Defendants Forest Service
1
and Defendants-Intervenors-Appellants Environmental Groups
2
appeal the district court’s order setting aside and permanently enjoining the Roadless Area Conservation Rule (“Roadless Rule”), which the Forest Service promulgated in 2001. In setting-aside the Roadless Rule, the district court held that the rule violated the Wilderness Act of 1964 (‘Wilderness Act”), 16 U.S.C. §§ 1131-36, and the National Environmental Policy Act of 1969 (“NEPA”), 42 U.S.C. §§ 4321-70.
See Wyoming v. U.S. Dep’t of Agric.,
On appeal, the Forest Service and the Environmental Groups ask us to hold that the Roadless Rule was not promulgated in violation of the Wilderness Act or NEPA. Furthermore, even if we were to conclude that the rule was promulgated in violation of federal law, they ask us to nevertheless reverse the district court’s order establishing a permanent nationwide injunction. Plaintiff-Appellee State of Wyoming and Intervenor-Appellee Colorado Mining Association (“CMA”) 4 ask us to affirm the district court order on the grounds that the rule does in fact violate the Wilderness Act and NEPA. In the event that we conclude that the Roadless Rule complies with the Wilderness Act and NEPA, they ask us to affirm on the alternate grounds that the rule was promulgated in violation of the Multiple-Use Sustained-Yield Act (“MUSYA”), 16 U.S.C. §§ 528-31, and also the National Forest Management Act (“NFMA”), 16 U.S.C. §§ 1600-14. Exercising jurisdiction pursuant to 28 U.S.C. § 1291, we REVERSE the district court’s order granting Plaintiffs declaratory relief and issuing a permanent injunction, and REMAND the case for the district court to vacate the permanent injunction.
I. BACKGROUND
Due to the complexity of this case, we initially offer an overview of the applicable statutory framework, the factual back *1221 ground of the Roadless Rule, and the procedural history.
A. Statutory Framework
The Forest Service currently manages over 191 million acres of National Forest System (“NFS”) land, including 155 national forests, 20 national grasslands, 8 land utilization projects, 20 research and experimental areas, and 33 “other areas.” 36 C.F.R. § 200.1. The Forest Service is responsible for managing the NFS under, inter alia, the Organic Administration Act of 1897 (“Organic Act”), 16 U.S.C. §§ 473-482, 551, MUSYA, and NFMA. On a general level, these statutes authorize the Forest Service to manage NFS lands for multiple uses. In managing the NFS, however, the Forest Service also must comply with the Wilderness Act and NEPA. These relevant statutes are briefly discussed in turn.
In 1897, Congress passed the Organic Act. 16 U.S.C. §§ 473-482, 551. The Act “established a limited multiple-use mandate for management of the National Forests,”
Wyoming,
More than sixty years later, in 1960, Congress enacted MUSYA. 16 U.S.C. §§ 528-31. MUSYA codified the multiple-use mandate first articulated in the Organic Act, directing the Forest Service to “administer the renewable surface resources of the national forests for multiple use and sustained yield,” including for the purposes of “outdoor recreation, range, timber, watershed, and wildlife and fish purposes.” Id. §§ 528, 529.
In 1964, Congress enacted the Wilderness Act, 16 U.S.C. §§ 1131-36, which “established a National Wilderness Preservation System to be composed of federally owned areas designated by Congress as ‘wilderness areas,’ ” id. § 1131. More specifically, the Act put in place a process under which Congress designates “wilderness areas,” id. § 1132, and established requirements for the management and protection of such areas, see id. § 1133 (listing the uses permitted in congressionally designated wilderness areas). In order to aid Congress in designating “wilderness,” the Act required the Forest Service to review “primitive” areas of the NFS to determine their “suitability or nonsuitability for preservation as wilderness.” Id. § 1132(b).
In 1972, the Forest Service completed the Roadless Area Review and Evaluation project (RARE I), which resulted in a nationwide inventory of NFS areas — totaling approximately 56 million acres — -that the agency deemed to be suitable for “wilderness” designation pursuant to the Wilderness Act. However, the RARE I inventory was abandoned following a successful judicial challenge under NEPA.
See Wyo. Outdoor Coordinating Council v. Butz,
In 1976, Congress passed NFMA. 16 U.S.C. §§ 1600-14. The Act, “which is primarily concerned with planning,”
Utah
*1222
Envtl. Cong. v. Richmond,
From 1977 until 1979, the Forest Service embarked on a second Roadless Area Review and Evaluation project (RARE II), which again created a national inventory of roadless areas that were potentially suitable for “wilderness” designation under the Wilderness Act.
See, e.g., California v. Block,
B. History of the Roadless Rule
The RARE II undertaking, completed in 1979, produced a nationwide inventory of roadless areas that the Forest Service found worthy of some level of protection. Over the next two decades, however, the Forest Service began permitting road construction to occur in some of those inventoried roadless areas (“IRAs”) on a site-specific basis. 66 Fed.Reg. 3244, 3246 (Jan. 12, 2001);
see also Kootenai Tribe of Idaho v. Veneman,
In the late 1990s, the Forest Service began to reevaluate its road-management policy in response to changes in public opinion, shifts in resource demands, budget constraints regarding the management of the NFS road system, and an increase in scientific knowledge regarding the effects that roads have on NFS lands. See 63 Fed.Reg. 4350, 4350 (Jan. 28, 1998). The agency published an advance notice of proposed rulemaking in January of 1998, which solicited public comment on future regulation and protection of IRAs. Id. The Forest Service thereafter adopted an eighteen-month moratorium on road construction in most IRAs — the “Interim Roadless Rule” — which ran from March 1999 through August 2000. 64 Fed.Reg. 7290, 7290 (Feb. 12, 1999). The Interim Road-less Rule “temporarily suspended] decisionmaking regarding road construction and reconstruction in many unroaded areas within the National Forest System,” in order to “retain resource management options in those unroaded areas subject to suspension from the potentially adverse effects associated with road construction, *1223 while the Forest Service develop[ed] a revised road management policy.” Id.
While the Interim Roadless Rule was in effect, in October of 1999, President William J. Clinton “direct[ed] the Forest Service to develop ... regulations to provide appropriate long-term protection for most or all of these currently inventoried ‘road-less’ areas” in the NFS. Aplt.App. at 1524 (Memorandum from President William Clinton to the Secretary of Agriculture (Oct. 13, 1999)). On October 13, 1999, in response to President Clinton’s directive, as well as public comments received on the 1998 advanced notice of proposed rulemaking and the Interim Roadless Rule, the Forest Service published a notice of intent (“NOI”) to prepare an environmental impact statement (“EIS”) in accordance with NEPA, and to “initiat[e] a public rulemaking process to propose the protection of remaining roadless areas within the National Forest System.” 64 Fed.Reg. 56,-306, 56,306 (Oct. 19, 1999). The NOI announced the agency’s intent to promulgate a two-part rule for protection of roadless areas: (1) “[P]art one would immediately restrict certain activities, such as road construction, in unroaded portions of inventoried roadless areas, as previously identified in RARE II and existing forest plan inventories”; and (2) “[p]art two would establish national direction for managing [IRAs], and for determining whether and to what extent similar protections should be extended to uninventoried roadless areas,” a process that “would be implemented at the forest plan level through the plan amendment and NEPA process.” Id. at 56,307.
The NOI also initiated a sixty-day “scoping period,” during which the agency sought public comment on the nature and scope of the issues and alternatives to be analyzed during the NEPA process. Id. During the sixty-day scoping period, the Forest Service received more than 517,000 comments in response to the NOI, held 187 meetings around the nation (including several in Wyoming) attended by approximately 16,000 citizens, and launched a Roadless Area Conservation website (road-less.fs.fed.us) to provide information about the rulemaking. 66 Fed.Reg. at 3248; 64 Fed.Reg. 67,822, 67,825-29 (Dec. 3, 1999). Despite several requests, the Forest Service declined to extend the scoping period beyond the initial sixty days.
On May 10, 2000, the Forest Service issued a draft EIS (“DEIS”) and proposed Roadless Rule. See generally 65 Fed.Reg. 30,276 (May 10, 2000); ApltApp. at 425 (Draft Environmental Impact Statement, dated May 2000) [hereinafter DEIS]. The DEIS identified 54.3 million acres of IRAs that were subject to the proposed rule. 65 Fed.Reg. at 30,276. The stated purposes of the proposed rule were “to immediately stop activities that have the greatest likelihood of degrading desirable characteristics of inventoried roadless areas,” and “to ensure that ecological and social characteristics of inventoried roadless and other unroaded areas are identified and considered through local forest planning efforts.” DEIS at S — 4; see also id. at 1-12 (stating that the first objective of the rule was to “[p]revent activities that can most directly threaten [IRAs] by implementing national prohibitions against road construction and reconstruction”).
The proposed rule was two-fold, composed of (1) a “Prohibition Rule,” which banned road construction and reconstructions in IRAs, and (2) a “Procedural Rule,” which required forest managers to identify additional roadless areas during the forest planning process and determine whether such areas warranted protection under individual forest plans. See 65 Fed.Reg. at 30,288 (to be codified at 36 C.F.R. §§ 294.12, 294.13). The Forest Service *1224 considered four alternatives to the Prohibition Rule in detail in the DEIS — a “no-action” alternative and three alternatives prohibiting road building and timber harvest to varying degrees. See id. at 2-3 to 2-6. Specifically, the four prohibition alternatives analyzed were: (1) Alternative 1 — the “no action” alternative, id. at 2-4; (2) Alternative 2 — a prohibition on “road construction and reconstruction within unroaded portions of [IRAs],” id. at 2^1 to 2-5; (3) Alternative 3 — a prohibition on “road construction, reconstruction, and timber harvest except for stewardship purposes within unroaded portions of [IRAs],” id. at 2-5; and (4) Alternative 4 — a prohibition on “road construction, reconstruction[,] and all timber harvest within unroaded portions of [IRAs],” id. at 2-6. In the DEIS, the Forest Service designated Alternative 2 as the preferred alternative for the prohibition rule. Id. at 2-13. 6
Other alternatives to the Prohibition Rule were addressed by the Forest Service, such as allowing more (rather than less) road building and development, but those alternatives were eliminated from detailed environmental analysis because they were inconsistent with the purpose of protecting IRAs or for other reasons.
Id.
at 2-15 to 2-20. The Forest Service provided sixty-nine days for public comment on the DEIS and proposed rule,
In November 2000, the Forest Service issued a final EIS (“FEIS”). 65 Fed.Reg. 69,512 (Nov. 17, 2000); Aplt.App. at 520 (Final Environmental Impact Statement, dated Nov. 9, 2009) [hereinafter FEIS]. The FEIS included several changes to the proposed action that were not included in the DEIS. First, it increased the total acreage of IRAs subject to the Prohibition Rule from 54.3 million acres to 58.5 million acres. FEIS at 2-23. The revised figure included 4.2 million acres of IRAs not identified in the DEIS or proposed rule. Id. Second, it made the rule applicable to both the “unroaded” and “roaded” portions of IRAs; that is, the Roadless Rule would “now apply to the entire area within the boundaries of an [IRA],” whereas the 2.8 million acres of “roaded” IRAs were not subject to the prohibitions in the proposed rule as it was described in the DEIS. Id. 7 Third, the FEIS changed the preferred alternative — previously identified as Alternative 2, which prohibited road construction and reconstruction in IRAs — to Alternative 3, which, as described in the FEIS, prohibited “[r]oad construction, reconstruction (including temporary construction) and timber harvest except for stewardship purposes” in IRAs, subject to a few limited exceptions. FEIS at 2-13 to 2-14 (emphasis added). Fourth, the FEIS eliminated the procedural aspect of the rule, leaving only the Prohibition Rule, due to the Forest Service’s decision to incorporate such procedures into a separate and distinct set of forest planning regulations. See FEIS at 1-16 (stating that “the Forest Service determined that the procedures contemplated in the [proposed] Roadless Rule should be an explicit part of the plan revision process, and addressed them at 36 *1225 CFR 219.9(b)(8) of the final Planning Regulations”).
