine where, when, and under
what terms and conditions oil and gas development should occur. Id. § 226; 43 C.F.R. § 3101.1-
2. Accordingly, the federal government may impose a broad range of stipulations on oil and gas
leases for federal land, including concerning the timing, pace, and scale of development. Id.
2. Federal Land Policy and Management Act
The MLA’s mandate to lease federal land for oil and gas development is carried out by
BLM, in strict compliance with the Federal Land Policy and Management Act of 1976
(“FLPMA”). 43 U.S.C. §§ 1701–1787. The FLPMA directs BLM to “manage the public lands
under principles of multiple use and sustained yield.” Id. § 1732(a). Under this mandate, the
FLPMA identifies “mineral exploration and production” as one of the “principal or major uses”
of public lands. Id. § 1702(l). As described below, the FLPMA establishes a series of steps that
BLM must take when leasing federal lands for oil and gas development. Id. § 1712(a); 43 C.F.R.
§ 1601.0-5(n). These steps are further governed by the National Environmental Policy Act
(“NEPA”).
3. National Environmental Policy Act
NEPA is the country’s “basic national charter for the protection of the environment.” 40
C.F.R. § 1500.1(a). Its purpose is “to promote efforts which will prevent or eliminate damage to
the environment and biosphere and stimulate the health and welfare of [humans],” 42 U.S.C. §
4321; to ensure that the federal government uses all practicable means to “assure for all
Americans safe, healthful, productive, and aesthetically and culturally pleasing surroundings”;
and to “attain the widest range of beneficial uses of the environment without degradation, risk to
health or safety, or other undesirable and unintended consequences,” among other policies, 42
3
U.S.C. § 4331(b). The Council on Environmental Quality (“CEQ”) promulgates regulations that
guide federal agencies’ compliance with NEPA. See 40 C.F.R. §§ 1500.1–1508.28.
At its core, NEPA simply requires that federal agencies consider the environmental
consequences of their actions. See 42 U.S.C. §§ 4321–4370h; 40 C.F.R. § 1501.1. Under
NEPA, agency decisionmakers must identify and understand the environmental effects of
proposed actions, and they must inform the public of those effects so that it may “play a role in
both the decisionmaking process and the implementation of [the agency’s] decision.” Robertson
v. Methow Valley Citizens Council, 490 U.S. 332, 349 (1989); see also 42 U.S.C. § 4321; 40
C.F.R. § 1501.1. In other words, “NEPA was designed ‘to insure a fully informed and well-
considered decision.’” Park Cty. Res. Council, Inc. v. U.S. Dep’t of Agric., 817 F.2d 609, 621
(10th Cir. 1987) (quoting Vt. Yankee Nuclear Power Corp. v. Nat. Res. Def. Council, Inc., 435
U.S. 519, 558 (1978)), overruled in part on other grounds by Village of Los Ranchos De
Albuquerque v. Marsh, 956 F.2d 970 (10th Cir. 1992) . Importantly, “NEPA documents must
concentrate on the issues that are truly significant to the action in question, rather than amassing
needless detail.” 40 C.F.R. § 1500.1(b). NEPA is not intended to “generate . . . excellent
paperwork,” but rather to “foster excellent action” through informed decisionmaking. Id. §
1500.1(c).
NEPA dictates that an agency must prepare an environmental impact statement (“EIS”)
for every “major [f]ederal action[] significantly affecting the quality of the human environment.”
42 U.S.C. § 4332(C); 40 C.F.R. § 1502.3. The “detailed” EIS must consider “the environmental
impact of the proposed action” and “any adverse environmental effects which cannot be
avoided.” 42 U.S.C. § 4332(C)(i)–(ii). It must also examine “alternatives to the proposed
4
action,” and the action’s direct, indirect and cumulative effects. 2 42 U.S.C. § 4332(2)(C)(iii); 40
C.F.R. §§ 1502.16, 1508.7, 1508.8. 3
Not every federal action, however, requires the preparation of an EIS, because not every
federal action significantly affects the quality of the human environment. To determine whether
an EIS is necessary for a particular action, the agency may prepare an Environmental
Assessment (“EA”). See 40 C.F.R. §§ 1501.4, 1508.9. An EA is “a ‘concise public document’
that ‘[b]riefly provide[s] sufficient evidence and analysis for determining whether to prepare an
[EIS].’” Dep’t of Transp. v. Pub. Citizen, 541 U.S. 752, 757 (2004) (quoting 40 C.F.R. §
1508.9(a)). As in an EIS, the EA must take a “hard look” at the environmental consequences of
the proposed action, Kleppe v. Sierra Club, 427 U.S. 390, 410 n.21 (1976), including its direct,
indirect, and cumulative effects, see EarthReports, Inc. v. FERC, 828 F.3d 949, 953 (D.C. Cir
2016); 40 C.F.R. §§ 1508.9, 1508.25(c). If, after preparing the EA, the agency determines that
an EIS is not necessary, the agency must issue a finding of no significant impact (“FONSI”)
summarizing its decision. See 40 C.F.R. §§ 1501.3, 1501.4, 1508.13; see also AR28440.
For multi-stage agency programs, such as the oil and gas development program at issue
here, NEPA provides that the environmental analysis conducted at each stage may incorporate by
reference previous, related analyses. In NEPA parlance, this is called “tiering.” NEPA more
precisely defines tiering as the:
2
“Effects” and “impacts” are synonymous in this opinion, as they are in NEPA’s
implementing regulations. 40 C.F.R. § 1508.8.
3
“Direct” environmental effects “are caused by the [agency’s] action and occur at the
same time and place.” 40 C.F.R. § 1508.8. “Indirect” environmental effects “are caused by the
action and are later in time or farther removed in distance, but are still reasonably foreseeable.”
Id. “Cumulative” environmental effects account for “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.” Id. § 1508.7.
5
coverage of general matters in broader environmental impact statements (such as
national program or policy statements) with subsequent narrower statements or
environmental analyses (such as regional or basinwide program statements or
ultimately site-specific statements) incorporating by reference the general
discussions and concentrating solely on the issues specific to the statement
subsequently prepared.
40 C.F.R. §§ 1502.20, 1508.28. CEQ regulations state that “[t]iering is appropriate when the
sequence of statements or analyses is . . . [f]rom a program, plan, or policy environmental impact
statement to a . . . site-specific statement or analysis.” Id. § 1508.28(a).
In other words, “[a]n [EA] prepared in support of an individual proposed action can be
tiered to a programmatic or other broader-scope [EIS] . . . for a proposed action with significant
effects . . . if the . . . broader [EIS] . . . fully analyzed those significant effects.” 43 C.F.R. §
46.140(c). However, “[t]o the extent that any relevant analysis in the broader NEPA document is
not sufficiently comprehensive or adequate to support further decisions, the tiered NEPA
document must explain this and provide any necessary analysis.” Id. § 46.140(b). Put simply,
an EA for a specific BLM action may incorporate program-wide EISs, but must supplement
those EISs with more specific environmental analyses of the action at issue. See id. § 46.120(d).
B. Oil and Gas Development Framework
Oil and gas development on federal land is typically conducted through a three-stage
process governed by the FLPMA, NEPA, and the BLM’s Land Use Planning Handbook. These
stages are: (1) land use planning; (2) leasing; and (3) drilling.
1. Land Use Planning Stage
The land use planning stage begins when a BLM field office develops a resource
management plan for its assigned geographic area (the “planning area”). 43 U.S.C. § 1712(a);
43 C.F.R. §§ 1601.0-5(n), 1610.1. The resource management plan determines which portions of
the planning area will be open to oil and gas leasing, and under what conditions. 43 U.S.C. §
6
1712(a). The plan typically incorporates a reasonably foreseeable development scenario
(“RFDS”), which projects the scope and pace of oil and gas development within the planning
area. See AR55736–46. And by regulation, a resource management plan must be accompanied
by an EIS. See 43 C.F.R. § 1601.0-6. 4
2. Leasing Stage
If a resource management plan authorizes oil and gas development on certain land
parcels, BLM must sell leases for those parcels on a quarterly basis. 30 U.S.C. § 226(b)(1)(A);
43 C.F.R. § 3120.1-2. An oil and gas lease confers “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.” 43 C.F.R. § 3120.1-2. However, BLM may impose terms and
conditions on the leases, including conditions designed to protect the environment. Id. § 3101.1-
3. 5 At the leasing stage an EIS may be required, but is not mandated by regulation.
3. Drilling Stage
Once a lease is sold, the lessee must apply for a permit to drill (“APD”) for oil and gas on
the leased parcel, subject to BLM approval. 43 C.F.R. § 3162.3-1(c). BLM may condition APD
approval on the lessee’s adoption of “reasonable measures,” delimited by the lease and the
lessee’s surface use rights, to mitigate the drilling’s environmental impacts. Id. § 3101.1-2. And
before approving an APD, BLM must confirm that the APD complies with the governing
resource management plan, see id. § 1610.5-3, and it must undertake additional NEPA analysis,
id. § 3162.5-1.
4
The public may comment on both the resource management plan and its accompanying
EIS. 43 C.F.R. § 1610.2.
5
The public may comment on a proposed lease sale before it begins. 43 C.F.R. § 3120.3.
7
C. Relevant Factual and Procedural Background
Plaintiffs claim that BLM failed to comply with NEPA at stage two of the oil and gas
development framework, the leasing stage. They have challenged BLM’s approval and issuance
of 473 oil and gas leases, issued through eleven different lease sales, covering over 460,000 acres
of land in Wyoming, Utah, and Colorado. See Am. Compl. ¶ 1, ECF No. 22; Pls. Mem. Supp.
Mot. Summ. J. (“Pls. Mem.”) at 1, ECF No. 55. BLM determined that these lease sales did not
require the issuance of EISs, so BLM instead issued EAs and FONSIs. See Pls. Mem. at 7–8.
Plaintiffs claim that these EAs and FONSIs failed to sufficiently account for the greenhouse gas
(“GHG”) emissions that would be generated by oil and gas development on the leased parcels.
See generally Am. Comp. Plaintiffs seek to set aside the leases pending further environmental
analyses. Id.
Early in the action, the Court allowed five entities to intervene as Defendants: Western
Alliance, American Petroleum, the State of Wyoming, the State of Utah, and the State of
Colorado (the “States”). Mem. & Order Granting Mot. Intervene (Feb. 14, 2017), ECF No. 46;
Mem. & Order Granting Mot. Intervene (Nov. 23, 2016), ECF No. 19. In November 2016, the
Court entered a scheduling order trifurcating the briefing. Scheduling Order (Nov. 28, 2016),
ECF No. 24. The parties agreed to first brief the merits of Plaintiffs’ claims concerning the
Wyoming leasing decisions, with briefing on the Utah and Colorado leasing decisions to follow.
Id. Accordingly, the current round of briefing concerns five BLM oil and gas lease sales held in
Wyoming between May 2015 and August 2016 (the “Wyoming Lease Sales”).
BLM issued 282 leases through the Wyoming Lease Sales, encompassing approximately
303,000 acres of federal land across multiple BLM planning areas. Pls. Mem. at 1. The leased
parcels are managed by ten different BLM field offices—which are responsible for drafting and
8
implementing the resource management plans and EISs governing the parcels—overseen by
three district offices. 6 See Fed. Defs.’ Cross-Mot. Summ. J. & Opp’n Pls. Mem. (“BLM Mem.”)
at 7, ECF No. 63. Those three district offices conducted the lease sales at issue here in May,
August, and November 2015, and May and August 2016. 7 Id. at 7–8. 8 For each lease sale, each
district office involved prepared (1) an EA tiered to the relevant resources management plans and
EISs issued by field offices at the land use planning stage; and (2) a FONSI disavowing the need
for a new, leasing stage EIS. In total, therefore, the record contains nine EA 9/FONSI 10
combinations, tiered to nineteen resource management plan/EIS combinations, including
resource management plan amendments. Id. WildEarth participated in the comment and protest
periods for each of the challenged lease sales. 11
The challenged EAs referenced environmental analyses conducted at the land use
planning stage and, in accordance with NEPA’s tiering requirements, conducted their own
analyses of the specific parcels to be leased. The Court will briefly summarize the relevant
portions of the EAs and then discuss them in greater detail below.
6
The relevant district offices are High Desert, High Plains, and Wind River-Bighorn
Basin (“Wind River”), and the relevant field offices are Rock Springs, Rawlins, Pinedale,
Kemmerer, Buffalo, Casper, Newcastle, Cody, Worland, and Lander. See Fed. Defs.’ Cross-
Mot. Summ. J. & Opp’n Pls. Mem. (“BLM Mem.”) at 7–8, ECF No. 63.
7
Plaintiffs helpfully submitted a chart identifying which district offices conducted each
lease sale. See Pls. Mem. at 8.
8
The May 2016 sale involved leases that were originally designated for sale in February
2016, but were not sold then due to inclement weather that forced the sale’s postponement.
AR34764.
9
AR3373; AR13707; AR13943; AR19449; AR28168; AR28435; AR35276; AR54973;
AR55232.
10
AR3470; AR13925; AR14237; AR19561; AR28233; AR28509; AR35376; AR55027;
AR55272.
11
Comments: AR1969; AR8905; AR16829; AR23682; AR32220. Protests: AR 2997;
AR12984; AR18816; AR27646; AR34764; AR54453.
9
The EAs discuss climate change on a conceptual level. They summarize Wyoming’s
current climate, explain the mechanics of climate change, acknowledge that oil and gas drilling
contributes to climate change, and predict the impact of climate change on the state’s climate.
See AR3411–3415; AR13961–63; AR19502–06; AR28195. Certain EAs also reference various
climate change reports. For instance, several EAs incorporate reports issued by the
Intergovernmental Panel on Climate Change (“IPCC”) discussing the impact of GHG emissions
on climate change. See AR3412; AR13962; AR19504; AR34663.
The EAs also include more specific GHG emissions assessments, which are slightly
different across the challenged EAs but are similarly detailed. The EAs acknowledge that oil and
gas drilling on leased parcels will emit GHGs, and they describe the sources of those emissions,
but they do not attempt to quantify and project the GHG emissions likely to result from a given
lease sale. For instance, certain EAs acknowledge that each potential oil or gas well on the
leased parcels could emit approximately 0.00059 metric tons of carbon dioxide, 12 but they state
that “[t]he [total] amount of increased emissions cannot be quantified at this time since it is
unknown how many wells might be drilled, the types of equipment needed if a well were to be
completed successfully . . . or what technologies may be employed by a given company for
drilling any new wells.” AR13989; see also AR13754; AR28220; AR55015–16. Likewise,
certain EAs incorporate a report quantifying and projecting consumption-based GHG emissions
in Wyoming through 2020—the “Wyoming GHG Inventory”—but the EAs do not attempt to
apply those projections to particular lease sales. See AR3412; AR19503.