Following the issuance of the FEIS, the Forest Service received additional public comments on the FEIS and the modified preferred alternative. 66 Fed.Reg. at 3248. The comments submitted in response to the FEIS “were considered by the agency in the development of the final rule” and were admitted into the administrative record. Id.
On January 12, 2001, the Forest Service issued the final Roadless Rule and the Record of Decision on the rule.
The final Roadless Rule was applicable to the 58.5 million acres of IRAs identified in the FEIS, which amounts to approximately one-third of all NFS lands and approximately 2% of the land base of the continental United States. 66 Fed.Reg. at 3245. As specific to Wyoming, “[t]he Roadless Rule affects 3.25 million acres (or 35%) of the 9.2 million acres of National Forest System land in [the state].”
Wyoming,
C. Procedural History
This is not the first instance in which this court has considered a challenge to the Roadless Rule brought by Wyoming.
9
*1226
On May 18, 2001, shortly after the Road-less Rule was promulgated, Wyoming filed its first complaint in the United States District Court for the District of Wyoming challenging the legality of the Roadless Rule under several federal environmental statutes, including NEPA, the Wilderness Act, the Wyoming Wilderness Act of 1984, NFMA, and MUSYA. A number of environmental organizations intervened on behalf of the Forest Service, in defense of the rule.
10
On July 14, 2003, the Wyoming district court ruled that the Roadless Rule was promulgated in violation of NEPA and the Wilderness Act, and therefore permanently enjoined enforcement of the rule.
Wyoming v. U.S. Dep’t of Agric.,
During the pendency of that appeal — in May of 2005 — the Forest Service adopted the State Petitions Rule, which superseded the Roadless Rule.
See
State Petitions for Inventoried Roadless Area Management, 70 Fed.Reg. 25,654 (May 13, 2005) (to be codified at 36 C.F.R. pt. 294). Because the Roadless Rule had been superseded, this court dismissed the appeal as moot, vacated the district court’s July 14, 2003, decision, and remanded the case to the district court to dismiss without prejudice.
Wyoming v. U.S. Dep’t of Agric.,
Subsequently, several states and environmental groups challenged the Forest Service’s State Petitions Rule in the United States District Court for the Northern District of California. On October 11, 2006, a district court judge of that court set aside the State Petitions Rule for violating NEPA and the Endangered Species Act of 1973, 16 U.S.C. §§ 1531-44, and reinstated the Roadless Rule, despite the fact that the Wyoming district court had already found that the rule violated federal law.
California ex rel. Lockyer v. U.S. Dep’t of Agric.,
After the Roadless Rule was reinstated by the California district court, Wyoming brought a renewed challenge to the rule in the District of Wyoming, asserting violations of the Wilderness Act, NEPA, MUS-YA, and NFMA. On August 12, 2008, the Wyoming district court ruled — for the second time — that the Roadless Rule was promulgated in violation of the Wilderness Act and NEPA, and issued a permanent, nationwide injunction.
Wyoming v. U.S. Dep’t of Agric.,
II. DISCUSSION
A. Standard of Review
Because NEPA, NFMA, MUSYA, and the Wilderness Act do not provide a private right of action, we review the Forest Service’s promulgation of the Roadless Rule as “final agency action” under the Administrative Procedure Act (“APA”), 5 U.S.C. §§ 551-59.
E.g., Forest Guardians v. U.S. Forest Serv.,
In conducting our review, “we must determine whether the [agency]: (1) acted within the scope of [its] authority, (2) complied with prescribed procedures, and (3) took action that was neither arbitrary and capricious, nor an abuse of discretion.”
Forest Guardians v. U.S. Fish & Wildlife Serv.,
We review the district court’s order of injunctive relief for abuse of discretion.
FTC v. Accusearch Inc.,
B. Wilderness Act Claim
Wyoming’s Wilderness Act claim asserts that the Roadless Rule constitutes a de facto designation of “wilderness” in contravention of the process established by Congress in the Wilderness Act of 1964. The district court agreed, holding that the “Forest Service, through the promulgation of the Roadless Rule, designated 58.5 million acres of National Forest land as a de facto wilderness area in violation of the Wilderness Act,” and therefore the rule was “promulgated in excess of [the] Forest Service’s statutory jurisdiction and authority.”
Wyoming,
1. Overview of Wilderness Act
Congress passed the Wilderness Act in 1964, 16 U.S.C. §§ 1131-36, for the purpose of “securing] for the American people of present and future generations the benefits of an enduring resource of wilderness.” Id. § 1131(a). The Wilderness Act established the National Wilderness Preservation System, which was “to be composed of federally owned areas designated by Congress as ‘wilderness areas.’” Id. Congress immediately designated certain areas as “wilderness areas” in the Act. See id. § 1132(a) (“All areas within the national forests classified ... by the Secretary of *1228 Agriculture or the Chief of the Forest Service as ‘wilderness’, ‘wild’, or ‘canoe’ are hereby designated as wilderness areas.”). The Wilderness Act also established a process by which NFS lands could be designated as “wilderness areas” in the future. Id. § 1132(b). Under this process for designating “wilderness” in the future, the Secretary of Agriculture determines which NFS lands are suitable for preservation as wilderness and reports those findings to the President, who then submits recommendations to Congress as to which NFS lands should be regulated as wilderness areas under the Act. Id. Such lands actually become “wilderness areas” protected by the provisions of the Wilderness Act only if Congress enacts legislation to that effect. Id. Indeed, Congress explicitly stated that “no Federal lands shall be designated as ‘wilderness areas’ except as provided for in [the Wilderness Act] or by a subsequent Act.” Id. § 1131(a).
The Act defines “wilderness” as “an area where the earth and its community of life are untrammeled by man, where man himself is a visitor who does not remain,” as well as “an area of undeveloped Federal land retaining its primeval character and influence, without permanent improvements or human habitation.” Id. § 1131(c). Congress further defined “wilderness” as an area that
(1) generally appears to have been affected primarily by the forces of nature, with the imprint of man’s work substantially unnoticeable; (2) has outstanding opportunities for solitude or a primitive and unconfined type of recreation; (3) has at least five thousand acres of land or is of sufficient size as to make practicable its preservation and use in an unimpaired condition; and (4) may also contain ecological, geological, or other features of scientific, educational, scenic, or historical value.
Id.
Areas designated as “wilderness areas” by Congress under the Act must be maintained so as to “preserv[e] the wilderness character of the area” and “shall be devoted to the public purposes of recreational, scenic, scientific, educational, conservation, and historical use,” unless an exception applies. Id. § 1133(b). In order to preserve the character of areas designated by Congress as “wilderness,” the Act prohibits a wide array of uses within such areas:
[T]here shall be no commercial enterprise and no permanent road within any wilderness area designated by this chapter and, except as necessary to meet minimum requirements for the administration of the area for the purpose of this chapter (including measures required in emergencies involving the health and safety of persons within the area), there shall be no temporary road, no use of motor vehicles, motorized equipment or motorboats, no landing of aircraft, no other form of mechanical transport, and no structure or installation within any such area.
Id. § 1133(c).
The Act includes seven “special provisions,” which serve as exceptions to the general use prohibitions found in § 1133(c). See id. § 1133(d)(l)-(7). These “special provisions” allow, among other things, for (1) “measures ... [for] control of fire, insects, and diseases, subject to such conditions as the Secretary deems desirable”; (2) “prospecting” and activities carried out “for the purpose of gathering information about mineral or other resources, if such activity is carried on in a manner compatible with the preservation of the wilderness environment”; (3) certain development of water resources, if approved by the President; (4) *1229 “grazing of livestock,” but only if established before September 1964; and (5) “[c]ommercial services ... to the extent necessary for activities which are proper for realizing the recreational or other wilderness purposes of the areas.” Id. § 1133(d)(1), (2), (4), & (5). 12
Lastly, the Wilderness Act establishes that its provisions are “declared to be within and supplemental to the purposes for which national forests ... are established and administered,” id. § 1133(a), and therefore Congress made clear that “[njothing in [the Wilderness Act] shall be deemed to be in interference with the purpose for which national forests are established as set forth in the [Organic Act] (30 Stat. 11), and [MUSYA] (74 Stat. 215).” Id. § 1133(a)(1).
2. Discussion
As stated by the district court, the narrow issue presented by this claim is “whether the Forest Service has usurped Congresses] power regarding access to, and management of, public lands by a de facto designation of ‘wilderness’ in violation of the Wilderness Act of 1964.”
Wyoming,
On appeal, the Forest Service first argues that the Wilderness Act did not repeal or in any way limit its broad authority to regulate NFS lands for conservation purposes, including “wilderness,” and therefore it was authorized to promulgate the Roadless Rule. In the alternative, even assuming, arguendo, that the Wilderness Act did repeal or limit the Forest Service’s authority to regulate “wilderness areas” by administrative rule, the Forest Service and the Environmental Groups argue that the IRAs governed by the Roadless Rule are not de facto wilderness areas. Therefore, they assert that the Roadless Rule was a valid exercise of the authority granted under the Organic Act and MUSYA “to manage NFS lands for an array of uses or combinations of use, including conservation uses that fall short of statutory ‘wilderness’ designations.” Forest Serv. Opening Br. at 32 (emphasis added). We agree with the latter argument — viz., that the Forest Service did not usurp congressional authority because the Roadless Rule did not establish de facto wilderness areas— and, therefore, conclude that the district court erred in holding otherwise. Accordingly, we need not address the first argument advanced by the Forest Service regarding whether it retains the authority under the Organic Act and MUSYA to regulate de facto wilderness areas by administrative rule.
a. Roadless Rule Did Not Establish De Facto Wilderness Areas
The district court’s conclusion that the Roadless Rule created de facto wilderness in violation of the Wilderness Act was based largely on its finding that “wilderness areas” governed by the Wilderness Act and IRAs governed by the Roadless Rule “are essentially the same,” and that “[i]n fact, uses in [IRAs] are even more restricted than those permitted in congressionally designated wilderness areas.”
Wyoming,
As a general matter, the Roadless Rule restricts only two activities — road construction and commercial timber harvesting, unless an exception applies. See 66 Fed.Reg. at 3272-73 (to be codified at 36 C.F.R. §§ 294.12-.13). On the other hand, although the Wilderness Act likewise prohibits permanent and temporary roads and commercial logging, it additionally prohibits all “commercial enterprise,” “motor vehicles, motorized equipment or motorboats,” all “form[s] of mechanical transport,” and any “structure or installation,” unless an exception applies. 16 U.S.C. § 1133(c). This rudimentary comparison of the general use prohibitions in IRAs and wilderness areas demonstrates that they are not the same; the uses prohibited in wilderness areas under the Wilderness Act are greater in number and scope than those prohibited in IRAs under the Roadless Rule.
We acknowledge that the Wilderness Act and Roadless Rule do in fact overlap in coverage in many ways. However, the issue we are to consider is whether the IRAs governed by the Roadless Rule are de facto wilderness areas; that is, whether the Roadless Rule essentially mirrors the Wilderness Act by a different label. A closer examination of the precise differences between IRAs and wilderness areas further demonstrates that the Roadless Rule does not establish de facto wilderness. First, although the Wilderness Act prohibits permanent structures and installations, the Roadless Rule does not prohibit the construction of permanent or temporary structures or installations. Compare 16 U.S.C. § 1133(c), with 66 Fed.Reg. at 3272-73 (to be codified at 36 C.F.R. §§ 294.10-14). Therefore, structures and installations that can be erected without the construction of a new road — for example, through the use of an existing road— are permitted in IRAs, but not in wilderness areas.
Second, the Wilderness Act imposes significantly more stringent prohibitions on recreational activities. Under the Wilderness Act, any “use of motor vehicles, motorized equipment or motorboats, ... landing of aircraft, ... [or] other form of mechanical transport” is prohibited. 16 U.S.C. § 1133(c). On the other hand, the Roadless Rule contains no prohibitions on the use of motorized vehicles or equipment, boats or aircraft, or other forms of mechanical transport. Therefore, many recreational uses allowed to continue un *1231 der the Roadless Rule — such as off-road vehicle use, biking, snowmobiling, and other motorized and mechanical activities— would be prohibited under the Wilderness Act. See, e.g., 66 Fed.Reg. at 3245 (stating that “unlike Wilderness,” the Roadless Rule permits the “use of mountain bikes, and other mechanized means of travel”); id. at 3249 (“The Roadless [Rule], unlike the establishment of wilderness areas, will allow a multitude of activities including motorized uses....”); id. at 3267 (“[IRAs] provide a remote recreation experience without the activity restrictions of Wilderness (for example, off-highway vehicle use and mountain biking).”). 14
Third, the Wilderness Act is more restrictive in terms of road maintenance, road construction, and use of existing roads. The Wilderness Act prohibits any “permanent road” or any “temporary road,” and road maintenance activities, subject to limited exceptions, 15 and prohibits any use of motor vehicles. 16 U.S.C. § 1133(c); 36 C.F.R. § 293.6. On the other hand, the Roadless Rule allows all existing classified roads — defined as roads “wholly or partially within or adjacent to [NFS] lands that [are] determined to be needed for long-term motor vehicle access, including State roads, county roads, privately owned roads, National Forest System roads, and other roads authorized by the Forest Service,” 66 Fed.Reg. at 3272 (to be codified at 36 C.F.R. § 294.11) — to be maintained. Id. at 3273 (to be codified at 36 C.F.R. § 294.12(c)). 16 Therefore, unlike the Wilderness Act, the Roadless Rule permits unlimited maintenance of all existing roads and does not prohibit the use of motorized vehicles or other motorized transportation on such existing roads.
Furthermore, the Roadless Rule provides broader exceptions for when new road construction or reconstruction can occur. For example, unlike in wilderness areas, “a road may be constructed or reconstructed in an [IRA] ... as provided for by statute or treaty,” id. at 3272 (to be codified at 36 C.F.R. § 294.12(b)(3)); 17 when “needed to conduct a response action under the Comprehensive Environmental Response, Compensation, and Liability Act (CERCLA) or to conduct a natural re *1232 source restoration action under CERCLA, [§ ] 311 of the Clean Water Act, or the Oil Pollution Act,” id. (to be codified at 36 C.F.R. § 294.12(b)(2)); or when the “Secretary of Agriculture determines that a Federal Aid Highway project ... is in the public interest or is consistent with the purposes for which the land was reserved or acquired,” id. (to be codified at 36 C.F.R. § 294.12(b)(6)), among other instances. The Wilderness Act includes no exceptions of this kind to its prohibition of temporary and permanent roads.
Fourth, the Roadless Rule is less restrictive in terms of “grazing.” Under the Wilderness Act’s mandate that “there shall be no commercial enterprise ... within any wilderness area,” 16 U.S.C. § 1133(c), commercial livestock grazing is prohibited. The Act includes a grandfather clause that permits “the grazing of livestock ... [that was] established prior to September 3, 1964,”
id.
§ 1133(d)(4)(2), more than four decades ago, but otherwise completely bars such activity. By contrast, the Road-less Rule does not explicitly prohibit
any
type of “commercial enterprise,” with the exception of commercial logging, and therefore permits commercial grazing within IRAs. The district court found this distinction meaningless because “one could not meaningfully set cattle out to pasture in a roadless area with no way of rounding those cattle back up or tracking them in and out of the forest allotment,” unless a new road was constructed.
Wyoming,
Fifth, the Roadless Rule allows for mineral development to a greater extent than does the Wilderness Act. Although the Wilderness Act initially permitted mineral development under United States mining laws, wilderness areas governed by the Act are now closed to mineral-development activities. 16 U.S.C. § 1133(d)(3).
18
On the other hand, the Roadless Rule imposes no general prohibition on mining or mineral-development activities, other than the limitations imposed through the road-building prohibition. Therefore, “leasing activities not dependent on road construction, such as directional (slant) drilling and underground development,” and mineral-leasing activities that could be carried out through utilization of existing roads, “would not be affected by the prohibition.” 66 Fed.Reg. at 3265;
see also Wilderness Workshop,
The exceptions to the Roadless Rule’s road-building prohibition would also permit new road construction or reconstruction for mineral development in certain situations. Under the exception for existing mineral leases, road construction is permitted “in conjunction with the continuation, extension, or renewal of a mineral lease on lands that are under lease by the Secretary of the Interior as of January 12, 2001[,] or for a new lease issued immediately upon expiration of an existing lease.” 66 Fed.Reg. at 3272-73 (to be codified at 36 C.F.R. § 294.12(b)(7)). This exception “extends indefinitely the timeframe for which roads can be constructed on areas currently under lease.” Id. at 3265-66. In addition, under the exception permitting road construction “as provided for by statute or treaty,” id. at 3272 (to be codified at 36 C.F.R. § 294.12(b)(3)), “[reasonable access to conduct exploration and development of valid claims for locatable minerals (metallic and nonmetallic minerals subject to appropriation under the General Mining Law of 1872)” would not be prohibited under the Roadless Rule. Id. at 3268. “Reasonable access” could “involve some level of road construction that, depending on the stage of exploration or development, could range from helicopters, temporary or unimproved roads, more permanent, improved roads, or nonmotorized transport.” Id. In sum, the Roadless Rule is less restrictive than the Wilderness Act in regard to mineral development.
These distinctions clearly demonstrate that wilderness areas governed by the Wilderness Act and IRAs governed by the Roadless Rule are not only distinct, but that the Wilderness Act is more restrictive and prohibitive than the Roadless Rule. Accordingly, we conclude that the IRAs governed by the Roadless Rule are not de facto administrative wilderness areas; therefore, the district court erred by holding otherwise.
In reaching the contrary conclusion that “uses in [IRAs] are even more restricted than those permitted in congressionally designated wilderness areas,”
Wyoming,
a road could be constructed in a wilderness area to “control fire, insects, and diseases,” whereas a road could only be constructed in a roadless area in the “case of an imminent flood, fire, or other catastrophic event that, without intervention, would cause the loss of life or property.” Compare 16 U.S.C. § 1133(d)(1) ivith 36 C.F.R. § 294.12(b)(1).
Id. at 1349-50 (emphasis added). However, this distinction alone, when viewed in light of the numerous distinctions discussed above, does not demonstrate that the uses in IRAs are overall more restricted than those permitted in wilderness areas. 19 The district court’s reliance on this *1234 single distinction in concluding that the Roadless Rule is more restrictive than the Wilderness Act was erroneous.
In sum, we conclude that the Roadless Rule did not designate de facto administrative wilderness areas in contravention of the procedures set out in the Wilderness Act.
b. Roadless Rule Was Promulgated Pursuant to Broad Authority Granted in Organic Act and MUSYA
Because we conclude that the Roadless Rule did not establish de facto wilderness areas in contravention of the procedures established in the Wilderness Act, and therefore did not usurp congressional authority under the Act, the only remaining issue is whether the Forest Service otherwise acted within its statutory authority in promulgating the Roadless Rule. We conclude that the Forest Service acted within the authority that Congress granted to it under the Organic Act and MUSYA.
As stated above, the Organic Act of 1897 empowers the Secretary of Agriculture, through the Forest Service, to “make provisions for the protection against destruction by fire and depredations upon the public forests and national forests” and “make such rules and regulations ... to regulate [the national forests’] occupancy and use and to preserve the forests thereon from destruction.” 16 U.S.C. § 551. The Organic Act gives the Forest Service broad discretion to regulate the national forests, including for conservation purposes.
See United States v. Grimaud,
The broad rulemaking authority granted the Forest Service under the Organic Act — to regulate “occupancy and use” of NFS lands and “to preserve the forests thereon from destruction” (for example, from road construction and logging) — is alone sufficient to support the Forest Service’s promulgation of the Roadless Rule.
See Kootenai Tribe,
The Forest Service was further authorized to manage NFS lands through MUS-YA, which reaffirmed the Forest Service’s authority to manage national forests for a wide range of uses. Specifically, MUSYA directs the Forest Service to manage the national forests for “multiple uses,” including “outdoor recreation, range, timber, watershed, and wildlife and fish purposes.” 16 U.S.C. § 528. Congress directed the Forest Service to “mak[e] the most judicious use of the land for some or all of these resources,” and acknowledged “that some land will be used for less than all of the resources.” Id. § 531(a). Furthermore, MUSYA states that “establishment and maintenance of areas of wilderness are consistent with the purposes and provisions of [the Act].” Id. § 529. Congress expressly indicated that MUSYA was “to be supplemental to, but not in derogation of,” the Organic Act. Id. § 528.
As with the Organic Act, the provisions of MUSYA give the Forest Service broad discretion to regulate NFS lands for a wide variety of purposes.
See Perkins v. Bergland,
*1236 C. NEPA Claims
Wyoming asserts that the Forest Service, in promulgating the Roadless Rule, violated NEPA in seven ways. Specifically, it argues that the Forest Service failed to comply with the NEPA requirements regarding: (1) scoping, (2) cooperating-agency status, (3) consideration of a reasonable range of alternatives in the EIS, (4) consideration of the cumulative impacts of the proposed action in the EIS, (5) preparation of a supplemental impact statement, (6) inclusion of site-specific analysis in the EIS, and (7) an objective “hard look” at the environmental consequences of agency action, by instead predetermining the outcome of the NEPA process. The district court ruled in favor of Wyoming on all its NEPA claims except for two — the site-specific analysis claim, on which it found in favor of the Forest Service,
Wyoming,
1. Overview of NEPA
Congress enacted NEPA in 1969. 42 U.S.C. §§ 4321-70. The statute, which has been described as “[t]he centerpiece of environmental regulation in the United States,”
Forest Guardians,
NEPA has two aims: “First, it places upon an agency the obligation to consider every significant aspect of the environmental impact of a proposed action. Second, it ensures that the agency will inform the public that it has indeed consid
*1237
ered environmental concerns in its decisionmaking process.”
Forest Guardians,
Under NEPA, before a federal agency “undertakes a ‘major Federal aetion[ ] significantly affecting the quality of the human environment,’ it must prepare an environmental impact statement (‘EIS’) that details, among other things, the environmental impacts of the proposed action, any adverse environmental effects that would occur as a result, and alternatives to the proposed action.”
Greater Yellowstone Coal. v. Flowers,
Initially, an agency announces its intent to study a proposed action through a process called scoping, during which the agency solicits comments and input from the public and other state and federal agencies with the goal of identifying specific issues to be addressed and studied. 40 C.F.R. § 1501.7. After assessing the input from the scoping process, the government then prepares a draft Environmental Impact Statement (DEIS), id. § 1502.9(a), which is then presented to the public and other government agencies for notice and comment. Id. § 1503.1(a). After evaluating the feedback received during the notice and comment process, the agency prepares a FEIS. Id. § 1502.9(b). If after preparing either a DEIS or FEIS, the proposed action substantially changes in a way “relevant to environmental concerns,” or if new information comes to light about environmental impacts, an agency must prepare a supplemental EIS (SEIS). Id. § 1502.9(c)(1).