12
Carbon dioxide is a GHG, along with methane, nitrous oxides, and hydrofluorocarbons.
See Chamber of Commerce of U.S. v. EPA, 642 F.3d 192, 197 n.1 (D.C. Cir. 2011).
10
Although the EAs acknowledge that GHG emissions may contribute to climate change,
they conclude that “[t]he inconsistency in results of scientific models used to predict climate
change at the global scale coupled with the lack of scientific models designed to predict climate
change on regional or local scales, limits the ability to quantify potential future impacts of
decisions made at this level.” AR3435; see also AR28219. Ultimately, the EAs conclude that
“[w]hen compared to total national or global emissions, the amount [of GHG emissions] released
as a result of potential production from the proposed lease tracts would not have a measurable
effect,” AR13989, or would represent only an “incremental contribution to the total regional and
global GHG emission levels.” AR55023.
Finally, the EAs emphasize that the leasing stage is a preliminary step towards oil and gas
drilling, but that specific drilling projects are not guaranteed to move forward simply because a
given lease was sold. For instance, the EAs state that “[t]he offering and subsequent issuance of
oil and gas leases is strictly an administrative action, which, in and of itself, does not cause or
directly result in any surface disturbance.” AR3382; see also, e.g., AR13718; AR19458;
AR54983. The EAs also state that “BLM cannot determine at the leasing stage whether or not a
nominated parcel will actually be leased, or if it is leased, whether or not the lease would be
explored or developed.” AR3382; see also AR13718; AR19458–59. They note that
BLM cannot determine exactly where a well or wells may be drilled or what
technology that [sic] may be used to drill, complete and produce wells, so the
impacts listed [in the EA] are more generic, rather than site-specific. Additional
NEPA and technical engineering analysis would be conducted prior to approval of
an APD to ensure that the proposal is compliant with all Federal and/or state rules
and regulations.
AR3426; see also AR13744; AR19518; AR55008. Accordingly, the EAs conclude that the
“filing of an [APD] may be the first useful point at which a site-specific environmental appraisal
[of a lease parcel] can be undertaken.” AR3382; see also AR13718; AR19458; AR28179.
11
* * *
In summary, according to Plaintiffs, NEPA required BLM to conduct a more piercing
consideration of the consequences of oil and gas drilling before it authorized the Wyoming Lease
Sales. More specifically, Plaintiffs argue that the EAs and FONSIs issued in conjunction with
the Wyoming Lease Sales violated NEPA because BLM failed to take a “hard look” at GHG
emissions and the climate change impact of those emissions. See generally Am. Compl; Pls.
Mem. at 2. Plaintiffs ask the Court to (1) declare that the leasing authorizations violated NEPA;
(2) vacate the leases; and (3) enjoin BLM from approving APDs for those leases until new
NEPA analyses have been conducted. Am. Compl. at 39–40. Defendants, on the other hand,
argue that Plaintiffs lack standing to challenge one of the lease sales, and that BLM’s
environmental analyses were sufficient. See generally Pls. Mem.; BLM Mem.; Mem. American
Petroleum Opp’n Pls. Mem. Supp. Cross-Mot. Summ. J. (“API Mem.”), ECF No. 60-1; Western
Alliance Statement P. & A. Supp. Cross-Mot. Summ. J. Opp’n Pls. Mem. (“Western Alliance
Mem.”), ECF No. 61-1; Mem. Supp. Wyo. Colo. & Utah’s Cross-Mot. Summ. J. Resp. Pls.
Mem. (“States Mem.”), ECF No. 62.
Now before the Court are the parties’ ripe cross-motions for summary judgment. See Pls.
Mem.; BLM Mem.; API Mem.; Western Alliance Mem.; States Mem. As explained below, the
Court concludes that Plaintiffs have standing to bring this action, and that BLM did not properly
discharge its NEPA obligations. Accordingly, the Court grants Plaintiffs’ motion for summary
judgment in part and denies Defendants’ motions for summary judgment. The Court also denies
12
the Institute’s motion to file an amicus brief, because the Institute’s arguments largely mirror
Plaintiffs’ arguments. 13
III. LEGAL STANDARD
In a typical case, a court may grant summary judgment to a movant who “shows that
there is no genuine dispute as to any material fact and the movant is entitled to judgment as a
matter of law.” Fed. R. Civ. P. 56(a). But when assessing administrative action, at the summary
judgment stage “the district judge sits as an appellate tribunal,” Am. Bioscience, Inc. v.
Thompson, 269 F.3d 1077, 1083 (D.C. Cir. 2001), limited to determining whether, as a matter of
law, the evidence in the administrative record supports the agency’s decision, Citizens for
Responsibility & Ethics in Wash. (“CREW”) v. SEC, 916 F. Supp. 2d 141, 145 (D.D.C. 2013).
In such a case, the complaint “actually presents no factual allegations, but rather only arguments
about the legal conclusion to be drawn about the agency action.” Rempfer v. Sharfstein, 583
F.3d 860, 865 (D.C. Cir. 2009) (quoting Marshall Cty. Health Care Auth. v. Shalala, 988 F.2d
1221, 1226 (D.C. Cir. 1993)). Accordingly, the Court’s review “is based on the agency record
and limited to determining whether the agency acted arbitrarily or capriciously.” 14 Id. (citing 5
U.S.C. § 706).
An agency action is arbitrary and capricious if:
13
Plaintiffs have requested oral argument on the pending summary judgment motions.
See Pls. Mot. Summ. J. at 2, ECF No. 55. Because the Court finds the parties’ written
submissions to be thorough and sufficient to resolve those motions, Plaintiffs’ request is denied.
See LCvR 7(f) (stating that the decision to allow oral argument is “within the discretion of the
Court.”).
14
The Court thus declines to consider Plaintiffs’ extra-record exhibits. See Commercial
Drapery Contractors, Inc. v. United States, 133 F.3d 1, 7 (D.C. Cir. 1998) (holding that APA
review is limited to the “administrative record . . . except when there has been a strong showing
of bad faith or improper behavior or when the record is so bare that it prevents effective judicial
review”). As explained below, however, the Court will consider Plaintiffs’ declarations in
support of their standing argument.
13
the agency has relied on factors which Congress has not intended it to consider,
entirely failed to consider an important aspect of the problem, offered an
explanation for its decision that runs counter to the evidence before the agency, or
is so implausible that it could not be ascribed to a difference in view or the product
of agency expertise.
Del. Riverkeeper Network v. FERC, 753 F.3d 1304, 1313 (D.C. Cir. 2014) (quoting Motor
Vehicle Mfrs. Ass’n of the U.S., Inc. v. State Farm Mut. Auto. Ins., 463 U.S. 29, 43 (1983)). This
standard applies when assessing an agency’s compliance with NEPA. WildEarth Guardians v.
Jewell, 738 F.3d 298, 319 (D.C. Cir. 2013) (citing Theodore Roosevelt Conservation P’ship v.
Salazar, 616 F.3d 497, 507 (D.C. Cir. 2010); Nevada v. Dep’t of Energy, 457 F.3d 78, 87 (D.C.
Cir. 2006)).
Applying this standard, the Court has a “limited” role in reviewing an agency’s decision
not to issue an EIS: it must merely confirm “that no arguably significant consequences have been
ignored.” Pub. Citizen v. Nat’l Highway Traffic Safety Admin., 848 F.2d 256, 267 (D.C. Cir.
1988). The Court’s task “is not to ‘flyspeck’ [BLM’s] environmental analysis for ‘any
deficiency no matter how minor.’” Sierra Club v. FERC (“Sierra Club (Freeport)”), 827 F.3d
36, 46 (D.C. Cir. 2016) (quoting Theodore Roosevelt, 661 F.3d at 75). Rather, NEPA’s “rule of
reason” dictates that an agency’s assessment is sufficient unless its “deficiencies are significant
enough to undermine informed public comment and informed decisionmaking.” Sierra Club v.
FERC (“Sierra Club II”), 867 F.3d 1357, 1368 (D.C. Cir. 2017) (citing Pub. Citizen, 541 U.S. at
767; Nevada, 457 F.3d at 93).
IV. INSTITUTE FOR POLICY INTEGRITY’S AMICUS BRIEF
Courts have wide discretion in deciding whether to grant a third party leave to file an
amicus brief. In the Matter of the Search of Info. Associated with [redacted]@mac.com that is
Stored at Premises Controlled by Apple, Inc., 13 F. Supp. 3d 157, 167 (D.D.C. 2014)
(citing Nat’l Ass’n of Home Builders v. U.S. Army Corps of Eng’rs, 519 F. Supp. 2d 89, 93
14
(D.D.C. 2007)). An amicus brief is appropriate where “the brief will assist the judges by
presenting ideas, arguments, theories, insights, facts, or data that are not to be found in the
parties’ briefs.” Voices for Choices v. Ill. Bell Tel. Co., 339 F.3d 542, 545 (7th Cir. 2003); see
also Jin v. Ministry of State Sec’y, 557 F. Supp. 2d 131, 137 (D.D.C. 2008) (holding that an
amicus brief is appropriate where “the amicus has unique information or perspective that can
help the court beyond the help that the lawyers for the parties are able to provide” (quoting Ryan
v. CFTC, 125 F.3d 1062, 1064 (7th Cir. 1997))).
Here, while the Institute clearly has expertise regarding the use of economic analysis in
conducting environmental assessments, the Court does not believe that its amicus brief presents
arguments that are not already found in the parties’ briefs. The Institute seeks to present three
arguments: (1) BLM incorrectly calculated the per-well emissions estimates cited in the EAs; (2)
BLM improperly failed to monetize the impact of climate change resulting from GHG emissions;
and (3) BLM improperly failed to “follow basic economic logic” and account for the increased
demand for oil and gas that would result from production on the leased parcels. Br. Institute
Supp. Pls. Mem. at 3, ECF No. 71-1. Plaintiffs raised the first two arguments in their briefing,
albeit in slightly less detail, and the Court will address those arguments below. The third
argument is a slight variation of Plaintiffs’ argument that BLM failed to account for the GHG
emissions generated by downstream consumption of oil and gas. The Court will also address this
argument below.
Moreover, it does not appear that the Institute participated in the public comment periods
for any of the challenged EAs. The Court finds it unhelpful to consider its third argument now,
past the point when BLM could have considered the argument in its decisionmaking process, and
after the parties negotiated a briefing schedule without the Institute’s participation. Because the
15
Institute’s amicus brief does not have “unique information or perspective that can help the
[C]ourt,” the Court denies the Institute’s motion to file that brief. Jin, 557 F. Supp. 2d at 137.
V. ANALYSIS
Plaintiffs challenge nine separate EAs, arguing that “[e]ach of these EAs share common
deficiencies, and none took a hard look at the impacts of GHG pollution and climate change
impacts, as required by NEPA.” Pls. Mem. at 1. Defendants contend that the EAs’ GHG
emissions assessments were sufficient, given that they were conducted at the leasing stage when
development of the parcels was uncertain. Defendants also contend that Plaintiffs lack standing
to challenge the August 2016 lease sale. The Court will discuss Plaintiffs’ standing, then the
merits of the parties’ cross-motions for summary judgment. It concludes that Plaintiffs have
standing to challenge all five lease sales, and that BLM’s leasing stage environmental
assessments were inadequate under NEPA. The Court therefore grants Plaintiffs’ motion for
summary judgment in part and denies Defendants’ motions.
A. Standing
The Court begins, as it must, by confirming that Plaintiffs have standing to bring this
action. Al–Zahrani v. Rodriguez, 669 F.3d 315, 318 (D.C. Cir. 2012). The doctrine of standing
derives from Article III of the U.S. Constitution, which confines the federal courts to
adjudicating actual “Cases” and “Controversies,” U.S. Const. art. III, § 2, cl. 1, and from “the
separation-of-powers principles underlying that limitation.” Lexmark Int’l, Inc. v. Static Control
Components, Inc., 134 S. Ct. 1377, 1386 (2014). Thus, a showing of standing “is an essential
and unchanging” predicate to any exercise of this Court’s jurisdiction. Lujan v. Defs. of
Wildlife, 504 U.S. 555, 560 (1992).
16
Ordinarily, a party has established standing if it shows that, at the time the complaint was
filed: (1) “the party has suffered an ‘injury in fact,’” (2) “the injury is ‘fairly traceable’ to the
challenged action of the defendant,” and (3) “it is ‘likely, as opposed to merely speculative, that
the injury will be redressed by a favorable decision.’” Grocery Mfrs. Ass’n v. EPA, 693 F.3d
169, 174 (D.C. Cir. 2012) (quoting Lujan, 504 U.S. at 560–61). The standing inquiry is
modified, however, in cases where a plaintiff alleges a violation of his or her procedural rights,
as when a plaintiff sues over an agency’s failure to conduct an EIS under NEPA. In such cases,
the plaintiff must “show that the interest asserted is more than a mere ‘general interest [in the
alleged procedural violation] common to all members of the public,’ the plaintiff must show that
the government act performed without the procedure in question will cause a distinct risk to a
particularized interest of the plaintiff.” Fla. Audubon Soc’y v. Bentsen, 94 F.3d 658, 664 (D.C.
Cir. 1996) (alteration in original) (quoting Ex parte Levitt, 302 U.S. 633, 634 (1937)). Although
such plaintiffs need not show that, but-for the procedural defect, the agency would have reached
a different decision, they must establish “a causal relationship between the final agency action
and the alleged injuries.” Ctr. for Law & Educ. v. U.S. Dep’t of Educ., 396 F.3d 1152, 1160
(D.C. Cir. 2005). This causation prong of the standing inquiry looks to the “causal nexus
between the agency action and the asserted injury, while redressability centers on the causal
connection between the asserted injury and judicial relief.” Id. at 1160 n.2 (quoting Freedom
Republicans v. FEC, 13 F.3d 412, 418 (D.C. Cir. 1994)).
Plaintiffs, as the parties invoking this Court’s jurisdiction, bear the burden of establishing
all three elements of standing. WildEarth Guardians v. Jewell, 738 F.3d at 305. At the summary
judgment stage, Plaintiffs must show that, taking their facts as true and drawing all reasonable
inferences in their favor, a reasonable juror could find that they have standing. See Dominguez v.