Citizens’ Comm. to Save Our Canyons v. U.S. Forest Serv.,
(i) the environmental impact of the proposed action, (ii) any adverse environmental effects which cannot be avoided should the proposal be implemented, (iii) alternatives to the proposed action, (iv) the relationship between local short-term uses of man’s environment and the maintenance and enhancement of long-term productivity, and (v) any irreversible and irretrievable commitments of resources which would be involved in the proposed action should it be implemented.
42 U.S.C. § 4332(2)(C). After completing the NEPA process and making a final decision on the proposed action, the agency “then must publish a record of its decision, showing how its final decision-making process incorporated the [EIS’s] findings.”
BioDiversity Conservation Alliance v. Bureau of Land Mgmt.,
2. Scoping
Wyoming’s first claim under NEPA alleges that the scoping period of the Forest Service was inadequate. Specifically, Wyoming argues that the Forest Service acted arbitrarily and capriciously when it failed to (a) extend the scoping period beyond the initial sixty days allotted, and (b) provide during the scoping period detailed maps of the IRAs affected by the Roadless Rule. The district court held that the Forest Service’s failure to extend the scoping period and provide maps accurately depicting the areas covered by the rule was arbitrary and capricious in that it deprived Wyoming of the opportunity to “meaningfully ‘participate’ in determining the scope and significant issues to be analyzed in the EIS.”
Wyoming,
“Scoping” is the initial phase of the overall EIS process under NEPA.
Citizens’ Comm, to Save Our Canyons,
In addition, the agency “may ... [s]et time limits” for the scoping process and “[h]old an early scoping meeting or meetings.” Id. § 1501.7(b)(2), (4) (emphasis added). In regard to setting time limits for the scoping process, the only requirement is that such limits comply with 40 C.F.R. § 1501.8. Id. § 1501.7(b)(1). Section 1501.8 does not “prescribe! ] universal time limits for the entire NEPA process,” but instead merely authorizes agencies to set time limits — including times limits on the scoping process — that are “appropriate to individual actions” and “are consistent with the purposes of NEPA and other essential considerations of national policy.” Id. § 1501.8. More specifically, the principal regulations governing scoping — i.e., the CEQ Regulations — do not set minimum time limits for the scoping period and do not require an agency to extend or reopen the scoping period; those determinations are generally left to the agency’s discretion.
In accordance with 40 C.F.R. § 1501.7, the Forest Service published a NOI commencing the scoping period for the Road-less Rule on October 19, 1999.
Turning to the Forest Service’s refusal to extend the scoping period, we conclude that it was not unreasonable— that is, not arbitrary, capricious, or an abuse of discretion — to limit the period to sixty days and to decline to extend it any further. As stated above, there is no requirement mandating a minimum number of days the scoping period must remain open or requiring the Forest Service to extend or reopen the scoping period. We have found that “[a]bsent constitutional constraints or extremely compelling circumstances the administrative agencies should be free to fashion their own rules of procedure and methods of inquiry permitting them to discharge their multitudinous duties.”
Phillips Petroleum Co. v. U.S. EPA,
Nothing in NEPA or the CEQ Regulations (or the APA for that matter) required the Forest Service to extend the scoping period beyond the initial sixty-day allotment; Wyoming itself acknowledges this.
See
Wyo. Br. at 16 (“Wyoming agrees that the NEPA scoping regulations do not specifically require ... extensions of the scoping period upon request.”). To impose upon the agency more stringent requirements than the legal framework requires, absent “extremely compelling circumstances,” would violate the well-settled principle articulated by the Supreme Court in
Vermont Yankee
“that the formulation of procedure is to be basically left within the discretion of the agencies to which Congress has confined the responsibility for substantive judgments.”
Phillips Petroleum,
The district court likewise erred in holding that the Forest Service’s failure to present detailed maps of the areas impacted by the Roadless Rule during the scoping period was arbitrary and capricious. The district court found that the Forest Service violated NEPA by failing to provide “maps accurately depicting the areas covered by the Roadless Rule” because without such maps “Wyoming could not meaningfully participate in defining the scope of a rule when it did not know what lands within its borders would be impacted by the rule.”
Wyoming,
As Wyoming acknowledges, neither NEPA’s provisions nor the CEQ Regulations require an agency to include detailed maps or a precise geographic description of the areas potentially affected by a proposed rule during the scoping process. 40 C.F.R. § 1501.7.
22
Furthermore, Wyoming’s assertion — and the district court’s conclusion — that the failure to provide maps deprived Wyoming of an opportunity to meaningfully participate in the scoping process because it could not determine which areas would be affected is wholly without merit. A review of the record demonstrates that Wyoming had adequate notice of the unroaded areas within their borders that would be affected by the proposed rule, which in turn enabled Wyoming to meaningfully participate in the scoping process.
See Kootenai Tribe,
First, the Forest Service displayed preliminary versions of the Roadless Rule maps at the scoping meetings, including the meetings in Wyoming. See Aplt.App. at 312-18 (Baron Decl., dated Feb. 28, 2003) (stating that preliminary maps were presented at scoping meetings in Wyoming, which displayed rough depictions of the RARE II IRAs located within Bighorn, Bridger-Teton, Medicine Bow, Shoshone, and Ashley National Forests, as well as the Thunder Basin National Grassland); id. at 2023-26 (large-scale copies of Geographic Information System (“GIS”) maps depicting RARE II IRAs in Bighorn, Bridger-Teton, and Medicine Bow National Parks, which were displayed at scoping meetings in Wyoming). These maps, although not depicting the precise boundaries of the rule’s geographic scope, gave Wyoming sufficient notice as to which IRAs within its borders would generally be impacted by the rule. Second, even without the maps, Wyoming was aware of the IRAs that would be impacted because the NOI indicated that the rule would “restrict certain activities ... in unroaded portions of inventoried roadless areas, as previously identified in RARE II and existing forest plan inventories.” 64 Fed.Reg. at 56,307. This description alone reasonably informed the public, including Wyoming, of which IRAs would be affected by the rule. The notice provided by the preliminary maps and also the NOI’s reference to IRAs identified in the RARE II and existing forest plan inventories were more than sufficient to allow Wyoming to meaningfully participate in the initial scoping phase of the EIS process; that is, sufficient to allow them to meaningfully participate in the “early and open process for determining the scope of issues to be addressed and for identifying the significant issues related to a proposed action.” 40 C.F.R. § 1501.7. 23 Accordingly, we hold that the district court erred in holding that the Forest Service’s failure to provide more detailed maps during the scoping period was arbitrary and capricious.
3. Cooperating-Agency Status
In February of 2000, early in the NEPA process, Wyoming requested the Forest Service to grant it “cooperating agency” status under the CEQ Regulations. The Forest Service never responded, thereby impliedly rejecting or denying Wyoming’s request. The district court concluded that, although administrative agencies generally have “the discretion to grant or deny the states cooperating agency status,” the Forest Service acted arbitrarily and capriciously in denying Wyoming’s request because “[t]here is not one
*1242
good reason in the administrative record before the Court explaining why cooperating-agency status was denied to the ten most affected states, including Wyoming.”
Wyoming,
All agency actions are presumed reviewable under the APA.
Payton v. U.S. Dep’t of Agric.,
The CEQ Regulations state that “[u]pon request of the lead agency, any other Federal agency which has jurisdiction by law shall be a cooperating agency.” 40 C.F.R. § 1501.6. A “cooperating agency” is defined as “any Federal agency other than a lead agency which has jurisdiction by law or special expertise with respect to any environmental impact involved in a proposal (or a reasonable alternative) for legislation or other major Federal action significantly affecting the quality of the human environment.” Id. § 1508.5. A non-federal agency, such as a State or local agency, “may request the lead agency to designate it a cooperating agency,” id. § 1501.6 (emphasis added), and “may by agreement with the lead agency become a cooperating agency,” id. § 1508.5 (emphasis added).
Although it is true that the CEQ Regulations permit Wyoming to request cooperating-agency status from the Forest Service, and further authorize the agency to grant such status, nothing in the regulations mandates or requires that the Forest Service grant such a request. More importantly, the applicable regulations provide no standard for a court to apply in reviewing the Forest Service’s denial of such a request, and are likewise devoid of any standards or directives that would guide the Forest Service in granting or denying such a request. In other words, there is simply no law to apply.
Cf. Solis,
4. Alternatives Analysis
Wyoming and CMA also claim that the Forest Service violated NEPA by failing to adequately consider a reasonable range of alternatives to the proposed action. More specifically, they argue that the Forest Service impermissibly defined the purpose of the proposed action too narrowly, which therefore precluded consideration of a reasonable range of alternatives. The district court, finding in favor Wyoming and CMA, held that the Forest Service violated NEPA because it “failed to rigorously explore and objectively evaluate all reasonable alternatives” to the proposed action, which “was the result of the agency narrowly defining the scope of its project” thereby “eliminatfing] competing alternatives out of consideration and existence.”
Wyoming,
a. NEPA’s Alternatives-Analysis Mandate
Under NEPA, an EIS prepared by a federal agency must include a discussion of “alternatives to the proposed action.” 42 U.S.C. § 4332(2)(C). The analysis of alternatives “is characterized as ‘the heart’ of the environmental impact statement.”
Colo. Envtl. Coal. v. Dombeck,
“We review an EIS under a ‘rule of reason’ standard to determine ... whether the discussion of alternatives in the EIS is sufficient to permit a reasoned choice among the options.”
Ass’ns Working for Aurora’s Residential Env’t
*1244
(AWARE) v. Colo. Dep’t of Transp.,
We have held that “[o]nce an agency appropriately defines the objectives of an action, NEPA does not require agencies to analyze the environmental consequences of alternatives it has in good faith rejected as too remote, speculative, or ... impractical or ineffective.”
Citizens’ Comm. to Save Our Canyons,
For the alternatives selected for detailed analysis in the EIS, the agency must “[d]e-vote substantial treatment to each alternative ... including the proposed action so that reviewers may evaluate their comparative merits.” 40 C.F.R. § 1502.14(b). Within the detailed alternatives analysis, agencies are also required to “[i]nclude the alternative of no action.”
Id.
§ 1502.14(d);
accord Forest Guardians,
b. Discussion
As stated above, agencies have considerable discretion to define the pur
*1245
poses and objectives of a proposed action, as long as they are reasonable.
Utah Envtl. Cong. v. Bosworth,
To achieve the defined purpose of the proposed rule, “the agency determined that only those uses and activities that are likely to significantly alter landscapes and cause landscape fragmentation on a national scale [would] be considered for prohibition in this proposal.” DEIS at 1-10. Specifically, the Forest Service decided— based on the stated purpose of the action and a review of public commentary — to limit the alternatives analyzed in detail to those that prohibited road construction and reconstruction, in addition to the “no action” alternative. Id.
Within this established scope, the Forest Service analyzed four prohibition alternatives in detail in the EIS: three “action” alternatives and the “no action alternative.” Alternative 1 was the “no action” alternative, DEIS at 2-4, under which “no rule prohibiting activities in [IRAs] would be issued” and “[c]urrent management plans would continue to guide forest and grassland management.” FEIS at ES-5. Alternative 2, which was the preferred alternative identified in the DEIS, proposed a prohibition on “road construction and reconstruction within unroaded portions of [IRAs],” with no explicit restriction on timber harvest. DEIS at 2-4 to 2-5; FEIS at 2-6 to 2-7. Alternative 3, which was the preferred alternative in the FEIS, proposed a prohibition on “road construction, reconstruction, and timber harvest except for stewardship purposes within unroaded portions of [IRAs].” DEIS at 2-5; FEIS at 2-7. Lastly, Alternative 4 proposed a prohibition on “road construction, reconstruction!,] and all timber harvest within unroaded portions of [IRAs],” with no stewardship exception. DEIS at 2-6; FEIS at 2-8.
The Forest Service explained that it was limiting the action alternatives to restrictions on
road construction, reconstruction, and timber harvest, because these activities occur on a national scale, have the greatest likelihood of altering landscapes, often cause significant landscape fragmentation, and often result in immediate, irreversible, and long-term loss of road-less characteristics. In addition, timber harvest historically generates the need for most of the road construction in inventoried roadless areas.
DEIS at 1-10 to 1-11. We conclude that the Forest Service’s decision to limit the alternatives considered in detail to those that focused on restrictions on road construction and timber harvest (as well as the required “no action” alternative) was reasonable in light of its conclusion, based on ample evidence presented in the EIS, that these activities posed the greatest risk of destroying the characteristics of IRAs, *1246 which the proposed rule was intended to protect and preserve.
The district court faulted the Forest Service for only considering alternatives that prohibited road construction, based on the court’s finding that Defendants had not “directed the Court to any evidence considered by the Forest Service to support th[e] conclusory premise” that “any road construction whatsoever would degrade the desirable characteristics of [IRAs] in contravention of the purpose of the Road-less Rule.”
Wyoming,
For example, the Forest Service explained that road construction and reconstruction in IRAs, which occur within IRAs on a nationwide basis: (a) create “the greatest likelihood of altering landscapes,” “[o]ften cause substantial landscape fragmentation and adverse changes to native plant and animal communities,” and can “result in immediate, irretrievable, and long-term loss of roadless characteristics,” FEIS at 1-16; (b) are “the primary human-caused source of soil and water disturbances in forested environments,”
id.
at 3-44; (c) “contribute more sediment to streams than any other land management activity,”
id.
at 3-165; (d) are “major contributors to forest fragmentation” and the associated disturbance of important wildlife habitat,
id.
at 3-131 to 3-133; (e) “convertf ] large areas of habitat into non-habitat” and “negative[ly] [a]ffect[ ] ... both terrestrial and aquatic ecosystems,”
id.
at 3-149 to 3-150; (f) create “avenues for invasion by nonnative invasive plant species that frequently compete with or displace native vegetation,”
id.
at 3-174; and (g) adversely impact threatened and endangered wildlife species, through habitat loss, loss of connectivity with other habitats, displacement, and access for poaching and illegal collection,
see id.
at 3-181 to 3-182. A review of this evidence, among other evidence presented in the DEIS and FEIS, supports the Forest Service’s judgment that a near-total ban on road construction was a necessary component of a rule with the goal of protecting and preserving the characteristics of IRAs.
See Kootenai Tribe,
Unlike the district court, we will defer to the Forest Service’s judgment on this issue.
Cf., e.g., Morris v. U.S. Nuclear Regulatory Comm’n,
*1247
The
district court’s holding
that
the Forest Service failed to satisfy its NEPA mandate was also based on several other conclusions, which we find to be erroneous. First, the district court erred in finding that the Forest Service had considered only two action alternatives. As discussed above, the Forest Service took the requisite “hard look” at four alternatives — the three “action” alternatives and the required “no action” alternative. The district court found that Alternative 2 and Alternative 4 would have the same practical effect of eliminating all logging, in addition to banning road construction and reconstruction, and were therefore essentially identical.
Wyoming,
Second, the district court erred in finding that the Forest Service failed to consider other alternatives, aside from the four alternatives considered in detail.
Wyoming,
The district court also erred in finding that the Forest Service failed to consider the benefits of road building or the environmental impacts of prohibiting road building in the EIS. Specifically, the district court stated that there is “nothing unreasonable about studying in detail an alternative that would permit the construction of a road into a roadless area to protect the forest through active forest management,” and the court disapproved of what it considered the Forest Service’s “cavalier dismissal of such forest management activities, which have been the environmental status quo for decades.”
Wyoming,
Turning to the problems with the district court’s findings, first, as discussed above, the Forest Service considered active forest management as an exception to the general prohibitions on road building in the proposed rule, but dismissed such an exception because the agency reasonably determined that these forest management “activities could lead to widespread road construction in many roadless areas that would be incompatible with the stated purpose and need” of the proposed rule. FEIS at 2-22. In addition, the Forest Service also analyzed the environmental effects and benefits of forest management activities in detail under the “no-action” alternative.
See generally id.
at 3-72 to 3-123 (analyzing “Forest Health and Fire Ecology”).
28
For example, under Alternative 1, the Forest Service analyzed in detail the use of “fuel management” and “fire suppression” practices,
see id.
at 3-76 to 3-93, as well as management practices used to reduce the risk of insect and disease infestation in order to protect and improve forest health,
see id.
at 3-116 to 3-120;
see also id.
at 3-19 to 3-20 (analyzing the use of “Active and Passive Forest Management,” and stating that “[t]he Forest Service recognizes that some management activity may be needed to achieve the most desirable ecological conditions in roadless areas,” but that such “management activities can be achieved in the absence of roads”). After reviewing the record, we therefore conclude that the Forest Service took a “hard look” at the forest management activities, which the district
*1249
court mistakenly asserted that the Forest Service so “cavalierly] dismiss[ed].”
Wyoming,
Lastly, the district court erred in finding that the Forest Service improperly “eliminated ... reasonable alternatives” when it moved the procedural aspect of the Roadless Rule to the 2000 Planning Regulations.
Wyoming,
The only alternatives discussed by the district court that were supposedly “eliminated from [detailed] consideration in the [DEIS] on the grounds that the procedural aspect of the Roadless Rule precluded further examination” were the so-called “mineral withdrawal exemptions.” Id. at 1338 (stating that the “mineral withdrawal exemptions were eliminated from study because such activities could be proposed through the implementation of the procedural alternatives, i.e., through proposals to local forest managers”). However, despite the district court’s conclusion that “the Forest Service did not reevaluate the need for mineral withdrawal exemptions,” the record demonstrates otherwise.
In the FEIS, which reflected the agency’s environmental analysis after the procedural aspects had been moved to the Planning Regulations, the Forest Service reconsidered the “mineral withdrawal” alternatives discussed by the district court and reiterated its conclusion, similarly stated in its DEIS, that “[withdrawal of [IRAs] from mining was considered but was dismissed from detailed study” because “[t]he potential impacts to roadless values from mining activities ... are not believed to be significant and widespread *1250 on a national level” and it would “be difficult to accomplish [specific mining requirements] in a proposal of national scope.” FEIS at 2-19. The Forest Service further reiterated in the FEIS that “mineral withdrawals for specific [IRAs] could be proposed in compliance with Department of the Interior rules and procedures,” id., as opposed to “the procedural alternatives” referenced in the DEIS, DEIS at 2-19. We fail to see how this demonstrates that the Forest Service eliminated reasonable alternatives from its alternatives analysis.
Furthermore, contrary to the district court’s apparent conclusion that the Forest Service failed to “reevaluate the need for mineral withdrawal exemptions,” as discussed above, see supra note 29, the Forest Service analyzed in detail the impacts of the proposed action on mining, mineral leasing, and the related social and economic impacts in the FEIS, and also added an exception to allow road construction “in conjunction with the continuation, extension, or renewal of a mineral lease.” 66 Fed.Reg. at 3256 (to be codified at 36 C.F.R. § 294.12(b)(7)); see FEIS at 2-9 (stating that the mineral-lease exception “was added in response to comments regarding the impacts the prohibition on road construction may have on future mineral leasing”).
In sum, we conclude that the Forest Service considered a reasonable range of alternatives in detail in the EIS, and reasonably rejected those alternatives that did not further the defined purpose of the Roadless Rule. In doing so, “the agency gathered ‘information sufficient to permit a reasoned choice of alternatives as far as environmental aspects are concerned,’ ”
Greater Yellowstone Coal.,
5. Cumulative Impacts
Wyoming next claims that the Forest Service violated NEPA by failing to adequately address the cumulative impacts of the Roadless Rule and three other coordinated rulemaking proceedings: the 2000 Planning Regulations, 65 Fed.Reg. 67,514 (Nov. 9, 2000); the 2001 Road Management Rule, 66 Fed.Reg. 3206 (Jan. 12, 2001); and the 2001 Transportation Policy, 66 Fed.Reg. 3219 (Jan. 12, 2001); 66 Fed. Reg. 65,796 (Dec. 20, 2001).
30
Wyoming asserts that the Forest Service’s cumulative impacts analysis “did not provide needed information to the public or focus the agency’s attention on the environmental consequences of its proposal, as required by NEPA.” Wyo. Br. at 30. The district court, agreeing with Wyoming, concluded that the “Forest Service’s final
*1251
EIS does not provide an adequate discussion of the cumulative impacts of the [four coordinated rulemakings],” and that “the Forest Service failed to make a reasonable, good faith, and objective presentation of the cumulative impacts of these rules on the environment.”
Wyoming,
On appeal, the Forest Service does not dispute that it was required to include a discussion of the cumulative impacts of the four coordinated rulemakings in the Road-less Rule FEIS. Instead, it argues that the discussion of the cumulative impacts contained in the FEIS was adequate in that it “fully disclosed ... that the Roadless Rule was one of several coordinated rulemaking initiatives relating to NFS roads,” it discussed and disclosed the cumulative impacts that “reasonably could be foreseen,” and it “reasonably declined to speculate about what was ‘impossible’ to predict; viz., where increases in unroaded areas might occur as a result of the agency’s future planning and project decisions (which themselves will be subject to NEPA analysis).” Forest Serv. Opening Br. at 54, 56-57. The Forest Service argues that “[n]othing more was required.” Id. at 57. Similarly, the Environmental Groups argue that the cumulative-impacts analysis included in the EIS was reasonable and adequate, and any “further analysis of the cumulative impacts of these three policies would have been wholly speculative because they were merely planning provisions to be applied in later forest-specific decisions.” Envtl. Grps. Opening Br. at 30 (emphasis omitted).
Under NEPA, an EIS “must analyze not only the direct impacts of a proposed action, but also the indirect and cumulative impacts of ‘past, present, and reasonably foreseeable future actions regardless of what agency (Federal or non-Federal) or person undertakes such other actions.’ ”
Colo. Envtl. Coal.,
In the FEIS, the Forest Service disclosed the existence of the other coordinated rulemakings and stated that the cumulative purpose of these rulemakings was to collectively “address[] management of existing roads, inventoried roadless areas, and other unroaded areas” in the NFS. FEIS at 1-6, 3-398 (disclosing the existence of and giving an overview of the final Planning Regulations and the future Transportation Policy and Road Management Rule). In the cumulative-impacts section of the FEIS, the Forest Service acknowledged “that the Roadless Rule together with the other proposed and finalized rules and policies could have cumulative effects.” Id. at 3-396. As to the analysis of the Planning Regulations— which were enacted to “guide land management planning for the [NFS] and describe the required planning process and content of land and resource management plans,” but “not [to] specify criteria or characteristics for roadless area delineation or management,” id. at 3-397 — the Forest Service stated that “the two rules (Planning Regulations and Roadless Rule) are complementary, not additive.” Id. The Forest Service stated that “if the two rule[s] are implemented together, it is reasonable to predict that more inventoried roadless areas would be allocated to management uses that maintain undeveloped roadless characteristics th[a]n may have been allocated by the Planning Regulations alone”; however, “[t]o what extent this would occur is not predictable since it would occur through the local decision making process.” Id.