17
UAL Corp., 666 F.3d 1359, 1362 (D.C. Cir. 2012). To meet this burden, Plaintiffs must put forth
specific facts—not mere allegations—that show a “substantial probability” that Plaintiffs were
injured, that Defendants caused the injury, and that a favorable decision of this Court could
redress that injury. Sierra Club v. EPA, 292 F.3d 895, 898–99 (D.C. Cir. 2002).
Where a plaintiff is an organization suing on behalf of its members—as is the case here—
the organization has “representative” or “associational” standing if: “(1) at least one of its
members would have standing to sue in his own right; (2) the interests the association seeks to
protect are germane to its purpose, and (3) neither the claim asserted nor the relief requested
requires that an individual member of the association participate in the lawsuit.” Id. at 898. 15
Ultimately, the Court need only find that one plaintiff has standing to allow a case to proceed to
the merits. See Comcast Corp. v. FCC, 579 F.3d 1, 6 (D.C. Cir. 2009) (“[I]f one party has
standing in an action, a court need not reach the issue of the standing of other parties when it
makes no difference to the merits of the case.”).
Moreover, although judicial review of agency action is typically confined to the
administrative record, where there is insufficient evidence of standing in the record because the
question was not before the agency, plaintiffs may submit extra-record evidence to establish
standing. Sierra Club, 292 F.3d at 899. Here, WildEarth has submitted the declarations of Erik
Molvar and Jeremy Nichols to support its standing. See Decl. Erik Molvar (“Molvar Decl.”),
Pls. Mem. Ex 6, ECF No. 55-6; Decl. Jeremy Nichols (“Nichols Decl.”), Pls. Mem. Ex 7, ECF
No. 55-7. Defendants contend that the declarations do not establish that the August 2016 lease
15
The Court has no reason to doubt that the interests Plaintiffs seek to protect in this
action are germane to their purposes, and the relief requested does not require that one of
Plaintiffs’ individual members participate in the action. The Court will therefore focus on
whether one of Plaintiffs’ members would have standing to sue.
18
sale caused Plaintiffs injury in fact. BLM Mem. at 13; API Mem. at 22. 16 Having reviewed the
declarations, the Court disagrees.
“[E]nvironmental plaintiffs adequately allege injury in fact when they aver that they use
the affected area and are persons ‘for whom the aesthetic and recreational values of the area will
be lessened’ by the challenged activity.” Friends of the Earth, Inc. v. Laidlaw Envtl. Servs.
(TOC), Inc., 528 U.S. 167, 183 (2000) (quoting Sierra Club v. Morton, 405 U.S. 727, 735
(1972)). The plaintiffs must show “concrete and particularized injury which has occurred or is
imminent due to geographic proximity to the action challenged.” City of Olmsted Falls v. FAA,
292 F.3d 261, 267 (D.C. Cir. 2002). While Plaintiffs’ declarations are slightly ambiguous, they
do state that the declarants have visited areas impacted by the August 2016 lease sale, and that
they plan to return to those areas. The August 2016 sale covered land parcels in BLM’s High
Plains and Wind River-Bighorn Basin (“Wind River”) districts. Decl. of Merry E. Gamper
(“Gamper Decl.”) ¶ 6, ECF No. 68-1. Mr. Molvar states that he annually visits the Red Desert,
Bighorn Basin, and Wind River Basin of Wyoming—each of which contain land falling within
one or both of the High Plains and Wind River districts—and he provides concrete plans to
return to those areas within the year. Molvar Decl. ¶ 8; Gamper Decl. ¶¶ 3, 7. Mr. Nichols’s
declaration is more precise. He states that he “regularly visit[s] lands,” including land “between
Rawlins and Rock Spring north and south of Interstate 80,” that he “often visit[s] and hike[s] in
lands that are within the Great Divide Basin,” that he visits these lands “at least once a year and
ha[s] since 2001,” and that he intended to visit them again in August 2017. Nichols Decl. ¶ 14.
16
Defendants concede that the declarations support standing to challenge the first four
Wyoming Lease Sales. See BLM Mem. at 13–14; API Mem. at 22. The Court agrees, for the
same reasons that it concludes Plaintiffs have standing to challenge the August 2016 sale.
19
BLM’s declarant, Merry E. Gamper, admits that two parcels within the Great Divide Basin were
offered at the August 2016 sale. See Gamper Decl. ¶ 3.
In arguing that Plaintiffs’ declarations fail to demonstrate injury in fact for the August
2016 sale, Defendants have failed to fully parse those declarations. Focusing on the declarants’
statements that they regularly visit the Red Desert, Defendants contend that the declarations lack
sufficient “geographic specificity” with respect to the August 2016 sale, because the areas
referenced are “vast.” BLM Mem. 14; API Mem. 22. Defendants thus analogize this case to
Summers v. Earth Island Institute, which involved a challenge to United States Forest Service
regulations that would impact development projects in national forests. 555 U.S. 488, 493–94
(2009). In asserting injury in fact, the plaintiff organizations’ declarant stated that he “visited
many national forests and plan[ned] to visit several unnamed forests in the future.” Id. at 495.
The Supreme Court held that this declaration was insufficient to establish the plaintiffs’ injury in
fact. Id. “[N]ational forests occupy more than 190 million aces, an area larger than Texas”; it
was highly unlikely that the declarant’s “wanderings w[ould] bring him to a parcel about to be
affected” by a project subject to the challenged regulations. Id. at 495–96. The declarant–and
the plaintiffs—thus could not demonstrate a sufficient likelihood of concrete harm from the
challenged regulations to convey standing. Id. at 496.
The ambiguous declaration at issue at Summers was far less specific than the declarations
at issue here. Here, rather than generally asserting that they visit BLM lands, or even that they
visit BLM lands within Wyoming, WildEarth’s declarants state that they have visited and will
visit specific areas within Wyoming that will be impacted by the lease sales. See Molvar Decl. ¶
8, 14, 15 (listing specific lease parcels, and identifying the Red Desert, Adobe Town, Bighorn
Basin, and Wind River Basin areas); Nichols Decl. ¶¶ 14, 22 (identifying specific areas within
20
the Red Desert, including the Great Divide Basin and areas north of interstate 80). While it is
true that Mr. Molvar and Mr. Nichols do not state that they have visited or plan to visit specific
parcels offered in the August 2016 lease sale, API Mem. at 22, the Court concludes that such
specificity is not necessary here, where the parcels at issue cover thousands of acres of open,
undeveloped landscape, and where oil and gas development prompts “drilling rigs that rise above
the land” and create “haze and dust in the air” that can be seen “up to a hundred miles” away.
Nichols Decl. ¶¶ 16–18; see also id. at 8–14 (attaching photographs demonstrating the
juxtaposition of oil and gas drilling rigs against the open landscape). Mr. Nichols’s declaration
indicates that development of “particular” parcels offered in the August 2016 lease sale would
“impede a specific and concrete plan of [his] to enjoy the [Great Divide Basin].” Summers, 555
U.S. at 495. This is sufficient to establish Mr. Nichols’s injury in fact. Sierra Club v. EPA, 292
F.3d at 898; WildEarth Guardians v. Jewell, 738 F.3d at 307 (holding that while the plaintiffs
challenging a BLM leasing decision could not “establish standing based on the effects of global
climate change,” they “established a separate injury in fact not caused by climate change—the
harm to their members’ recreational and aesthetic interests from local pollution”); WildEarth
Guardians v. Salazar, 880 F. Supp. 2d 77, 86–87 (D.D.C. 2012) (holding that the plaintiffs had
standing where they alleged that “BLM’s failure to take full stock of the environmental impacts
of NO2 emissions during mining operations will lead to haze, smog, and dust clouds in the areas
immediately adjacent to the [mining] tracts”). 17
17
Because the Court holds that Mr. Nichols’s declaration was sufficient to demonstrate
Plaintiffs’ standing, the Court will not address Mr. Molvar’s supplemental declaration offering
“further clarification and details of his visits to the August 2016 leases.” Pls. Reply Supp. Pls.
Mem. (“Pls. Reply”) at 1, ECF No. 76; Suppl. Decl. Erik Molvar, Pls. Reply Ex. 9, ECF No. 76-
1.
21
The aesthetic injuries suffered by Mr. Nichols and Mr. Molvar also satisfy the two
remaining elements of standing: the injuries are “fairly traceable” to BLM’s allegedly deficient
NEPA reviews and they would “be redressed by a favorable decision.” Grocery Mfrs. Ass’n, 693
F.3d at 174. In NEPA procedural-injury cases, an “adequate causal chain” contains two links:
“one connecting the omitted EIS to some substantive government decision that may have been
wrongly decided because of the lack of an [adequate] EIS,” and “one connecting that substantive
decision to the plaintiff’s particularized injury.” Fla. Audubon Soc’y, 94 F.3d at 668. Here,
BLM’s alleged failure to discharge its NEPA obligation led directly to authorization of the
Wyoming Lease Sales, which will enable the oil and gas development causing Plaintiffs’
injuries. “The proof is in the pudding: if [the Court] were to vacate [BLM’s] order authorizing
the [Wyoming Lease Sales] for violating NEPA, not only would [the injuries of Mr. Nichols and
Mr. Molvar] be redressed, the remedy would also be limited to the inadequacy—here, [deficient
EAs]—that produced the injury in fact that [Plaintiffs] ha[ve] established.” Sierra Club
(Freeport), 827 F.3d at 44. Accordingly, because at least one of WildEarth’s members would
have standing to bring this action, Plaintiffs have standing to challenge all five Wyoming Lease
Sales. Sierra Club v. EPA, 292 F.3d at 898.
B. Merits
Because Plaintiffs have standing, the Court will assess the merits of Plaintiffs’ arguments
with respect to each sale. The gravamen of Plaintiffs’ motion for summary judgment is that (1)
BLM failed to take a “hard look” at GHG emissions from potential oil and gas drilling on the
leased parcels; and (2) its FONSIs were deficient. As explained below, the Court concludes that
BLM did not take a hard look at drilling-related and downstream GHG emissions from the leased
parcels, and it failed to sufficiently compare those emissions to regional and national emissions.
22
These shortcomings also rendered the challenged FONSIs deficient, because the FONSIs could
not convincingly state that BLM’s leasing decisions would not significantly affect the quality of
the environment.
1. BLM Failed to Take a “Hard Look” at Greenhouse Gas Emissions
Plaintiffs’ first core argument is that BLM “universally failed” to “take a hard look at the
impacts of GHG pollution and climate change resulting from its leasing decisions . . . in EAs for
the [Wyoming Lease Sales].” Pls. Mem. at 11. More specifically, Plaintiffs contend that “BLM
arbitrarily failed to analyze the direct, indirect, and cumulative impacts of GHG emissions of oil
and gas leasing—an omission admitted by the agency that requires no flyspecking of the record.”
Pls. Mem. at 11–12. The Court agrees that BLM’s leasing stage analyses of GHG emissions
were inadequate, but it does not hold that those analyses required the degree of detail demanded
by Plaintiffs.
Again, NEPA requires that an agency consider the direct, indirect, and cumulative
impacts of its proposed projects. 40 C.F.R. § 1508.25(c). Direct impacts are “caused by the
action and occur at the same time and place.” Id. § 1508.8(a). Indirect impacts are “caused by
the action and are later in time or farther removed in distance, but are still reasonably
foreseeable.” Id. § 1508.8(b). A cumulative impact is an “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.” Id. § 1508.7. “Cumulative impacts can result from
individually minor but collectively significant actions taking place over a period of time.” Id.
The Court will consider BLM’s evaluation of each type of impact in turn. First, however,
it must address an issue that pervades the parties’ briefs: whether BLM could defer certain
23
environmental impact analyses to the drilling stage, rather than conducting them at the leasing
stage. See AR3458 (“Emissions of all regulated pollutants (including GHGs) and their impacts
will be quantified and evaluated at the time that a specific development project is proposed.”). In
short, because BLM cannot fully prevent GHG emissions from oil and gas drilling once leases
have been issued, BLM was required to assess the reasonably foreseeable impacts of drilling, at
the leasing stage. BLM’s assessments fell short of NEPA’s requirements.
a. Leasing is an Irrevocable Commitment to Oil and Gas Drilling
In evaluating BLM’s EAs the Court must assure itself that “the agency took a ‘hard look’
at the environmental consequences of its decision[s].” Conner v. Burford, 848 F.2d 1441, 1446
(9th Cir. 1988) (citing Kleppe, 427 U.S. at 410 n.21; California v. Block, 690 F.2d 753, 761 (9th
Cir. 1982)); accord TOMAC, Taxpayers of Mich. Against Casinos v. Norton, 433 F.3d 852, 861
(D.C. Cir. 2006). A hard look requires that BLM assess the “reasonably foreseeable” impacts of
a proposed action before an “irretrievable commitment[] of resources” is made that would trigger
those impacts. 42 U.S.C. § 4332(2)(C)(v); see also Wyo. Outdoor Council v. U.S. Forest
Serv., 165 F.3d 43, 49 (D.C. Cir. 1999) (“[T]he law does not require an agency to prepare an EIS
until it reaches the critical stage of a decision which will result in ‘irreversible and irretrievable
commitments of resources’ to an action that will affect the environment.” (quoting Mobil Oil
Corp. v. FTC, 562 F.2d 70, 173 (2d Cir. 1977))). “[T]he appropriate time for preparing an EIS
is prior to a decision, when the decisionmaker retains a maximum range of options.” Sierra
Club v. Peterson, 717 F.2d 1409, 1414 (D.C. Cir. 1983) (citations omitted). While the parties
seem to agree on this standard, they dispute whether BLM’s decision to proceed with the
Wyoming Lease Sales was the critical stage of the oil and gas leasing program, beyond which
BLM could not defer more detailed environmental analyses.
24
Relying primarily on a thirty-year-old D.C. Circuit opinion, Peterson, and a thirty-year-
old Ninth Circuit opinion, Conner, Plaintiffs argue that BLM could not defer analyzing the
reasonably foreseeable impacts of oil and gas drilling past the Wyoming Lease Sale stage. Pls.
Mem. at 16. This is because, according to Plaintiffs, after the leasing stage BLM could no longer
fully prevent drilling and its environmental consequences. Id. While Peterson and Conner have
been supplemented by decades of NEPA-related law, their core holdings have stood the test of
time. They dictate the Court’s conclusion here.