The cumulative-impacts analysis also discussed the Transportation Policy and Road Management Rule, which had not been promulgated at the time the FEIS was issued. Together, the rule and policy dealt with, among other things, the decommissioning of NFS roads, identification of minimum transportation needs on NFS lands, and construction of new roads or reconstruction of existing roads on NFS land (for compelling reasons only). Id. at 3-398. More specifically, the Road Management Rule “would change definitions and road management objectives, establish information to be contained in the road atlas (maps and inventory), and direct officials to identify the minimum transportation system needed that would best serve current and anticipated management objectives and public uses of NFS lands.” Id. The proposed Transportation Policy would give “unneeded roads ... decommissioning priority if they were causing environmental impacts,” would “require[] a determination of a compelling need for road construction and reconstruction in certain unroaded areas,” and would require the establishment of a forest-wide “science-based roads analysis process” that would “help analyze effects [of road construction] to unroaded areas.” Id. In its analysis, the Forest Service concluded that the Roadless Rule would “augment the provisions of the proposed Roads Policy that address [IRAs], since under the [Roadless Rule] construction and reconstruction in [IRAs] would be prohibited,” and would cumulatively result “in better road planning and a probable decrease in road construction overall.” Id.) see also id. (“The proposed Roads Policy is complementary to the proposed Roadless Rule and provides an additional level of review and analysis in certain unroaded areas of NFS lands.”).
*1253 In sum, the Forest Service identified and gave an overview of the three other coordinated rulemakings and addressed the reasonably foreseeable cumulative effect of the rules — viz., that they would likely result in an overall decrease in road construction and an increase in unroaded areas in IRAs. On the other hand, because the agency could not reasonably predict what specific actions and decisions would be taken under the other three rulemakings in the future, the agency declined to address the magnitude or degree of these cumulative impacts on specific NFS lands in any further detail.
The district court found this analysis “woefully inadequate.”
Wyoming,
In general, we have not required agencies to consider “speculative” impacts or actions in an EIS, whether it be in the context of the reasonable-alternatives analysis or the reasonably foreseeable impacts of the proposed project or other projects.
See, e.g., Wilderness Workshop,
Therefore, although the Forest Service was right to disclose the coordinated rule-makings and acknowledge that they could have some cumulative impacts — i.e., that they likely would result in an overall decrease in road construction and an increase in unroaded areas in the NFS — it was required to include only impacts that were reasonably foreseeable.
32
Aecording
*1254
ly, we conclude that the Forest Service made “a reasonable, good faith, objective presentation of those [cumulative] impacts sufficient to foster public participation and informed decision making.”
Colo. Envtl. Coal.,
6. Site-Specific Analysis
Wyoming asserts that the Forest Service also violated NEPA in promulgating the Roadless Rule because it failed to conduct a “site-specific analysis” of the environmental impacts for each of the specific forest units affected by the Rule. The district court rejected this argument and held that the Forest Service was not required under NEPA to conduct a site-specific analysis for every affected IRA.
Wyoming,
In preparing the EIS for the Roadless Rule, the Forest Service was required to provide a “detailed statement” regarding, among other things, “the environmental impact” of the rule and “any adverse environmental effects which cannot be avoided should the [rule] be implemented.” 42 U.S.C. § 4332(2)(C);
see also
40 C.F.R. § 1502.16 (stating that the detailed statement should include: “environmental impacts of the alternatives ..., any adverse environmental effects which cannot be avoided should the proposal be implemented, the relationship between short-term
*1255
uses of man’s environment and the maintenance and enhancement of long-term productivity, and any irreversible or irretrievable commitments of resources which would be involved in the proposal”). For “broad Federal actions such as the adoption of new agency programs or regulations,” the CEQ Regulations state that the agency “may find it useful to evaluate the proposal! ] ... [gjenerically, including actions which have relevant similarities, such as common timing, impacts, alternatives, methods of implementation, media, or subject matter.” 40 C.F.R. § 1502.4(c)(2). There is nothing in the statute or CEQ Regulations that requires an agency to include a site-specific analysis for every particular area affected by the proposed action. Furthermore, as the district court correctly acknowledged, “[njeither the Supreme Court nor the Tenth Circuit has ascribed to the ... view that an agency must conduct a ‘reasonably thorough’ site-specific analysis under NEPA.”
Wyoming,
Wyoming asserts that NEPA uniformly requires an agency to prepare a site-specific analysis for every specific area affected by a proposed action, regardless of whether the agency is proposing a localized project or a broad nationwide rule. In making this argument, Wyoming cites three decisions from other circuits where an EIS was found to be insufficient for failing to assess the site-specific environmental consequences unique to each proposed action on appeal.
See Conservation Law Found. of New England, Inc. v. Gen. Servs. Admin.,
*1256 We conclude that the district court did not err in holding that the Forest Service was not required in this instance to conduct a site-specific analysis for every IRA affected by the rule. Because the Road-less Rule is a “broad” nationwide rule, the Forest Service was permitted under 40 C.F.R. § 1502.4(c)(2) to evaluate the common environmental impacts and effects of the rule “generically.” In accordance with that provision, the Forest Service “generically” evaluated the common environmental impacts of the four alternatives on IRAs. See generally FEIS at 3-1 to 3-407 (analyzing the “affected environment and environmental consequences” of the Road-less Rule, and the general environmental impacts under each of the four prohibition alternatives).
Furthermore, in addition to this general analysis, the Forest Service actually considered some regional distinctions and site-specific aspects of the proposed Roadless Rule, including the impact of the proposed alternatives on specific forest areas and IRAs. See, e.g., id. at 3-49 to 3-53 (analyzing the effects on “water quality and drinking water source areas,” and noting distinctions in the impact on various regions, states, and specific forest areas); id. at 3-55 to 3-58 (analyzing the risk of “soil loss” under the proposed alternatives and indicating which regions would be most affected under the prohibition alternatives); id. at 3-58 to 3-62 (analyzing the correlation between landslides and land-management activities — such as road construction and timber harvesting — and noting the risk of landslides under the proposed alternatives in specific areas such as the “coastal forests of Oregon, Washington, and northern California”); id. at app. B (“State-by-State Summaries of Key Information for the Preferred Alternative”).
Under NEPA, our role in reviewing the Forest Service’s EIS “is simply to
*1257
ensure that the agency has adequately considered and disclosed the environmental impact of its actions.”
Utahns for Better Transp.,
7. Supplemental Environmental Impact Statement
Wyoming next claims that the Forest Service violated NEPA when it failed to prepare a supplemental EIS after making changes to the rule in the FEIS and the final rule. The district court, agreeing with Wyoming and CMA, held that the Forest Service violated NEPA when it “made four substantial changes between the draft EIS and the final EIS and did not prepare a supplemental EIS.”
Wyoming,
An agency is required to prepare a supplemental DEIS or FEIS if: (1) “[t]he agency makes substantial changes in the proposed action that are relevant to environmental concerns,” or (2) “[t]here are significant new circumstances or information relevant to environmental concerns and bearing on the proposed action or its impacts.” 40 C.F.R. § 1502.9(c)(1 )(i)-(ii). The duty to prepare a supplemental EIS is based on the need to facilitate informed decisionmaking.
S. Utah Wilderness Alliance v. Norton,
Therefore, a supplemental EIS is required only if the new information or changes made to the proposed action “will affect the quality of the human environment in a significant manner or to a significant extent not already considered.”
Friends of Marolt Park v. U.S. Dept. of Transp.,
First, the Forest Service did not make a substantial change when it shifted the procedural component of the proposed Roadless Rule to the 2000 Planning Regulations. See FEIS at xi (stating that “[t]he procedural alternatives described in the DEIS have been removed from the FEIS because of the decision to incorporate the procedures in the final Planning Regulations”). The Forest Service initially analyzed the proposed procedural aspect, as well as the “no action; no procedures” alternative to the proposed procedures, in the DEIS. See DEIS at S-23, 2-6 to 2-10, 3-223 to 3-225. Thereafter, the Forest Service did not discard those procedures, but instead moved the procedures to the 2000 Planning Regulations. In the FEIS, the Forest Service explained the reasoning behind this change, stating:
Public comments on the proposed Planning Regulations and Agency comments on the DEIS [for the Roadless Rule] also suggested that the procedures for roadless area protection were best suited for the Planning Regulations. Upon review, most of the roadless area characteristics identified in the DEIS and proposed Roadless Rule were similarly required by the Planning Regulations. Therefore, the Forest Service determined that the procedures contemplated in the Roadless Rule should be an explicit part of the plan revision process, and addressed them at [§] 36 CFR 219.9(b)(8) of the final Planning Regulations.
FEIS at 1-16; see also id. at 1-10 (“Since the close of the DEIS comment period ..., the Agency determined [the procedural] requirements were more appropriately addressed in the [§] 36 CFR 219 Planning Regulations. Comments received on the DEIS about the procedures were shared with the Planning Regulations team, and were incorporated into that rulemaking.”).
After making this shift, the Forest Service fully analyzed the effects of the procedural aspects in the 2000 Planning Regulations. See, e.g., National Forest System Land and Resource Management Planning Regulations; Final Rule, 65 Fed.Reg. 67,-514, 67,514-81 (Nov. 9, 2000). Furthermore, the Forest Service addressed the impact of this shift as part of the cumulative-impacts analysis in the FEIS, which revealed that the shift was not “substantial” in terms of the “environmental concerns” of the proposed action. See supra Part II.C.5 (discussing the sufficiency of the Forest Service’s analysis of the cumulative impacts of, inter alia, the 2000 Planning Regulations and the Roadless Rule). Under these circumstances, it cannot be said that the Forest Service acted arbitrarily and capriciously in failing to prepare a supplemental EIS after making this change, because shifting the procedural aspect of the proposed Roadless Rule to the 2000 Planning Regulations was not a “substantial change[] in the proposed action *1259 that [is] relevant to environmental concerns.” 40 C.F.R. § 1502.9(c)(l)(i). 35
Second, the Forest Service was not required to prepare a supplemental EIS when it made the Roadless Rule’s prohibitions applicable to “roaded” portions, in addition to “unroaded” portions, of IRAs. As initially proposed, the prohibitions in the Roadless Rule were not intended to apply to the 2.8 millions acres of IRAs on which roads had been constructed. See DEIS at S-4 (stating that of the 54.3 million acres of IRAs, “roads have been constructed in approximately 2.8 million acres.... The remaining 51.5 million acres make up the ‘unroaded portions of [IRAs]’ discussed in the proposed rule”). In the FEIS, the Forest Service abandoned the distinction between “roaded” and “unroaded” IRAs, making the rule “applicable] to the entire area within the boundaries of the [IRAs], including portions that contain existing roads.” FEIS at 2-5.
The Forest Service indicated that this change was made in response to “[p]ublie comments indicating] that this [roaded versus unroaded] concept was confusing and would be difficult to apply and administer consistently.” Id. at 2-5 n. 3. After making this change, however, the Forest Service explained that “[t]he effects analysis in the DEIS was actually based on application of the prohibitions to entire [IRAs], since data was not specific to road-ed or unroaded portions. Therefore, both the concept and the definition of ‘unroaded portion’ were deleted from the alternatives and analysis in this FEIS.” Id. In other words, even though the proposed rule was initially only intended to apply to “unroaded” portions of IRAs, the DEIS analyzed the environmental effects and consequences of the rule as it applied to both “roaded” and “unroaded” areas. Therefore, the Forest Service had already considered the environmental effects of this change in the DEIS.