Both cases involved a challenge to the United States Forest Service’s decision to issue oil
and gas leases over large swaths of National Forest. Peterson, 717 F.2d at 1410; Conner, 848
F.2d at 1443–44. Certain of the leases contained No Surface Occupancy (“NSO”) stipulations—
which forbid a lessee from conducting surface-level activity on a leased parcel without additional
agency approval—while other leases allowed for some surface-disturbing activity without
agency authorization. See Peterson, 717 F.2d at 1411; Conner, 848 F.2d at 1444. At the leasing
stage, the Forest Service drafted an EA and a FONSI that declined to fully assess the reasonably
foreseeable impacts of each leasing decision—including the impacts of surface-disturbing
activities—because “any impacts which might result from the act of leasing would either be
insignificant or, if significant, could be mitigated by exercising the controls provided in the lease
stipulations.” Peterson, 717 F.2d at 1413–14; see also Conner, 848 F.2d at 1443–44. Thus, the
agency’s finding of “no significant impact” was “premised upon the conclusion that the lease
stipulations w[ould] prevent any significant environmental impacts until a site-specific plan for
exploration and development [was] submitted by the lessee.” Peterson, 717 F.2d at 1413.
The D.C. and Ninth Circuits held that this conclusion fell short of NEPA’s requirements
with respect to leases lacking NSO stipulations. The Forest Service could not defer assessing the
25
impacts of surface-disturbing activities on the leased parcels, because at the leasing stage “the
[agency] made an irrevocable commitment to allow some surface-disturbing activities,” and it
was therefore required to analyze those activities before it could no longer preclude them.
Peterson, 717 F.2d at 1414; see also Conner, 848 F.2d at 1449–50. In other words, an agency
“may delay preparation of an EIS provided that it reserves both the authority to preclude all
activities pending submission of site-specific proposals and the authority to prevent proposed
activities if the environmental consequences are unacceptable.” Peterson, 717 F.2d at 1415; see
also N.M. ex rel. Richardson v. BLM, 565 F.3d 683, 718–19 (10th Cir. 2009) (holding that BLM
“was required to analyze any foreseeable impacts of [surface-disturbing activity on an oil and gas
lease] before committing the resources”); Conner, 848 F.2d at 1451.
These cases establish that an agency cannot defer analyzing the reasonably foreseeable
environmental impacts of an activity past the point when that activity can be precluded. This
principle, and the parties’ briefing, raises a threshold question for the Court here: can BLM
preclude oil and gas drilling even after having sold leases authorizing such drilling? The
regulatory framework and Defendants’ supplemental briefing make clear that the answer is no.
Prior to a lease sale, BLM has the authority to impose conditions, such as NSO
stipulations, dictating steps leaseholders must take to protect the environment. 43 C.F.R. §
3101.1-3. After the lease sale, however, the leaseholder has “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.” Id. § 3101.1-2. As Plaintiffs note, Pls. Mem. at 16, and as some
of the EAs at issue make clear, the Wyoming Leases do not contain stipulations preventing oil
and gas drilling without further post-lease approval by BLM. Moreover, BLM’s fluid minerals
planning handbook states that “[b]y law, [direct, indirect and cumulative] impacts must be
26
analyzed before the agency makes an irreversible commitment,” which, for oil and gas drilling,
“occurs at the point of lease issuance.” AR55446 (quoting the BLM Handbook H-1624-1).
Finally, Defendants themselves concede that once the Wyoming Leases were issued, BLM could
no longer prevent the lease-holders from exploring the parcels and drilling for oil and gas,
producing GHG emissions. See States Suppl. Br. at 2–3, ECF No. 93; API Suppl. Br. at 2, ECF
No. 94; BLM Suppl. Br. at 2, 18 ECF No. 95; Western Alliance Suppl. Br. at 1, ECF No. 96.
While it may be true that after the leasing stage BLM can impose conditions to limit and
mitigate GHG emissions and other environmental impacts, see, e.g., States Suppl. Br. at 3–4;
API Suppl. Br. at 2–4, the leasing stage is the point of no return with respect to emissions. Thus,
in issuing the leases BLM “made an irrevocable commitment to allow some” GHG emissions.
Peterson, 717 F.2d at 1414. 19 BLM was therefore required to fully analyze the reasonably
foreseeable impacts of those emissions at the leasing stage. Id.; see also Conner, 848 F.2d at
1449–50. “[T]he next question is whether any environmental impacts were reasonably
foreseeable at the leasing stage.” Richardson, 565 F.3d at 718.
b. BLM Need Not Conduct Site-Specific Assessments at the Leasing Stage
Plaintiffs seem to suggest that because the leasing stage represents an irretrievable
commitment to oil and gas drilling, BLM was required to undertake certain “site-specific”
analyses of individual lease parcels at that stage. See Pls. Mem. at 15. Defendants counter that
18
Because this brief does not include internal page numbers, the Court refers to the page
numbers automatically generated by CM/ECF.
19
Defendants note certain factual distinctions between Peterson, Conner, and this case,
but they are distinctions without a difference. For instance, BLM notes that unlike here, the
leasing decisions in Peterson and Conner “were based entirely on EAs and FONSIs—no EISs
were ever prepared.” BLM Mem. at 20. But as discussed below, BLM’s analyses in EISs
generated at the land use planning stage did not absolve it of the duty to conduct more specific
analyses at the leasing stage, when it made an irretrievable commitment of resources.
27
site-specific analyses at the leasing stage without access to “key [site-specific] variables would
be speculative at best, would not aid in BLM’s decision-making, and would undoubtedly be
fruitless or impossible.” Western Alliance Mem. at 20. Defendants have the stronger argument.
At the leasing stage, BLM could not reasonably foresee the projects to be undertaken on
specific leased parcels, nor could it evaluate the impacts of those projects on a parcel-by-parcel
basis. As the EAs explain, BLM did not know “whether or not [a given] lease would be explored
or developed.” AR3426. And even if BLM assumed that a given lease would be developed, it
could not know the resource to be extracted from the lease—oil or gas—the type of wells to be
drilled, and the technology that would be used to drill those wells. See AR11957; AR35366.
NEPA does not require an agency to issue these types of wholly speculative assessments at the
leasing stage, even assuming an irretrievable commitment of resources. See Park County, 817
F.2d at 623 (holding that “[t]o require a cumulative EIS contemplating full field development” at
the leasing stage would “result in a gross misallocation of resources, ‘would trivialize NEPA and
would diminish its utility in providing useful environmental analysis for major federal actions
that truly affect the environment.’” (quoting Cabinet Mountains Wilderness v. Peterson, 685
F.2d 678, 682 (D.C. Cir. 1982))); 20 Chihuahuan Grasslands All. v. Norton, 507 F. Supp. 2d
1216, 1231 (D.N.M. 2007), vacated and remanded on other grounds, 545 F.3d 884 (10th Cir.
2008) (holding that “site-specific analysis would be impractical, speculative and unduly
expensive” at the leasing stage, especially where “BLM has conceded that further analysis is
20
Park County applied a reasonableness standard to its NEPA review that the Tenth
Circuit overruled in Village of Los Ranchos, in favor of the APA’s arbitrary and capricious
standard. 956 F.2d at 973. However, the Tenth Circuit left Park County’s substantive NEPA
analysis intact, noting that “the difference between the arbitrary and capricious and
reasonableness standards is not of great pragmatic consequence; therefore, changing to the
former will not require a substantial reworking of long-established NEPA law.” Id.
(quoting Marsh v. Oregon Nat. Res. Council, 490 U.S. 360, 377–78, 77 n.23 (1989)).
28
necessary, and will be done, prior to site-specific activities in order to fully comply with its
NEPA obligations”); accord San Juan Citizens All. v. BLM, 326 F. Supp. 3d 1227, 1246 (D.N.M.
2018) (holding that “BLM acted within its discretion to defer consideration of site-specific
mitigation measures [for oil and gas development] until the APD stage”); Oceana v. Bureau of
Ocean Energy Mgmt., 37 F. Supp. 3d 147, 166–67 (D.D.C. 2014) (at the leasing stage, allowing
an agency to defer discussion of “high pressure and high temperature” off-shore oil wells
“because these are postlease operational issues that cannot be reasonably predicted at the lease
stage without site-specific information”). “That [BLM] may continue to assess impacts as more
information becomes available does not indicate that [it] failed to take a ‘hard look’ at the
environmental consequences of its proposed action” here. Wilderness Soc’y v. Salazar, 603 F.
Supp. 2d 52, 62 (D.D.C. 2009).
c. BLM Must Quantify Drilling-Related GHG Emissions in Aggregate 21
While BLM could not, at the leasing stage, reasonably foresee the environmental impacts
of specific drilling projects, it could reasonably foresee and forecast the impacts of oil and gas
drilling across the leased parcels as a whole. “In determining what effects are ‘reasonably
foreseeable,’ an agency must engage in ‘reasonable forecasting and speculation,’ with
reasonable being the operative word.” Sierra Club v. U.S. Dep’t of Energy (“Sierra Club I”),
21
This section refers to GHG emissions resulting from oil and gas drilling on the lease
parcels, as opposed to emissions resulting from the downstream combustion of that oil and gas.
See AR34665 (“Oil and gas development activities can generate [GHGs] (during processing).”).
Defendants take different positions regarding whether drilling-related GHG emissions are the
“direct,” or “indirect” effects of BLM’s leasing decisions. See AR34682 (“The administrative
act of leasing . . . would not result in any direct GHG emissions.”); Western Alliance Mem. at 21
(“BLM reasonably determined that no direct GHG emission or climate change effects would
result from the” leasing decisions); BLM Mem. at 16 (stating, in its discussion of “direct
effects,” that “all nine EAs at issue in this case considered GHG emissions and climate”). But all
parties agree that BLM was required to analyze drilling-related emissions.
29
867 F.3d 189, 198 (D.C. Cir. 2017) (quoting Del. Riverkeeper, 753 F.3d at 1310). “The agency
‘need not foresee the unforeseeable, but by the same token neither can it avoid drafting an impact
statement simply because describing the environmental effects of and alternatives to particular
agency action involves some degree of forecasting.’” Id. (quoting Scientists’ Inst. for Pub. Info.,
Inc. v. Atomic Energy Comm’n, 481 F.2d 1079, 1092 (D.C. Cir. 1973)). Plaintiffs contend that
GHG emissions from oil and gas drilling were reasonably foreseeable at the leasing stage here,
and that BLM could have reasonably quantified and forecasted those emissions. See Pls. Mem.
at 13–16. They argue that BLM’s failure to quantify GHG emissions was thus contrary to
NEPA. See id. The Court agrees.
Defendants vigorously assert that quantifying GHG emissions at the leasing stage would
be overly speculative, 22 but that assertion is belied by an administrative record replete with
information on oil and gas development and GHG emissions. The EAs include raw data that
would allow BLM to project the pace and scope of oil and gas development on the leased
parcels. See AR28179 (stating, in the May 2016 High Plains EA, that from 1960 through 2011,
“6.5 percent of the [oil and gas] leases sold and 5.3 percent of the acreage was actually
developed into production”); AR28217 (calculating the number of active oil and gas wells in the
High Plains District as of 2010, and the average annual number of APDs approved by each field
office in that District from 2000 through 2010); AR28220 (noting that in 2010, the High Plains
District “accounted for approximately 59 percent of the total Federal wells in Wyoming and 66
percent of the total wells”); AR3430–31 (approximating the number of oil and gas wells spudded
22
Defendants admit in the administrative record and in their briefing that some level of
GHG emissions were reasonably foreseeable at the leasing stage. See, e.g., BLM Mem. at 25;
AR3411 (stating that “[s]everal activities that occur in the” relevant field office planning areas
“contribute to the phenomena of climate change,” including “emissions of greenhouse gases
(GHGs) . . . from fossil fuel development”).
30
annually in the relevant planning areas). And the EAs demonstrate that BLM could project GHG
emissions resulting from that development. See AR28220 (calculating the total and per-well
GHG emissions from wells in the High Plains District in 2010); AR55016 (calculating an
approximate per-well GHG emissions figure); 23 see also Western Alliance Mem. at 26–29
(summarizing the data contained in the EAs).
The EAs also incorporate studies quantifying and categorizing GHG emissions more
generally. For instance, several EAs cite the Wyoming GHG Inventory, see AR3412; AR19503,
which quantifies and forecasts the state’s consumption-based GHG emissions through 2020.
AR83658–60. Similarly, the May 2015 High Desert EA includes a chart projecting methane
emissions from fossil fuel development. AR3435.
Finally, the EAs tier to EISs containing “thousands of pages of quantitative . . . analyses,
including additional analys[e]s of GHG emission and climate change impacts.” Western
Alliance Mem. at 34. For instance, several EAs tier to the GHG emissions assessments
conducted for the Wyoming Greater Sage-Grouse EIS, see AR19457; AR28442; AR35284;
AR54979, which projects oil and gas development in certain field office planning areas and
quantifies and projects GHG emissions for those planning areas. See AR86687–87309. This
EIS also projects GHG emissions for specific oil and gas well types. See AR87264–65, tbl.4-4.
Several EAs also tier to the Rawlins Resource Management Plan Air Quality Impact Technical
23
Plaintiffs dispute the EAs’ per-well GHG emissions estimates in their EA protests, see
AR12518, and in their briefing, see Pls. Reply at 9–10. However, BLM explained in the EAs
how it derived this estimate. See AR13753–54. And it is “clearly within the expertise and
discretion of the agency to determine proper testing methods.” Sierra Club v. U.S. Dep’t of
Transp., 753 F.2d 120, 128 (D.C. Cir. 1985). The Court thus declines to wade into this debate.
That said, Plaintiffs have raised valid questions regarding whether BLM’s figure is
mathematically correct. See Pls. Reply at 9 (identifying record evidence suggesting that BLM
erroneously interpreted certain data). On remand, BLM must confirm the estimates’ accuracy.
31
Support Document, which projects short-term and long-term annual GHG emissions and
analyzes potential emissions mitigation measures based on those measures’ costs, limitations and
effectiveness. See AR68747–67. And multiple EAs tier to the May 2015 Buffalo EIS, which
estimates 2024 GHG emissions in the Buffalo field office planning area for various oil, gas, and
coal development alternatives, and compares those estimates to the projected state-wide GHG
emissions. See ECF No. 63-1 at 16–30; 24 see also AR78456–604 (Bighorn Basin EIS containing
similar projections).
In sum, given the mix of information available to BLM at the leasing stage, NEPA
required that BLM reasonably quantify the GHG emissions resulting from oil and gas
development on the leased parcels in the aggregate. BLM had at its disposal estimates of (1) the
number of wells to be developed; (2) the GHG emissions produced by each well; (3) the GHG
emissions produced by all wells overseen by certain field offices; and (4) the GHG emissions
produced by all wells in the state. With this data, BLM could have reasonably forecasted, by
multiple methods, the GHG emissions to be produced by wells on the leased parcels. See Sierra
Club II, 867 F.3d at 1374 (holding that an agency was required to make “educated assumptions”
in quantifying GHG emissions, where the agency possessed information allowing for reasonable
forecasting); Wilderness Workshop v. BLM, 342 F. Supp. 3d 1145, 1156 (D. Colo. 2018) (“It is
arbitrary and capricious for a government agency to use estimates of energy output for one
portion of an EIS, but then state that it is too speculative to forecast effects based on those very
outputs.”). BLM places the burden of analyzing the data on the public, stating that “[a]n
interested citizen would be able to draw a number of useful conclusions” from the information
24
This EIS was “inadvertently omitted from the administrative record” submitted to the
Court. BLM Mem. at 9 n.4. It was instead filed in conjunction with BLM’s motion for summary
judgment. Plaintiffs do not challenge its authenticity.
32
provided. BLM Mem. at 27. That may be true, but it did not relieve BLM of its burden to
consolidate the available data as part of its “informed decisionmaking,” before issuing the leases
and irretrievably committing to drilling on the parcels. WildEarth Guardians v. Jewell, 738 F.3d
at 303 (quoting New York v. Nuclear Regulatory Comm’n, 681 F.3d 471, 476 (D.C. Cir. 2012)).
Defendants’ explanations for why BLM was not required to quantify GHG emissions at
the leasing stage are unpersuasive because they do not address the volume of information
available to BLM. First, Defendants argue—and the EAs assert—that GHG emissions from oil
and gas drilling were too difficult to forecast at the leasing stage, given (1) the mix of economic
drivers that could change future demand for oil and gas; (2) possible technological changes; (3)
the heterogenous land composition across the leased parcels; and (4) the various methods by
which wells may be spaced and drilled. See BLM Mem. at 22–24; Western Alliance Mem. at
24–26; AR11957; AR13989; AR18656; AR19524. 25 But as discussed above, BLM did in fact
have information allowing it to forecast GHG emissions. BLM could have expressed the
forecasts as ranges, and it could have explained the uncertainties underlying the forecasts, but it
was not entitled to simply throw up its hands and ascribe any effort at quantification to “a crystal
ball inquiry.” Scientists’ Inst. for Pub. Info., 481 F.2d at 1092; see also Sierra Club II, 867 F.3d
25
For instance, the July 2015 BLM Decision greenlighting the agency’s August 2015
lease sale noted “the substantial uncertainty that exists at the time the BLM offers a lease for sale
regarding crucial factors that will affect potential GHG emissions,” including:
well density; geological conditions; development type (vertical, directional,
horizontal); hydrocarbon characteristics; equipment to be used . . . ; and potential
regulatory changes pertaining to GHGs over the life of the 10-year primary lease
term.
AR12516. And the May 2015 High Desert EA noted that “[t]he degree of [environmental]
impact will also vary according to the characteristics of the geologic formations from which
production occurs.” AR3430.
33
at 1374 (“We understand that emission estimates would be largely influenced by assumptions
rather than direct parameters about the project, but some educated assumptions are inevitable in
the NEPA process.” (citing Scientists’ Inst. for Pub. Info., 481 F.2d at 1092)). 26
Second, and relatedly, Defendants argue that the EAs’ qualitative discussions of GHG
emissions and the possible environmental impacts of those emissions were sufficient under
NEPA. See Western Alliance Mem. at 30–33; API Mem. at 32. The EAs acknowledge that
GHGs from the leased parcels will contribute to climate change, they summarize current local
and regional climates, and they discuss how climate change may affect those climates. See, e.g.,
AR18634–36 (“Temperature in western Wyoming is expected to increase by 0.25 to 0.40
degrees Fahrenheit per decade while temperatures in surrounding locations in Utah, Wyoming,
and Colorado are expected to increase by 0.40 to 1.2 degrees Fahrenheit per decade.”);
AR34683–85 (listing “potential [climate] changes identified by the EPA that are expected to
occur at the regional scale, where the proposed action and its alternatives are to take place”).
They also tier to EISs containing similar qualitative analyses. See, e.g., AR76493–96 (discussing
the likely impacts of rising temperatures in the Bighorn Basin field office planning area). While
“qualitative analyses are acceptable in an [EA] where an agency . . . provides a reasonable
‘justification regarding why more definitive information could not be provided,’” League of
Wilderness Defs.-Blue Mountains Biodiversity Project v. U.S. Forest Serv., 689 F.3d 1060, 1076
(9th Cir. 2012) (citations omitted), BLM’s justification here—quantification would be overly
speculative and not helpful in conducting informed decisionmaking—was not reasonable given
26
In addition to the points made above, it should not be overlooked that there was enough
information at the leasing stage to allow the oil and gas industry to determine that certain leases
were sound long-term investments. If the industry had enough information to forecast the leases’
production, BLM should have had enough information to do the same.
34
the data available to BLM. 27 Thus, while BLM’s qualitative discussions of GHG emissions and
climate change no doubt contributed to informed decisionmaking, they alone were not enough.
Third, Defendants note that the challenged EAs tier to EISs issued at the land use
planning stage that engage in more robust quantitative and qualitative discussions of GHG
emissions. See Western Alliance Mem. at 33–37. But BLM admits that “the EISs tiered to for
the first and second lease sales [at issue] did not discuss GHGs and climate.” BLM Mem. at 16–
17. Moreover, GHG analyses conducted in EISs issued at the land use planning stage are
necessarily more general than analyses conducted at the leasing stage, and in some cases rely on
outdated data and methodologies. BLM at least implicitly acknowledges this in the record,
stating that the EISs’ oil and gas development projections were both “too coarse,” AR12518, and
too broad, AR28814, to support GHG emissions forecasts at the leasing stage. Under BLM’s
own regulations, because the EISs were not “adequate to support” BLM’s leasing stage GHG
27
Defendants also rely on various agency policy statements to support this argument.
For instance, Western Alliance cites 2008 and 2011 draft BLM guidance permitting BLM field
offices to forgo quantitative analyses of climate change. See Western Alliance Mem. at 17
(citing AR56279; AR56464). Western Alliance also cites a 2010 memorandum issued by
BLM’s Wyoming state office instructing BLM field offices to qualitatively discuss GHG
emissions and climate change. Id. at 18 (citing AR81582). But BLM’s draft guidance is not
binding or persuasive authority for this Court, see S. Utah Wilderness All. v. Dabney, 222 F.3d
819, 829 (10th Cir. 2000) (holding that draft agency guidance that has not been “finalized or
adopted by the agency” is afforded no judicial deference), and BLM’s ability to reliably project
and analyze GHG emissions has presumably improved in the years since the guidance and
memorandum were issued, cf. City of Dall. v. Hall, 562 F.3d 712, 720 (5th Cir. 2009) (“Properly
analyzing the risks of an action requires an agency to use updated information or data . . . .”).
Similarly, American Petroleum cites 2014 draft CEQ guidance providing BLM field offices with
“discretion, based on their expertise and experience, to determine whether and to what extent to
prepare an analysis” of climate change. See API Mem. at 13 (citing AR56910). But again, the
2014 CEQ draft guidance was never formalized and is not binding on this Court; BLM at times
explicitly disavowed reliance on that guidance, see AR34585 (noting that the guidance “has not
been formalized” as a NEPA requirement, in response to a WildEarth comment relying on the
guidance); and whatever discretion the draft guidance grants, it cannot give BLM field offices
discretion to ignore NEPA’s “hard look” requirement. The policy statements cited in
Defendants’ briefs and the EAs do not alter the Court’s conclusions.
35
emissions projections, BLM was required to “provide any [additional] necessary analysis.” 43
C.F.R. § 46.140(b). Accordingly, BLM failed to take a hard look at the environmental impacts
of leasing because it failed to quantify and forecast aggregate GHG emissions from oil and gas
development.
d. BLM Must Discuss Downstream GHG Emissions in Greater Detail
Plaintiffs also argue that BLM failed to sufficiently consider another potential effect of
leasing: the GHG emissions generated by the use of oil and gas pulled from the leased parcels.
NEPA requires an agency to evaluate the indirect effects of a proposed action, “which are caused
by the action and are later in time or farther removed in distance, but are still reasonably
foreseeable.” 40 C.F.R. § 1508.8(b). Again, “[i]n determining what effects are ‘reasonably
foreseeable,’ an agency must engage in reasonable forecasting and speculation,” Sierra Club I,
867 F.3d at 198 (quoting Del. Riverkeeper, 753 F.3d at 1310), but it “need not foresee the
unforeseeable.” Scientists’ Inst. for Pub. Info., 481 F.2d at 1092. NEPA thus “‘requires a
reasonably close causal relationship between the environmental effect and the alleged cause,’
analogous to proximate causation from tort law.” Sierra Club I, 867 F.3d at 198 (quoting Sierra
Club (Freeport), 827 F.3d at 47). Building on that standard, in determining whether an agency
must consider particular types of information in its NEPA analyses, a court must consider the
“usefulness of any new potential information to the decisionmaking process.” Pub. Citizen, 541
U.S. at 767 (citation omitted). Thus, just as baseless speculation is unhelpful, so too is
information that the agency “lacks [any] power to act on.” Sierra Club I, 867 F.3d at 198
(quoting Pub. Citizen, 541 U.S. at 768).
Plaintiffs contend that GHG emissions from “downstream” use of oil and gas were an
indirect effect of BLM’s leasing decisions that BLM “failed to even acknowledge.” See Pls.
36
Mem. at 20–21. 28 Defendants respond that (1) downstream GHG emissions are not an indirect
effect of oil and gas leasing, see Western Alliance Reply at 12–14, ECF No. 83; API Mem. at
33–36; and (2) even if they are an indirect effect, the EAs’ qualitative discussions of GHG
emissions and climate change were sufficient, see BLM’s Mem. at 22–27, States Mem. at 16–20.
These responses raise a simple, but nuanced, question: at what point does the foreseeable effect
of an agency decision become too attenuated to be an “indirect effect” requiring NEPA analysis?
28
BLM argues that Plaintiffs waived this argument “with respect to the first three [lease]
sales, all in 2015,” because Plaintiffs failed to “call[] BLM’s attention” to them at the time the
sales were authorized. BLM Mem. at 22. BLM is correct that “[a] party will normally forfeit an
opportunity to challenge an agency [decision] on a ground that was not first presented to the
agency for its initial consideration.” Guindon v. Pritzker, 31 F. Supp. 3d 169, 189 (D.D.C. 2014)
(quoting Flaherty v. Bryson, 850 F. Supp. 2d 38, 57 (D.D.C. 2012)); accord Pub. Citizen, 541
U.S. at 764; Vt. Yankee, 435 U.S. at 553–54. However, an argument is not forfeited when “the
agency has had an opportunity to consider the identical issues presented to the court but which
were raised by other parties” in the administrative proceeding. CTIA-The Wireless Ass’n v. FCC,
466 F.3d 105, 117 (D.C. Cir. 2006) (quoting Nat. Res. Def. Council, Inc. v. EPA, 824 F.2d 1146,
1151 (D.C. Cir. 1987)); see also Guindon, 31 F. Supp. 3d at 189. Thus, so long as BLM was
aware during its 2015 leasing decisions that certain stakeholders believed it should consider
downstream GHG emissions in its environmental analyses, it is irrelevant whether Plaintiffs
themselves raised the issue. See CTIA, 466 F.3d at 117 (holding that the plaintiff could assert an
argument raised by third parties’ comments to the defendant agency); Wyo. Lodging & Rest.
Ass’n v. U.S. Dep’t of Interior, 398 F. Supp. 2d 1197, 1208, 1210–11 (D. Wyo. 2005) (holding
that the plaintiffs could challenge an EA despite not providing “meaningful participation in the
public processes” by which the EA was drafted, because non-parties submitted comments
addressing the issues raised by the plaintiffs).
Here, the record indicates that BLM was aware, when drafting its EAs for the 2015 lease
sales, that downstream GHG emissions would be an issue for stakeholders. In its response to
comments to the draft May 2015 EA, BLM acknowledged that it did not attempt to “quantify
costs and benefits associated with drilling, possible production or eventual combustion of fluid
minerals from the lease parcel.” AR3337 (emphasis added). Three commenters, including
WildEarth, requested that downstream combustion of oil and gas play a role in BLM’s two
August 2015 EAs. See AR12093; AR12257–58; AR12329–30 (“The very purpose of oil and gas
leasing is the production, and subsequent combustion, of hydrocarbon fossil fuels.”). And
WildEarth requested that BLM consider “both emissions produced onsite and those created from
the burning of the oil and gas likely to be produced” on the leased parcels, in its November 2015
EA. AR16834. Because BLM had notice of this issue when drafting the 2015 EAs, Plaintiffs
may raise it now.
37
The Supreme Court considered this very question in Public Citizen, in which it addressed
the NEPA obligations of an agency setting safety standards for Mexican trucks operating in the
United States. 541 U.S. at 765. Once the agency established the standards, Mexican trucking
companies would be authorized by statute to perform cross-border services. Id. at 765–66.
Although the relevant statutory provision would be triggered only by the agency’s action, the
Court held that the agency, in taking that action, was not required to address the environmental
effects of increased Mexican truck traffic. Id. at 766–69. Because the agency itself had no
statutory authority to exclude Mexican trucks from the United States, the agency had no
obligation to gather data on the environmental harms of admitting them. Id.
Applying that principle in more analogous circumstances, the D.C. Circuit recently held
that FERC, in authorizing upgrades to natural gas shipping terminals, was not required to address
the environmental effects of gas exports flowing through the terminals. See Sierra Club
(Freeport), 827 F.3d at 47–48; Sierra Club v. FERC, 827 F.3d 59, 68–69 (D.C. Cir. 2016);
EarthReports, 828 F.3d at 955–56. Those exports could be authorized only by a different
agency, and FERC could not refuse to approve a terminal upgrade based on the effects of a
decision “over which [it] [had] no regulatory authority.” Sierra Club (Freeport), 827 F.3d at 48.