As stated above, we have held that even when an agency makes a substantial change, “the failure to issue a supplemental EIS is not arbitrary or capricious [if] the relevant environmental impacts [of that change] have already been considered” during the NEPA process.
Friends of Marolt Park,
Third, the Forest Service was not required to prepare a supplemental EIS when it revised the relevant maps to include an additional 4.2 million acres in the IRAs subject to the Rule. Guided by prescriptions of the Council on Environmental Quality, we have stated that a new or different alternative does not require preparation of a supplemental EIS evaluating such a change when the “new alternative is ‘qualitatively within the spectrum of alternatives that were discussed in the [DEIS].’ ”
New Mexico ex rel. Richardson,
In the Forty Questions guidance document, which we have previously relied upon, 36 the CEQ explains when a modified alternative addressed in the FEIS, but not addressed in the DEIS, would be considered “qualitatively within the spectrum of alternatives that were discussed in the draft”:
If it is qualitatively within the spectrum of alternatives that were discussed in the draft, a supplemental draft will not be needed. For example, a commentor on a draft EIS to designate a wilderness area within a National Forest might reasonably identify a specific tract of the forest, and urge that it be considered for designation. If the draft EIS considered designation of a range of alternative tracts which encompassed forest area of similar quality and quantity, no supplemental EIS would have to be prepared. The agency could fulfill its obligation by addressing that specific alternative in the final EIS.
Forty Questions, 46 Fed.Reg. at 18,035 (emphasis added). This is analogous to the situation currently at issue.
In the DEIS, the prohibitions in the preferred alternative were applicable to 54.3 million acres of IRAs, totaling 28% of the NFS. See, e.g., DEIS at A-3, A-4 tbl.l, 2-3. The Forest Service indicated in the proposed rule that “[p]rior to finalizing this proposed rule, map adjustments may be made for forests and grasslands currently undergoing assessments or land and resource management plan revisions,” thereby increasing or decreasing the total acreage of IRAs affected. 65 Fed.Reg. at 30,279 (proposed § 294.11). The Forest Service — after making these map adjust *1261 ments — increased the “total inventoried roadless area acreage ... from 54.3 million acres in the DEIS to 58.5 million acres in the FEIS.” FEIS at 2-23; see also id. at 1-1 n. 2 (stating that the “[58.5 million-acre] figure has been revised from the 54.3 million acres shown in the DEIS”).
These additional areas identified in the FEIS embody the same characteristics as those areas identified in the DEIS — namely, pristine roadless areas of the NFS, generally 5,000 acres or larger in size, that, for example, “support a diversity of aquatic and terrestrial habitats,” FEIS at 1-1, 1-4; “provide large, relatively undisturbed blocks of habitat for a wide variety of native plants” and “threatened, endangered, proposed, ... [and] sensitive species,”
id.
at 1-1, 1-4; and “provide people with unique recreation activities,”
id.
at 1-4. In other words, the additional IRAs identified in the FEIS can be reasonably characterized as “forest area[s] of similar quality and quantity” as those areas identified in the DEIS. Forty Questions,
Lastly, the Forest Service did not make a substantial change to the proposed “stewardship” exception to the timber-harvesting prohibition by limiting that exception in the final Roadless Rule to harvesting “generally small diameter timber.” 66 Fed:Reg. at 3273 (to be codified at 36 C.F.R. § 294.13(b)(1)). 37 The timber-harvesting prohibition and “stewardship” exception were presented and analyzed in the DEIS and FEIS under Alternative 3. See DEIS at 2-4; FEIS at 2-7. In analyzing Alternative 3, the Forest Service did not propose specific language for the stewardship exception — i.e., permitting only harvesting of “small diameter trees” — but instead explained the objective of the exception as permitting the achievement of “ecological objectives, other than timber *1262 harvest, that may require vegetative manipulation such as improving forest ecosystem health, removing non-native species and replacing with native species, and improving wildlife habitat,” such as “thinning overly dense stands of trees to allow fire to be safely reintroduced into the ecosystem.” DEIS at 2-5; see FEIS at 2-7.
In the DEIS and FEIS analysis, the Forest Service indicated the “ecological objectives” furthered by the stewardship exception, such as improving forest health and reduction of fire hazard, were commonly achieved through the removal of “small diameter trees.” Compare DEIS at 3-21 (stating that many forest areas “now have dense stands of small diameter trees and shrubs,” and therefore “hav[e] a relatively lower degree of ecosystem health” and may be “vulnerable to catastrophic stand replacing wildland fires”), with FEIS at 3-121 (stating that under the forest-health-treatment activities permitted under Alternative 3, “[l]ess work would be done using timber sale contracts because the smaller-diameter, lower-value trees would likely result in fewer economically viable timber sales”). 38
Therefore, the Forest Service was not required to prepare a supplemental EIS in response to this change in the language of the stewardship exception because it had already analyzed the effects of the exception, as that exception was adopted in the final rule.
See Friends of Marolt Park,
In sum, we conclude that the changes made to the proposed action did not trigger a duty to prepare a supplemental EIS, either individually or collectively. The district court’s conclusion to the contrary was erroneous. 39
*1263 8. Predetermination
Wyoming’s final argument under NEPA is that the Forest Service impermissibly predetermined the outcome of the Roadless Rule proceeding. Specifically, Wyoming asserts that the Forest Service’s bias prevented it from taking a “hard look” at the environmental impacts of the Road-less Rule as required by NEPA. Although the district court noted in its opinion that the end-product of the Roadless Rule NEPA process was “predetermined” and “preordained,”
Wyoming,
In analyzing the environmental impacts of a proposed action under NEPA, agency officials are not required to be “subjectively impartial.”
Forest Guardians,
“[I]f an agency predetermines the NEPA analysis by committing itself to an outcome, the agency likely has failed to take a hard look at the environmental consequences of its actions due to its bias in favor of that outcome and, therefore, has acted arbitrarily and capriciously.”
Forest Guardians,
predetermination occurs only when an agency irreversibly and irretrievably commits itself to a plan of action that is dependent upon the NEPA environmental analysis producing a certain outcome, before the agency has completed that environmental analysis — which of course is supposed to involve an objective, good faith inquiry into the environmental consequences of the agency’s proposed action.
Id.
This “high” standard articulated in
Forest Guardians
makes clear that “predetermination is different in kind from mere ‘subjective impartiality.’ ”
Id.
(quoting
Envtl. Def. Fund,
After reviewing the record on appeal, we conclude that the Forest Service did not “irreversibly and irretrievably” commit itself to a certain outcome before it had completed its NEPA analysis. Wyoming asserts that the “Roadless Rule was a foregone conclusion — a decision made long before the public was brought into the process.” Wyo. Br. at 37. In support of its claim that the Forest Service predetermined the outcome of the Roadless Rule, and therefore did “not tak[e] a hard look at the Rule’s [environmental] impacts,” Wyo. Br. at 38, Wyoming points to the “expedited schedule [the Forest Service] set for itself,” the “insurmountable odds” that it overcame in such a short time, and the overall complexity of the rulemaking process. Id.
In addition, Wyoming points to the existence of several intra-agency comments made by “career Forest Service employ *1265 ees,” id.- — who apparently all were below the rank of political appointees — regarding the appearance of bias or predetermination. See Aplee. Supp.App. at 167-68 (Memorandum from Lyle Laverty, Forest Serv. Reg’l Forester, to Bill Supulski, Forest Serv. EIS Team Leader, on Internal Review and Comment on Roadless Rule DEIS (July 7, 2000)) (stating that the DEIS “appears biased” and “oversells the positive effects of the preferred alternative”); id. at 167 (stating that “[s]ome of the public has the perception that [Vice President A1 Gore’s] announcement [regarding his position on timber harvests in the IRAs] reveals the final decision and, therefore, further participation and comment is meaningless”); id. at 244 (E-mail Correspondence between Forest Service Employees, dated July 25, 2000) (stating that Forest Service employees “will be accused (and perhaps rightfully so) of not listening to the public comments, and having [their] minds made up before any reanalysis is done for the FEIS”). 41
However, the evidence before us simply does not satisfy the stringent standard applicable to claims of predetermination under NEPA. We have generally concluded that predetermination was present only when there was concrete evidence demonstrating that the agency had irreversibly and irretrievably bound itself to a certain outcome — for example, through a contractual obligation or other binding agreement.
See Davis,
The cited intra-agency comments certainly are not enough to show that
the Forest Service,
as a governmental body, “irreversibly and irretrievably” committed itself to a particular outcome before it completed the NEPA analysis of the Roadless Rule. As this court stated in
Forest Guardians,
“an individual’s comments remain immaterial to the predetermination analysis unless they (1) may fairly be attributed to the agency, and (2) tend to reflect the agency’s irreversible and irretrievable commitment to a course of action — in contemplation of a particular environmental outcome — even
before
the requisite environmental analysis has been completed.”
Accordingly, because the record does not contain sufficient evidence to show that the Forest Service irreversibly and irretrievably committed itself to a certain outcome before the NEPA analysis was completed, and because the Forest Service otherwise complied with the mandates of NEPA, we conclude that the Forest Service indeed took a “hard look” at the environmental consequences of the Roadless Rule and therefore did not act arbitrarily and capriciously in conducting its NEPA analysis.
D. MUSYA Claim
Although Wyoming claimed below that the Roadless Rule violated MUSYA, the district court declined to rule on that issue “[a]s the court ha[d] already found that the Roadless Rule was promulgated in violation of NEPA and the Wilderness Act.”
Wyoming,
First, contrary to Wyoming’s assertions, the Roadless Rule is not a “one size fits all” regulation requiring “identical treatment” of all IRAs. Although the rule does provide broad, uniform prescriptions for IRAs — through the general prohibitions on road building and commercial logging, 66 Fed.Reg. at 3272-73 (to be codified at 36 C.F.R. §§ 294.12(a), 294.13(a)) — it does not compel “identical treatment” of all IRAs. The seven exceptions enumerated in § 294.12(b) and the four enumerated in § 294.13(b), allow the “Responsible Official” for each IRA to permit road building and timber cutting in a variety of situations. Application of the exceptions will permit varied managements actions and strategies depending on the particularized and localized conditions unique to each IRA.
For example, responsible officials may permit the cutting, removal, and sale of small diameter timber to occur within a particular IRA in order to “improve threatened, endangered, proposed, or sensitive species habitat” of the area or “to maintain or restore the characteristics of ecosystem composition and structure” of the area. 66 Fed.Reg. at 3272-73 (to be codified at 36 C.F.R. § 294.13(b)(l)(i)-(ii)). Road construction may also be authorized by the Responsible Official — for example, if it is determined “that a Federal Aid Highway project ... is in the public interest,” or if “needed to implement a road safety improvement project,” or if “needed to prevent irreparable resource damage that arises from the design, location, use, or deterioration of a classified road ... [but] only if the road is deemed essential for public or private access, natural resource management, or public health and safety.” Id. at 3272 (to be codified at 36 C.F.R. § 294.13(a)(4)-(6)). Application of these exceptions will likewise be specific to the particular IRA in question.