The touchstone of these cases is that an agency need not consider environmental effects that
cannot influence its decision. See Sierra Club II, 867 F.3d at 1373.
Even under the heightened causation standard established by Public Citizen and Sierra
Club (Freeport), downstream GHG emissions from fossil fuel use are an indirect effect of
BLM’s oil and gas leasing program at issue here. The D.C. Circuit reached the same conclusion
under similar circumstances in Sierra Club II, a case debated heavily by the parties. Sierra Club
II required the Circuit to address whether FERC was obligated to consider, in an EA evaluating a
38
proposed natural gas pipeline, the GHG emissions from the use of the gas transported by that
pipeline. 867 F.3d at 1371. First, the Circuit noted that a reasonably foreseeable effect of
authorizing a pipeline to transport natural gas is the burning of that gas and the generation of
GHGs. Id. at 1371–72. Second, the Circuit concluded that FERC could decline to approve the
pipeline “on the ground that [it] would be too harmful to the environment.” Id. at 1373. Given
those factors, the Circuit held that FERC’s pipeline authorization was a “legally relevant cause”
of downstream GHG emissions from gas transported by the pipeline, and NEPA required
FERC’s EA to consider those emissions. Id. (quoting Sierra Club (Freeport), 827 F.3d at 47).
Sierra Club II’s logic applies equally here to the Wyoming Lease Sales. Producing oil
and gas for consumption “is the [leasing] project’s entire purpose.” Sierra Club II, 867 F.3d at
1372. Downstream use of oil and gas, and the resulting GHG emissions, are thus reasonably
foreseeable effects of oil and gas leasing. And just as FERC could decline to approve a pipeline
on environmental grounds, BLM could decline to sell the oil and gas leases at issue here if the
environmental impact of those leases—including use of the oil and gas produced—would not be
in the public’s long-term interest. See 30 U.S.C. § 226(a) (holding the Secretary responsible for
oil and gas leasing); 43 U.S.C. § 1732(a) (stating that the Secretary shall manage public lands
“under principles of multiple use and sustained yield”); id. § 1712(c)(7) (requiring the Secretary
to “weigh long-term benefits to the public against short-term benefits” when developing land use
plans). 29 Thus, the lease sales are a “legally relevant cause” of downstream GHG emissions, and
BLM was required to consider those emissions as indirect effects of oil and gas leasing. See
29
Defendants’ supplemental briefing indicates that BLM cannot categorically halt all oil
and gas leasing as a matter of policy. See API Suppl. Br. at 2–4. Defendants do not argue,
however, that BLM cannot withhold certain oil and gas leases based on the environmental
impacts of those specific leases. The EAs themselves anticipate this possibility; they discuss
“No Action” alternatives in which BLM does not offer any parcels for sale. See AR18593.
39
Wilderness Workshop, 342 F. Supp. 3d at 1155 (“[C]ombustion emissions are an indirect effect
of an agency’s decision to extract . . . natural resources.”); San Juan Citizens All., 326 F. Supp.
3d at 1242–43 (same, collecting cases). Defendants’ reliance on Public Citizen, Sierra Club
(Freeport), and their progeny is unpersuasive because unlike the agencies in those cases, here
BLM could act on information regarding downstream GHG emissions.
Although it is clear that BLM was obligated to discuss downstream GHG emissions in its
EAs, the level of detail required in those discussions is less clear. Plaintiffs imply that BLM
should have quantified and forecasted downstream emissions in the same manner that it should
have quantified and forecasted emissions from drilling itself. Pls. Mem. at 21; Pls. Reply at 11–
13, ECF No. 76. However, several of the cases that Plaintiffs cite in support of that argument are
distinguishable on their facts. They involved applications to expand existing coal mining
operations, where each operation existed for the “sole purpose” of supplying a nearby power
plant. See Dine Citizens Against Ruining Our Env’t (“Dine CARE”) v. U.S. Office of Surface
Mining Reclamation and Enf’t (“OSMRE”), 82 F. Supp. 3d 1201, 1212–14 (D. Colo. 2015);
WildEarth Guardians v. OSMRE, 104 F. Supp. 3d 1208, 1230 (D. Colo. 2015). Under those
circumstances, where the mine and the power plant were “interdependent,” it was “possible to
predict with certainty the combustion-related environmental impacts” of the downstream
emissions, and NEPA required such an analysis at the application stage. Dine CARE, 82 F.
Supp. 3d at 1212–13; WildEarth Guardians, 104 F. Supp. 3d at 1230. Because the coal had a
single downstream use, its downstream environmental impact could be estimated to a greater
degree of certainty than the downstream impact of oil and gas from the Wyoming Leases sold on
the open market.
40
Defendants, unsurprisingly, argue that the EAs’ current discussions are sufficient under
NEPA. The EAs acknowledge that oil and gas combustion increases GHG emissions and
contributes to climate change. See AR3396; AR12369; AR28195. Several EAs also reference
the Wyoming GHG Inventory, which projects consumption-based GHG emissions in the state.
See AR11959–60; AR28219. Much like their approach to GHG emissions from oil and gas
drilling, Defendants claim that uncertainty regarding technology, well characteristics, market
forces, and regulation would render any further quantification of downstream GHG emissions
unhelpful at the leasing stage. See BLM Mem. at 22–23. BLM provided a similar explanation to
WildEarth at various points in the administrative proceedings:
[H]ow crude oil will be used, whether any or all of the oil will be refined for plastics
or other products that will not be burned; the possible mix of ultimate uses with
disparate carbon emissions (e.g. auto fuel, bunker oil, diesel, kerosene); and the
market forces that November [sic] replace lost BLM production with production
from other sources are all uncertain. Therefore, the greenhouse gas emissions that
[may] ultimately result from the consumption of products derived from the crude
oil generated on BLM lands would not be reasonably foreseeable . . . .
AR19283–84; see also AR12518.
Defendants rely primarily on Sierra Club I in support of their argument that BLM need
not conduct any further analyses of downstream GHG emissions. But like Plaintiffs’ reliance on
the coal mining cases, Defendants’ reliance on Sierra Club I suffers from a clear difference in
the agency’s ability to forecast the indirect effect at issue. Sierra Club I involved the
Department of Energy’s NEPA analysis of its decision to approve natural gas exports. 867 F.3d
at 195. Authorizing exports would trigger increased domestic natural gas production, and the
agency could consider that indirect effect in its decisionmaking. Id. at 196–97. Notwithstanding
this causal connection, the D.C. Circuit held that the agency was not required to quantify the
domestic production increase or its environmental effects at the local level. Id. at 198–99.
Quantification would require the agency to speculate as to where in the country increased natural
41
gas production would occur, based on local geology, regulations, land use patterns, and the
development of supporting infrastructure. Id. at 199. Thus, “an economic model estimating
localized impacts would be far too speculative to be useful.” Id. (citation omitted). While Sierra
Club I illustrates that an agency need not “foresee the unforeseeable,” Scientists’ Inst. for Pub.
Info., 481 F.2d at 1092, projecting nationwide natural gas production and its localized effects is a
far cry from projecting the consumption of a reasonably forecastable amount of oil and gas.
The Court lands in the middle of the parties’ arguments. The EAs’ sparse discussions of
downstream GHG emissions are insufficient under NEPA, given BLM’s ability to forecast oil
and gas production and given that the entire purpose of oil and gas leasing is to generate a greater
supply of oil and gas for downstream use. That said, the Court will not require that BLM
quantify downstream emissions. See Sierra Club II, 867 F.3d at 1374 (holding that that
“quantification of [GHG emissions] is [not] required every time those emissions are an indirect
effect of an agency action,” so long as the agency provides “a satisfactory explanation for why”
quantification is not useful); Mid States Coal. for Progress v. Surface Transp. Bd., 345 F.3d 520,
550 (8th Cir. 2003) (holding that an agency violated NEPA when it “completely ignored the
effects of increased coal consumption” on air quality, but that the agency was not required to
quantify those effects in detail); Dine CARE, 82 F. Supp. 3d at 1213 (noting that in “a scenario in
which a coal mine markets its coal freely to multiple buyers, each of whom uses that coal in
different applications under different constraints,” an agency need not necessarily quantify
downstream emissions).
On remand, BLM must strengthen its discussions of the environmental effects of
downstream oil and gas use. It must also consider whether quantifying GHG emissions from that
use is reasonably possible, including through the use of the emissions calculator suggested by
42
Plaintiffs. See Pls. Mem. at 21. 30 If BLM decides that quantification is not possible or helpful, it
must thoroughly explain that decision. And, if BLM receives estimates from outside parties
based on the use of such calculators, it must assess those estimates and explain why they are
unreliable or otherwise inappropriate to use in its decisionmaking.
e. BLM Must Discuss the Cumulative Effects of GHG Emissions in Greater Detail
Finally, Plaintiffs contend that “BLM failed to provide any quantified or detailed
information on cumulative GHG impacts . . . which is far below the threshold of meaningful
analysis this Circuit demands.” Pls. Mem. at 22 (citations and internal quotation marks omitted).
“NEPA’s implementing regulations require an agency to evaluate ‘cumulative impacts’ along
with the direct and indirect impacts of a proposed action.” TOMAC, 433 F.3d at 864 (citing
Grand Canyon Trust v. FAA, 290 F.3d 339, 345 (D.C. Cir. 2002)). A cumulative impact is “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.” 40 C.F.R. § 1508.7. “Cumulative impacts can result from individually minor but
collectively significant actions taking place over a period of time.” Id. § 1508.7; see also id. §
1508.25(c) (stating that actions should be considered together when they have significant
30
The Court does not mandate the calculator’s use, just its consideration. Cf. Or. Envtl.
Council v. Kunzman, 817 F.2d 484, 496 (9th Cir. 1987) (“NEPA does not require that we decide
whether an [EIS] is based on the best scientific methodology available, nor does NEPA require
us to resolve disagreements among various scientists as to methodology.” (quoting Friends of
Endangered Species, Inc. v. Jantzen, 760 F.2d 976, 986 (9th Cir. 1985))); Cape Hatteras Access
Pres. All. v. U.S. Dep’t of Interior, 731 F. Supp. 2d 15, 35 (D.D.C. 2010) (holding that “NEPA
allows the agency the discretion of what methodology to use and does not require the use of the
best scientific methodology available”); City of Williams v. Dombeck, 151 F. Supp. 2d 9, 23
(D.D.C. 2001) (holding that the Forest Service did not violate NEPA by failing to apply the
plaintiffs’ preferred methodology, where the plaintiffs did “not demonstrate[] that the Forest
Service’s methodology violated agency regulations or were somehow beyond agency
discretion”).
43
combined impacts). In the D.C. Circuit, a proper NEPA cumulative impact analysis involves a
discussion of:
(1) the area in which the effects of the proposed project will be felt; (2) the impacts
that are expected in that area from the proposed project; (3) other actions—past,
present, and proposed, and reasonably foreseeable—that have had or are expected
to have impacts in the same area; (4) the impacts or expected impacts from these
other actions; and (5) the overall impact that can be expected if the individual
impacts are allowed to accumulate.
Grand Canyon Trust, 290 F.3d at 345.
Plaintiffs mount a two-pronged challenge to the EAs’ cumulative impacts analyses. First,
Plaintiffs claim that BLM failed to discuss the projected GHG emissions from the leased parcels,
“added to other past, present, and reasonably foreseeable BLM-managed oil and gas emissions
on a regional, national, and global scale,” as NEPA required. Pls. Mem. at 23–24. Second,
Plaintiffs claim that after quantifying GHG emissions, BLM should have applied a tool to
quantify the emissions’ cumulative impact on climate change. Id. at 26. Plaintiffs are correct in
part. BLM’s failure to quantify GHG emissions rendered the EAs’ cumulative impact analyses
inadequate, but BLM was not required to apply Plaintiffs’ proposed climate change protocols.
i. BLM’s Cumulative Effect Analyses Lacked Adequate GHG Quantification
Plaintiffs contend that NEPA required the challenged EAs to compare GHG emissions
from the leased parcels to emissions from other BLM-managed projects in the region and across
the country. Id. at 23–24. Thus, according to Plaintiffs, BLM’s refusal to quantify GHG
emissions rendered the EAs’ cumulative impacts analyses inadequate. The Court agrees.
The EAs and Defendants’ briefs acknowledge the cumulative, global nature of climate
change. For instance, the November 2015 High Desert EA states that selling leases “may
contribute to the effects of climate change through GHG emissions.” AR19551. It also states
that climate change occurs at the “global,” “regional,” and “local” scales. AR19528; see also
44
BLM Mem. at 28 (“GHG emissions and their effect on the climate . . . are necessarily
cumulative, and necessarily global in nature.”). It lists the number of active wells in the district.
AR19551; see also AR13763 (comparing the number of active wells in the High Plains district to
the number of active wells in Wyoming). Finally, it states that “[t]he average number of oil and
gas wells drilled annually in the [district] and probable GHG emission levels, when compared to
the total GHG emission estimates from the total number of federal oil and gas wells in the state,
represent an incremental contribution to the total regional and global GHG emission levels.”
AR19552; see also AR13763; AR28503. This conclusion, however, is not supported by any data
because BLM declined to quantify the “probable GHG emission levels” arising from the leased
parcels. Each challenged EA suffers from this deficiency.
True, the EAs tiered to EISs conducted at the land use planning stages that, at least in
some cases, quantify and forecast GHG emissions at the regional level and compare those
forecasts to state and national forecasts. See AR19552 (citing the Wyoming Greater Sage-
Grouse EIS). However, the lease sales included parcels from multiple planning areas covered by
different resource management plans, some of which do not quantify and forecast GHG
emissions. See AR28503 (tiering to the 1988 Grass Creek Resource Management Plan and the
1998 Washakie Resource Management Plan in its “Cumulative Impact Analysis” discussion).
Without access to a data-driven comparison of GHG emissions from the leased parcels to
regional and national GHG emissions, the public and agency decisionmakers had no context for
the EAs’ conclusions that GHG emissions from the leased parcels would represent only an
“incremental” contribution to climate change. Likewise, they could not conceptualize the extent
to which the lease sales would contribute to the local, regional, and global climate change
45
discussed qualitatively in the EAs and tiered EISs. See, e.g., AR3411–12; AR19552–53;
AR76493–96.
BLM protests that under Plaintiffs’ view, it “would be required to identify any past,
present, or reasonably foreseeable GHG-emitting projects worldwide,” an “impossible” scope of
analysis. BLM Mem. at 28. BLM is correct that NEPA does not require the impossible. It does,
however, require that BLM quantify the emissions from each leasing decision—past, present, or
reasonably foreseeable—and compare those emissions to regional and national emissions, setting
forth with reasonable specificity the cumulative effect of the leasing decision at issue. To the
extent other BLM actions in the region—such as other lease sales—are reasonably foreseeable
when an EA is issued, BLM must discuss them as well. Likewise, on remand, if BLM may
reasonably quantify downstream GHG emissions, it must place those emissions in the context of
local and regional oil and gas consumption. These quantitative analyses, combined with a robust
qualitative discussion of local, regional, and national climate change, would satisfy NEPA’s hard
look requirement. See WildEarth Guardians v. Jewell, 738 F.3d at 310 (holding that BLM
properly considered a proposed coal mine’s cumulative climate change impact where it
“evaluated GHG emissions as a percentage of state—and nation-wide emissions.”); WildEarth
Guardians v. BLM, 8 F. Supp. 3d 17, 35–36 (D.D.C. 2014) (holding that BLM sufficiently
examined the cumulative impact of a proposed lease sale where it quantified the GHG emissions
from the leased parcels and compared them to state-wide and nation-wide emissions). Although
BLM may determine that each lease sale individually has a de minimis impact on climate
change, the agency must also consider the cumulative impact of GHG emissions generated by
past, present, or reasonably foreseeable BLM lease sales in the region and nation.
46
ii. BLM’s Choice of Methodology was Appropriate
Plaintiffs also offer that BLM could have used certain protocols to quantify the climate
change impact of GHG emissions from the leased parcels. More specifically, Plaintiffs argue
that by not utilizing the “social cost of carbon” and the “global carbon budget,” BLM “arbitrarily
dismissed the need to analyze cumulative GHG impacts.” Pls. Mem. at 26. Plaintiffs are correct
that NEPA required BLM to undertake a more robust discussion of GHG emissions at the leasing
stage. Plaintiffs’ contentions regarding their suggested protocols, however, are of the
flyspecking variety. BLM’s decision to forgo the protocols’ use does not rise to the level of a
NEPA violation.
The social cost of carbon protocol monetizes GHG emissions. See Pls. Mem at 32.
Plaintiffs claim that BLM was required to utilize this protocol because the agency “include[d] the
economic benefits of oil and gas leasing and production in its leasing decisions.” Pls. Mem. at
32 (citing AR3425; AR13737; AR19518; AR28459; AR35335–36). According to Plaintiffs, it
was arbitrary and capricious for BLM to discuss the economic benefits of oil and gas drilling
without quantifying their economic costs.
Although the EAs briefly mention the economic benefits of oil and gas drilling, the
sparseness of those discussions differentiates this case from High Country Conservation
Advocates v. United States Forest Service, on which Plaintiffs rely. The High Country court held
that it was arbitrary for BLM to forgo using the social cost of carbon when the agency’s
challenged EIS stated that “nearly a billion dollars in lost revenues, royalties, payroll and local
payment for goods and services would be foregone by” declining to approve a proposed coal
mine. 52 F. Supp. 3d 1174, 1191 (D. Colo. 2014). BLM’s decision was particularly
inappropriate because the agency had included the social cost of carbon in a draft EIS, and the
47
final draft contained the “factually inaccurate justification” that no tool existed to quantify the
climate change impact resulting from the mine’s approval. Id.
The EIS at issue in High Country suffered from deficiencies not present in the EAs
challenged here. First, while the High Country EIS touted its “economic objectives” and the
“billion dollars” to be gained by approving the coal mine, here, the EAs’ discussions of
economic benefits were abbreviated and involved little quantification. See AR18650–51 (listing
profits from previous lease sales and calculating that the November 2015 sale would yield
$152,364); AR28459 (stating that “the State of Wyoming receives a percentage of the Federal oil
and gas lease sale receipts,” without calculating the dollar value of that percentage). Second,
BLM explained here that “because of the speculative nature of development [it did] not attempt
to quantify costs and benefits associated with drilling, possible production or eventual
combustion of fluid minerals.” AR2827. The Court does not agree that the EAs’ cursory
discussion of the economic benefits of oil and gas development obligated BLM to specifically
monetize climate change at the leasing stage. See 40 C.F.R. § 1502.23 (“[T]he weighing of the
merits and drawbacks of the various alternatives need not be displayed in a monetary cost-benefit
analysis . . . .”).
Also, unlike the misleading explanation flagged by the High Country court, BLM here
provided reasoned explanations for why it declined to use the social cost of carbon protocol.
See, e.g. AR8920–23; AR12993–98. BLM explained that in the context of each lease sale,
“calculating the [social cost of carbon] from CO2 emissions from the combustion of an unknown
quantity of produced oil and gas would be highly speculative,” AR2827, and that the range
provided by WildEarth’s comments and protests “represents a 4,000% difference in potential
[social cost of carbon] estimates.” AR12520; see also AR1986 (estimating that “[u]sing 2015
48
social cost of carbon values, the costs to society of the federal fossil fuel leasing program is
between $18 and $177 billion per year”). BLM reasonably determined that a 4,000 percent
range in potential costs would be “less than helpful in informing the public and the decision-
maker.” AR12520; see also AR19285 (“While we agree that some level of uncertainty is
unavoidable in assessing impacts from complex environmental systems, in this case that
uncertainty is compounded by basing any potential [social cost of carbon] estimates on
speculative GHG emissions.”).
That reasoned determination is entitled to deference. See EarthReports, 828 F.3d at 956
(deferring to the agency’s decision to not utilize the social cost of carbon given, among other
reasons, the methodology’s “significant variation in output”). And Plaintiffs have identified no
case law—outside of situations in which an agency quantified the economic benefits of an
action—suggesting that BLM violates NEPA when it fails to include the social cost of carbon in
an EIS or an EA. See Wilderness Workshop, 342 f. Supp. 3d at 1159–60 (“[BLM] chose not to
[apply the social cost of carbon], provided sufficient support in the record to show this, and thus
satisfied NEPA in this respect.”); W. Org. of Res. Councils v. BLM, No. 16-21-GF-BMM, 2018
WL 1475470, at *14 (D. Mont. Mar. 26, 2018) (“[D]espite the benefits of the social cost of
carbon protocol, NEPA does not require a cost-benefit analysis under these circumstances.”).
Moreover, while Plaintiffs make a policy argument for the use of the global carbon
budget, Pls. Mem. at 27–30, they cite no case law or statute suggesting that BLM must
implement that protocol at the leasing stage. While an agency must apply a sufficient level of
rigor to its NEPA analyses, it is within “the expertise and discretion of the agency” to determine
the methodologies underlying those analyses. Sierra Club v. U.S. Dep’t of Transp., 753 F.2d
120, 128 (D.C. Cir. 1985). Accordingly, BLM did not act arbitrarily and capriciously in not
49
utilizing the global carbon budget. “[B]ecause current climate science is uncertain (and does not
allow for specific linkage between particular GHG emissions and particular climate impacts) . . .
evaluating GHG emissions as a percentage of state-wide and nation-wide emissions . . . is a
permissible and adequate approach.” WildEarth Guardians v. BLM, 8 F. Supp. 3d at 35 (citing
WildEarth Guardians v. Jewell, 738 F.3d at 309); see also Barnes v. U.S. Dep’t of Transp., 655
F.3d 1124, 1139 (9th Cir. 2011) (“the effect of [GHGs] on climate is a global problem[,] a
discussion in terms of percentages is therefore adequate for [GHG] effects”) (citation omitted).
While BLM could have utilized one of Plaintiffs’ suggested protocols, and there may have been
good policy reasons to do so, its failure to do so here based on the record presented did not run
afoul of NEPA’s “rule of reason.” 31 Sierra Club II, 867 F.3d at 1368. 32
2. BLM’s FONSIs Were Inadequate
Plaintiffs’ second core argument is that the FONSIs accompanying the challenged EAs
were deficient, as were BLM’s decisions to not issues EISs. As a reminder, an agency must draft
and issue an EIS—a robust environmental analysis—for every major federal action that will
“significantly affect” the quality of the human environment. 42 U.S.C. § 4332(C). To determine
if an action will significantly affect the environment, an agency generates an EA. 40 C.F.R. §
1508.9. And if the agency concludes, based on the EA, that it need not prepare an EIS, the
31
That said, on remand, BLM must reassess whether the social cost of carbon or another
methodology for quantifying climate change may contribute to informed decisionmaking.
“Accurate scientific analysis” is “essential to implementing NEPA.” 40 C.F.R. § 1500.1(b).
And NEPA requires an agency to ensure “scientific integrity” in its environmental assessments.
Id. § 1502.24. BLM may not forgo using the social cost of carbon simply because courts have
thus far been reluctant to mandate it. Given that the Department of Energy and other agencies
consider the social cost of carbon reliable enough to support rulemakings, see Zero Zone, Inc. v.
U.S. Dep’t of Energy, 832 F.3d 654, 677 (7th Cir. 2016), the protocol may one day soon be a
necessary component of NEPA analyses.
32
The Court does not determine here whether climate change quantification is
appropriate or required at the drilling stage.
50
agency must issue a FONSI explaining its reasoning. Id. § 1508.13. BLM decided not to
prepare EISs for the Wyoming Lease Sales, and instead issued EAs and FONSIs. 33
A court’s role in “reviewing an agency’s decision not to prepare an EIS is a limited one,
designed primarily to ensure that no arguably significant consequences have been ignored.”
Mayo v. Reynolds, 875 F.3d 11, 20 (D.C. Cir. 2017). When examining the adequacy of a
FONSI, courts in this jurisdiction assess whether the agency:
(1) has accurately identified the relevant environmental concern, (2) has taken a
hard look at the problem in preparing its [FONSI or Environmental Assessment],
(3) is able to make a convincing case for its finding of no significant impact, and
(4) has shown that even if there is an impact of true significance, an EIS is
unnecessary because changes or safeguards in the project sufficiently reduce the
impact to a minimum.
Sierra Club v. Van Antwerp, 661 F.3d 1147, 1154 (D.C. Cir. 2011) (alteration in original)
(quoting TOMAC, 661 433 F.3d at 861). “The D.C. Circuit makes clear that although the phrase
‘convincing case’ (found in factor three above) has appeared in the case law, the scope of review
is the usual one for reviewing administrative action—‘arbitrary, capricious, or an abuse of
discretion.’” Nat’l Parks Conservation Ass’n v. Semonite, 311 F. Supp. 3d 350, 361–62 (D.D.C.
2018) (citing Van Antwerp, 661 F.3d at 1154), rev’d on other grounds, 2019 WL 983691 (D.C.
Cir. Mar. 1, 2019).
Environmental significance is a function of a proposed agency action’s “context and
intensity.” 40 C.F.R. § 1508.27. “Context” requires that the action be “analyzed in several
contexts such as society as a whole (human, national), the affected region, the affected interests,
33
Each FONSI incorporated the environmental analysis contained in its corresponding
EA. See AR34719; see also 40 C.F.R. § 1508.13 (stating that if an EA is included with a
FONSI, the FONSI “need not repeat any of the discussion in the [EA] but may incorporate it by
reference”). The FONSIs did not engage in independent analyses, aside from brief discussions
of certain criteria mandated by agency regulations. See AR34720 (citing 40 C.F.R. § 1508.27)).
Thus, the EAs’ flaws discussed above also apply to the FONSIs.
51
and the locality.” Id. § 1508.27(a). And “intensity” refers “to the severity of impact.” Id. §
1508.27(b). Among other factors, CEQ regulations identify the following “significance factors”
that should be considered in evaluating intensity:
1. The degree to which the effects on the quality of the human environment are likely
to be highly controversial.
2. The degree to which the possible effects on the human environment are highly
uncertain or involve unique or unknown risks.
3. Whether the action is related to other actions with individually insignificant but
cumulatively significant impacts. Significance exists if it is reasonable to anticipate
a cumulatively significant impact on the environment. Significance cannot be
avoided by terming an action temporary or by breaking it down into small
component parts.
Id. § 1508.27(b)(4), (5), (7).
“Implicating any one of [those] factors may be sufficient to require development of an
EIS.” Nat’l Parks Conservation Ass’n v. Semonite, No. 18-5179, 2019 WL 983691, at *5 (D.C.
Cir. Mar. 1, 2019) (citing Grand Canyon Trust, 290 F.3d at 347). Plaintiffs contend that the
Wyoming Lease Sales implicated all three. Pls. Mem. at 35–36 (citing 40 C.F.R. §
1508.27(b)(4), (5), (7)). 34 In other words, Plaintiffs argue that the lease sales’ effects were
highly controversial, uncertain, and cumulatively significant, and that BLM failed to provide a
convincing case to the contrary. As discussed above, BLM’s EAs did not take a sufficient hard
look at the cumulative effects of GHG emissions from the leased parcels. The Court thus cannot
determine whether those effects were so significant that they warranted the creation of EISs. The
other two significance factors cited by Plaintiffs do not, standing alone, require BLM to generate
EISs here.
34
Plaintiffs concede that the challenged EAs properly identified climate change as a
relevant environmental concern. Pls. Mem. at 35.
52
a. The Court Cannot Conclude that the Effects of Leasing are Highly Controversial
First, Plaintiffs claim that the parties’ disputes regarding the size of the lease sales’
environmental effects, and BLM’s refusal to apply Plaintiffs’ suggested climate change
protocols, rendered the lease sales’ effects highly controversial. 40 C.F.R. § 1508.27(b)(4).
Controversy in this context is not measured merely by the intensity of the opposition. As the
D.C. Circuit recently noted, “‘certainly something more is required’ for a highly controversial
finding ‘besides the fact that some people may be highly agitated and be willing to go to court
over the matter.” Nat’l Parks Conservation Ass’n, 2019 WL 983691, at *6 (emphasis in
original) (quoting Fund for Animals v. Frizzel, 530 F.2d 982, 988 n.15 (D.C. Cir. 1975) (per
curiam)). Rather, an action is highly controversial only if there is, at minimum, “a substantial
dispute . . . as to the size, nature, or effect of the major federal action.” Town of Cave Creek, 325
F.3d at 331 (quoting Found. for N. Am. Wild Sheep v. U.S. Dep’t of Agric., 681 F.2d 1172, 1182
(9th Cir. 1982)). Courts in this jurisdiction suggest that even a substantial dispute may not
suffice; there must be “scientific or other evidence that reveals flaws in the methods or data
relied upon by the agency in reaching its conclusions.” Nat’l Parks Conservation Ass’n v.
United States, 177 F. Supp. 3d 1, 33 (D.D.C. 2016) (citations omitted); see also Sierra Club v.
Van Antwerp, 719 F. Supp. 2d 58, 67–68 (D.D.C. 2010) (“While declarations were submitted to
the Corps from numerous experts who claimed that [the development project] will have
significant adverse impacts on Cypress Creek and its wetlands, these declarations alone fail to
rise to the level of ‘controversy’ under NEPA.”), aff’d in part, rev’d in part on other
grounds, 661 F.3d 1147 (D.C. Cir. 2011), as amended, (Jan. 30, 2012); Fund for Animals v.
Norton, 281 F. Supp. 2d 209, 235 (D.D.C. 2003) (“While plaintiffs have identified serious gaps
in defendants’ assessment of the local effects of the proposed action, they do not appear to have
53
identified any scientific controversy per se as to the extent of the effects.”); cf. Humane Soc’y of
U.S. v. Dep’t of Commerce, 432 F. Supp. 2d 4, 19–20 (D.D.C. 2006) (holding that the potential
environmental effects of an agency decision were highly controversial where the defendant
agency’s own leadership expressed “an appreciation of the degree of controversy surrounding”
the effects).
Applying these principles, the Court cannot conclude at this point that the Wyoming
Lease Sales were highly controversial. First, although Plaintiffs have shown that BLM failed to
sufficiently analyze the environmental effects of its leasing decisions, they have not shown that
the magnitude of those effects is significantly higher than BLM represented. Presumably,
BLM’s environmental analyses on remand will more fully illustrate that magnitude. Second,
Plaintiffs have not identified record evidence suggesting that BLM faced opposition from other
government agencies with stakes or “special expertise” in the leasing decisions; a factor that
weighs heavily in many decisions finding agency actions to be highly controversial. See Nat’l
Parks Conservation Ass’n, 2019 WL 983691, at *7 (holding an agency project to be highly
controversial where the project faced “repeated criticism from many agencies who serve as
stewards of the exact resources at issue, not to mention consultants and organizations with on-
point expertise”); N. Am. Wild Sheep, 681 F.2d at 1182 (holding that criticism from
conservationists, biologists, two state agencies, and “other knowledgeable individuals”
represented “precisely the type of ‘controversial’ action for which an EIS must be prepared”);
Friends of the Earth, Inc. v. U.S. Army Corps of Eng’rs, 109 F. Supp. 2d 30, 43 (D.D.C. 2000)
(holding an agency project to be “genuinely and extremely controversial” where three federal
agencies, one state agency, and the public “all disputed the Corps evaluation,” and “the Corps’
own leadership recognized that” the project at issue “engendered considerable controversy”).
54
And third, although WildEarth and other organizations raised concerns about the climate change
methodologies—or lack thereof—employed by BLM, see AR12984–88, BLM considered
Plaintiffs’ suggested methodologies and explained why it did not use them. Those explanations
were not flawed.
Ultimately, BLM “is entrusted with the responsibility of considering the various modes
of scientific evaluation and theory and choosing the one appropriate for the given
circumstances.” Sierra Club v. U.S. Dep’t of Transp., 753 F.2d at 129. It was not “required to
accept every possible method of . . . analyzing data” here, id., and it was not required to “follow
[WildEarth’s] comments slavishly—it just [had] to take them seriously,” Citizens Against
Burlington, Inc. v. Busey, 938 F.2d 190, 201 (D.C. Cir. 1991). Because BLM “considered the
various methodological challenges raised by the interested parties and addressed their concerns
appropriately,” and because Plaintiffs did not otherwise identify serious flaws in BLM’s
methods, the Wyoming Lease Sales’ environmental effects were not “highly controversial.”
Nat’l Parks Conservation Ass’n, 311 F. Supp. 3d at 365.
b. The Effects of Leasing are Not Highly Uncertain
Second, Plaintiffs claim that the Wyoming Lease Sales’ effects were “highly uncertain or
involve[d] unique or unknown risks,” such that an EIS was necessary. 40 C.F.R. §
1508.27(b)(5). As Defendants point out, case law, including the case cited by Plaintiffs, suggest
that this factor is implicated when an action involves new science, or when an action’s impact on
a species is unknown. See, e.g., Anderson v. Evans, 371 F.3d 475, 492 (9th Cir. 2004) (holding
that the impact of first ever whale hunt on local whale population and ecosystem was highly
uncertain); Found. On Econ. Trends v. Heckler, 756 F.2d 143, 153 (D.C. Cir. 1985) (holding that
the impact of dispersing genetically altered organisms was highly uncertain); Humane Soc’y of
55
U.S. v. U.S. Dep’t of Commerce, 432 F. Supp. 2d 4, 8–9, 20–21 (D.D.C. 2006) (holding that the
impact of first ever “harassing” studies of endangered sea lion populations was highly uncertain).
Those circumstances are not present here. Defendants correctly note that “oil and gas
leasing is commonplace in the mountain west,” and that the “uncertainties Plaintiffs point to
concerning quantity of GHG emissions . . . do not establish uncertainty as to the effect of GHG
emissions.” BLM Mem. at 32. The parties agree that oil and gas development on the Wyoming
Leases will produce GHG emissions. They agree that GHG emissions contribute to climate
change. Thus, while the parties debate the usefulness and accuracy of tools by which GHG
emissions and their precise environmental impacts may be measured, the risks of GHG emissions
are not “unique or unknown,” and the EAs adequately summarized those risks.
* * *
In summary, the challenged EAs failed to take a hard look at the climate change impacts
of oil and gas drilling because the EAs (1) failed to quantify and forecast drilling-related GHG
emissions; (2) failed to adequately consider GHG emissions from the downstream use of oil and
gas produced on the leased parcels; and (3) failed to compare those GHG emissions to state,
regional, and national GHG emissions forecasts, and other foreseeable regional and national
BLM projects. By asserting that these crucial environmental analyses are overly speculative at
the leasing stage and more appropriate for later, site-specific assessments, BLM risks relegating
the analyses to the “tyranny of small decisions.” Kern v. BLM, 284 F.3d 1062, 1078 (9th Cir.
2002) (quoting CEQ, Considering Cumulative Effects Under NEPA at 1 (Jan. 1997),
https://www.energy.gov/sites/prod/files/nepapub/nepa_documents/RedDont/G-CEQ-
ConsidCumulEffects.pdf); see also 40 C.F.R. § 1508.27(b)(7) (“Significance cannot be avoided
by . . . breaking [an action] down into small component parts.”). NEPA is intended to avoid that
56
outcome. Given the national, cumulative nature of climate change, considering each individual
drilling project in a vacuum deprives the agency and the public of the context necessary to
evaluate oil and gas drilling on federal land before irretrievably committing to that drilling. See
Grand Canyon Trust, 290 F.3d at 342.
Simply put, NEPA required more robust analyses of GHG emissions from oil and gas
drilling and downstream use. Accordingly, BLM’s EAs and FONSIs for the Wyoming Lease
Sales are inadequate. That said, the challenged EAs were not—at least at the time they were
issued—required to apply the social cost of carbon or global carbon budget protocols to quantify
the climate change impact of GHG emissions. Given these conclusions, the Court must
determine how to proceed.
3. Remedy
Plaintiffs ask this Court to, among other relief, “void the issued leases, and suspend and
enjoin BLM from any further leasing authorizations pending BLM’s full compliance with
NEPA.” Pls. Mem. at 38. Plaintiffs cite case law in this jurisdiction indicating that “vacating a
rule or action promulgated in violation of NEPA is the standard remedy.” Humane Soc’y of U.S.
v. Johanns, 520 F. Supp. 2d 8, 37 (D.D.C. 2007) (citing Am. Bioscience, Inc. v. Thompson, 269
F.3d 1077, 1084 (D.C. Cir. 2001)). However, this Court has discretion to leave the Wyoming
Leases in place while BLM attempts to cure the deficiencies raised. See Oglala Sioux Tribe v.
U.S. Nuclear Regulatory Comm’n, 896 F.3d 520, 538 (D.C. Cir. 2018). Ultimately, “[t]he
decision whether to vacate depends on ‘the seriousness of the order’s deficiencies (and thus the
extent of doubt whether the agency chose correctly) and the disruptive consequences of an
interim change that may itself be changed.’” Allied-Signal v. U.S. Nuclear Regulatory Comm’n,
988 F.2d 146, 150–51 (D.C. Cir. 1993) (quoting Int’l Union, United Mine Workers of Am. v.
57
Fed. Mine Safety & Health Admin., 920 F.2d 960, 967 (D.C. Cir. 1990)). “Put otherwise, this
Court must determine whether there is ‘at least a serious possibility that the [agency] will be able
to substantiate its decision on remand,’ and whether vacatur will lead to impermissibly disruptive
consequences in the interim.” Standing Rock Sioux Tribe v. U.S. Army Corps of Eng’rs, 282 F.
Supp. 3d 91, 97 (D.D.C. 2017) (citing Williston Basin Interstate Pipeline Co. v. FERC, 519 F.3d
497, 504 (D.C. Cir. 2008); Nat’l Parks Conservation Ass’n v. Jewell, 62 F. Supp. 3d 7, 20
(D.D.C. 2014)).
Allied-Signal dictates that remand is most appropriate here. Plaintiffs challenge only one
aspect of nine lease sales that otherwise complied with NEPA. BLM’s NEPA violation consists
merely of a failure to fully discuss the environmental effects of those lease sales; nothing in the
record indicates that on remand the agency will necessarily fail to justify its decisions to issue
EAs and FONSIs. Thus “though the disruptive consequences of vacatur might not be great,[ 35]
the probability that [BLM] will be able to justify retaining [its prior leasing decisions] is
sufficiently high that vacatur . . . is not appropriate.” Fox Television Stations, Inc. v. FCC, 280
F.3d 1027, 1049 (D.C. Cir. 2002) (citing U.S. Telecom Ass’n v. FBI, 276 F.3d 620, 627 (D.C.
35
Defendants argue that vacatur here would significantly disrupt both public and private
economic interests. See API Mem. at 43–44. Oil and gas leasing generates revenues for state
and local governments “through the bonus bids paid at lease auctions and annual rents collected
on leased parcels.” Id. at 43 (quoting AR3425). And, in reliance on BLM’s leasing decisions,
private oil and gas companies bought at least some of the Wyoming Leases and have spent time
and money exploring those leases. Id. at 44; Western Alliance Reply at 20. If the Court were to
vacate the Wyoming Leases, Wyoming and its local governments, according to API, would be
deprived of revenue streams from resource development, and the private leaseholders would
“lose the opportunity to seek BLM approval to explore for, and eventually produce, valuable
mineral deposits.” API Mem. at 43–44. Defendants, however, provide no empirical bases for
their assertions that vacatur would cause significant economic disruption. And as another court
in this jurisdiction recently stated, the risk of economic harm from procedural delay and
industrial inconvenience “is the nature of doing business, especially in an area fraught with
bureaucracy and litigation.” Standing Rock, 282 F. Supp. 3d at 104. The Court thus does not
deny vacatur here on the basis of alleged economic harm alone.
58
Cir. 2002)). Instead, the Court remands the EAs and FONSIs to BLM so that the agency may
address the deficiencies identified by the Court above. See Heartland Reg’l Med. Ctr. v.
Sebelius, 566 F.3d 193, 198 (D.C. Cir. 2009) (“When an agency may be able readily to cure a
defect in its explanation of a decision, the first factor in Allied-Signal counsels remand without
vacatur.” (citations omitted)); Standing Rock, 282 F. Supp. 3d at 109 (remanding a deficient EA
to the agency without vacating its decision “[i]n light of the ‘serious possibility’ that the [agency]
[would] be able to substantiate its prior conclusions”).
That said, BLM’s “lack of a reasoned explanation is a serious failing . . . because it leaves
the Court in doubt as to whether the agency chose correctly in making its” leasing decisions.
Standing Rock, 282 F. Supp. 3d at 98 (quoting AARP v. EEOC, 267 F. Supp. 3d 14, 37 (D.D.C.
2017)). To guard against the possibility that BLM did not choose correctly the first time around,
the Court enjoins BLM from issuing any APDs for the Wyoming Leases while the agency works
to substantiate its EAs and FONSIs. Until BLM sufficiently explains its conclusion that the
Wyoming Lease Sales did not significantly affect the environment, BLM may not authorize new
drilling on the leased parcels.
VI. CONCLUSION
BLM failed to take a “hard look” at GHG emissions from the Wyoming Lease Sales, and
therefore the EAs and FONSIs issued for those sales did not comply with NEPA. BLM must
supplement those documents, addressing the deficiencies identified by the Court above.
However, in light of the serious possibility that BLM may be able to substantiate the conclusions
drawn in its EAs and FONSIs, the Court declines to vacate the Wyoming Leases. That
determination does not excuse BLM from giving serious consideration to the Court’s concerns.
“Compliance with NEPA cannot be reduced to a bureaucratic formality, and the Court expects
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[BLM] not to treat remand as an exercise in filling out the proper paperwork post hac.” Standing
Rock, 282 F. Supp. 3d at 109. After BLM’s work on remand, Plaintiffs may again address
whether BLM fulfilled its NEPA obligations. The Court will retain jurisdiction over this matter
until those obligations are satisfied.
For the foregoing reasons, it is hereby ORDERED that:
1. Plaintiffs’ Motion for Summary Judgment (ECF No. 55) is GRANTED IN PART.
2. Defendants’ Motions for Summary Judgment (ECF Nos. 60–63) are DENIED.
3. The Institute’s Motion for Leave to File an Amicus Curiae Brief (ECF No. 71) is
DENIED.
It is FURTHER ORDERED that the nine EAs and FONSIs associated with the Wyoming Lease
Sales challenged in Plaintiffs’ complaint are REMANDED to BLM so that BLM may satisfy its
NEPA obligations in the manner described above. Until BLM supplements those documents, it
is ENJOINED from issuing APDs or otherwise authorizing new oil and gas drilling on the
Wyoming Leases. An order consistent with this Memorandum Opinion is separately and
contemporaneously issued.
Dated: March 19, 2019 RUDOLPH CONTRERAS
United States District Judge
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