Furthermore, the Roadless Rule does not prohibit the development of new rules specific to individual IRAs through the NFMA forest-planning process, which would be tailored to address local forest conditions. Moreover, it leaves in place pre-existing forest plans governing individual IRAs, at least to the extent that they do not conflict with the Roadless Rule. These examples demonstrate that the Roadless Rule will not require “identical treatment” of all IRAs. To the contrary, it permits — through the rule’s exceptions and through the NFMA forest-planning process — individualized treatment of IRAs. 44
Second, the Roadless Rule does not “preclude[ ] administration of renewable resources for multiple use” in violation of MUSYA. Wyoming correctly states that MUSYA mandates that the Forest Service “develop and administer the renewable surface resources of the national forests for multiple use,” 16 U.S.C. § 529, including “for outdoor recreation, range, timber, watershed, and wildlife and fish purposes,” id. § 528. However, contrary to Wyoming’s argument, the Roadless *1268 Rule fulfills this mandate; that is, the rule conforms to the multiple-use mandate of MUSYA, including management of NFS lands for “outdoor recreation,” “watershed,” and “wildlife and fish purposes.” Id. § 528. Although the Roadless Rule does not permit all uses specifically identified in MUSYA — namely, “timber” purposes — this is not required under MUSYA.
In defining “multiple use,” Congress acknowledged that “some [NFS] land will be used for less than all of the resources” identified. 16 U.S.C. § 531(a);
see also id.
(stating that “multiple use” management means “making the most judicious use of the land for
some or all
of these resources or related services” (emphasis added)). Therefore, although the Forest Service is directed to manage “the renewable surface resources of the national forests for multiple use,”
id.
§ 529, the agency has broad discretion to determine the proper mix of uses permitted within those lands.
See Bergland,
Wyoming argues that “multiple use cannot be seriously contemplated when access to forests is effectively cut off by the roads prohibition.” Wyo. Br. at 44 (citing
Wyoming,
Lastly, we disagree with Wyoming’s contention that the Forest Service failed to give “due consideration ... to the relative values of the various resources in particular areas.” 16 U.S.C. § 529. In support of this argument, Wyoming relies heavily on the Forest Service’s alleged “failure to take a site specific and genuinely hard look at the impacts of the Roadless Rule during the NEPA process.” Wyo. Br. at 44. However, as discussed supra, this allegation is incorrect; we have already concluded that the Forest Service took the requisite “hard look” at the environmental impacts and consequences of the Roadless Rule during the NEPA process. This assertion therefore lends no support to the MUSYA claim.
Furthermore, a review of the record demonstrates that the Forest Service adequately considered the “relative values of the various resources” within IRAs. In promulgating the Roadless Rule, the Forest Service assessed the value of the various resources found within IRAs, including consideration of, among other things: (a) timber, see FEIS at 3-193 to 3-207, 3-295 *1269 to 3-308 (evaluation of timber harvests); (b) recreational uses, see id. at 3-207 to 3-227, 3-271 to 3-280 (evaluation of “dispersed recreation activities” and “developed and road-based recreation activities”); (c) wilderness, see id. at 3-237 to 3-242, 3-271 to 3-280 (evaluation of wilderness); (d) watersheds and water quality, see id. at 3-46 to 3-55 (evaluation or “water quantity,” “water quality,” “drinking water source areas,” and stream “channel morphology”); and (e) wildlife and fish, see id. at 3-142 to 3-171 (evaluation of “biodiversity” in general, including terrestrial and aquatic habitat and animal and plant species, as well as threatened, endangered, proposed, and sensitive species). We therefore cannot agree with Wyoming’s argument that the Forest Service failed to give “due consideration ... to the relative values of the various resources” within IRAs when promulgating the Roadless Rule. As stated above, the ultimate mix of uses chosen by the Forest Service after consideration of the competing resource values is largely left to agency discretion.
In sum, we find that Wyoming’s arguments pertaining to the alleged violation of MUSYA are without merit. We conclude that the Forest Service did not violate MUSYA — or otherwise act arbitrarily and capriciously under MUSYA — in promulgating the Roadless Rule.
E. NFMA Claim
The district court also declined to rule on Wyoming’s NFMA claim.
Wyoming,
Under NFMA, “which is primarily concerned with planning,”
Utah Envtl. Cong. v. Richmond,
NFMA establishes both substantive and procedural requirements governing the development of individual forest plans.
See id.
§ 1604. For example, each forest plan must comply with MUSYA’s multiple-use mandate. 16 U.S.C. § 1604(e)(1);
accord Utah Envtl. Cong. v. Richmond,
Because the Roadless Rule is applicable to IRAs nationwide, rather than to a specific unit of the NFS, the Forest Service promulgated the rule pursuant to the general rulemaking authority granted to it under the Organic Act, which was reaffirmed under MUSYA. The Organic Act grants the Forest Service the authority to regulate the “occupancy and use” of the national forests in order “to preserve the forests thereon from destruction.” 16 U.S.C. § 551. As discussed
supra,
the Organic Act gives the Forest Service broad discretion to regulate the occupancy and use of the national forests for a wide variety of purposes.
See Grimaud,
The Forest Service is permitted to rely on its rulemaking authority under the Organic Act and MUSYA to resolve issues of broad, even nationwide, applicability — such as protection of IRAs — even though it is nevertheless required to engage in localized forest planning under the NFMA.
Cf. Am. Hosp. Ass’n v. NLRB,
More specifically, in enacting NFMA, Congress included no expression of intent to repeal or limit the Forest Service’s broad rulemaking authority under the Organic Act; in fact, NFMA does not even
*1271
reference 16 U.S.C. § 551. If Congress had intended to curtail the Forest Service’s broad rulemaking authority under § 551, it is assumed that it would have at least referenced that provision in some manner.
Cf Am. Hosp. Ass’n,
As stated above, the district court did not reach Wyoming’s NFMA issue in the instant case. However, in reviewing a similar challenge under NFMA to the Interim Roadless Rule — the precursor to the Roadless Rule that put in place an eighteen-month moratorium on road construction in IRAs — the same district court concluded that the Forest Service had not violated NFMA when it failed to abide by the Act’s specific procedural requirements because “the Forest Service had the right to proceed via rulemaking in lieu of forest plan modification.”
Wyo. Timber Indus. Ass’n v. U.S. Forest Serv.,
The Ninth Circuit, in reviewing a challenge to the Roadless Rule, came to the same conclusion. In
Kootenai Tribe,
the court stated that although “[t]here is some practical force in the contention that the Roadless Rule will override local forest-by-forest planning with regard to its intended scope,” there is “nothing in [NFMA], which establishes procedures and standards for National Forest System land and resource management plans, [that] precludes national action on a conservation issue within the power of the Forest Service.”
Accordingly, because the Roadless Rule was promulgated under the authority of the Organic Act and MUSYA, and was not otherwise governed by NFMA, the Forest Service was not required to comply with *1272 NFMA’s provisions. Wyoming’s NFMA claim must therefore fail.
F. Remedy: Permanent Injunction
The district court permanently enjoined the Roadless Rule on a nationwide basis.
Wyoming,
The first requirement is dispositive in this action. As discussed above, Wyoming failed to demonstrate that the Forest Service’s promulgation of the Roadless Rule violated the Wilderness Act, NEPA, MUS-YA, or NFMA. Thus, the district court abused its discretion in permanently enjoining the Roadless Rule on a nationwide basis because the court’s action was based on the erroneous legal conclusion that Wyoming had succeeded on the merits of its claims.
III. CONCLUSION
For the foregoing reasons, we REVERSE the district court’s order granting Plaintiff declaratory relief and issuing a permanent injunction, and REMAND the case for the district court to VACATE the permanent injunction.
Notes
. Defendants "Forest Service” collectively refers to the United States Department of Agriculture; the United States Forest Service; Tom Vilsack, Secretary of the United States Department of Agriculture, in his official capacity; and Tom Tidwell, Chief Forester of the United States Forest Service, in his official capacity.
When this action was commenced, Mike Johanns was the Secretary of Agriculture and Dale N. Bosworth was the Chief Forester for the Forest Service. Mr. Johanns and Mr. Bosworth have since been replaced by Tom Vilsack and Tom Tidwell. Thus, pursuant to Rule 25(d) of the Federal Rules of Civil Procedure, Mr. Vilsack and Mr. Tidwell were automatically substituted as the proper party Defendants.
. Defendants-Intervenors-Appellants "Environmental Groups” collectively refers to the Biodiversity Conservation Alliance; Defenders of Wildlife; National Audubon Society; Natural Resources Defense Council; Pacific Rivers Council; Sierra Club; Wilderness Society; and Wyoming Outdoor Council.
. As discussed below, this is the second time Wyoming has brought a challenge to the Roadless Rule, the second time the Wyoming district court has set it aside for violating NEPA and the Wilderness Act, and the second time Wyoming's challenge has come before this court on appeal. See infra Part I.C (discussing the procedural history of this case).
. CMA is an association, comprised of 650 members, that "engage[s] in the production of coal, metals, and agricultural and industrial minerals throughout Colorado and the West.”
Wyoming,
. The Forest Service began actively managing the NFS — under the authority of the Organic Act — in 1905, after the department was transferred to the Department of Agriculture.
Wyoming,
. The Forest Service also considered several “procedural alternatives.” DEIS at 2-6 to 2-10.
. This change was made because the Forest Service "believe[d] it would be difficult to identify the 'roaded portions’ [of IRAs] in a manner that would be ecologically meaningful and administratively consistent.” FEIS at 2-23. The FEIS did not include any additional maps identifying the 2.8 million acres of "roaded” IRAs that were now subject to the prohibitions under the rule.
. The final Roadless Rule restricted timber harvests under the stewardship exception to “small diameter timber,” whereas the FEIS did not explicitly limit the size or diameter that could be harvested for stewardship purposes. Compare 66 Fed Reg. at 3273 (to be codified at 36 C.F.R. § 294.13(b)(1)), with FEIS at 2-15.
. Since 2001, the Roadless Rule has been the subject of at least nine lawsuits, including suits filed in federal district court in Idaho, Utah, North Dakota, Wyoming, Alaska, and the District of Columbia.
Of particular importance, on May 10, 2001, the United States District Court for the District of Idaho found that the plaintiffs had demonstrated likely success on the merits of their claims that the Forest Service violated NEPA in promulgating the Roadless Rule by failing to (a) consider a reasonable range of alternatives, (b) satisfy the notice-and-comment requirements of the Act, and (c) adequately analyze the cumulative impacts of the rule.
Kootenai Tribe of Idaho v. Veneman,
. The Defendant-Intervenors in the first suit are the same Environmental Groups that intervened in this cause of action.
. On appeal, the Ninth Circuit affirmed the district court’s reinstatement of the Roadless Rule.
California ex rel. Lockyer v. U.S. Dep’t of Agric.,
. The Act also included an exception for "mining” that was conducted pursuant to U.S. mining laws and valid existing rights. 16 U.S.C. § 1133(d)(3). However, that "special provision” has expired and mining is no longer permitted in "wilderness areas” designated by Congress under the Wilderness Act.
. The district court also based its conclusion that the Roadless Rule “designated 58.5 million acres of National Forest land as a de facto wilderness area in violation of the Wilderness Act,"
Wyoming,
. The Wilderness Act does provide that the "use of aircraft or motorboats, where these uses have already become established, may be permitted to continue subject to such restrictions as the Secretary of Agriculture deems desirable.” 16 U.S.C. § 1133(d)(1). However, the Wilderness Act still prohibits all other types of motorized or mechanical recreation or transportation, subject to a very limited exception, see 36 C.F.R. § 293.6, as well as the use of aircraft or motorboats that had not already become established. The Roadless Rule, on the other hand, does not prohibit the use of aircraft or motorboats, which could be brought in and out of IRAs through existing roads, and does not prohibit the use of off-road vehicles, bicycles, and other forms of motorized or mechanized transportation.
. Under the Wilderness Act, temporary roads are permitted "as necessary to meet minimum requirements for the administration of the area for the purpose of [the Wilderness Act] (including measures required in emergencies involving the health and safety of persons within the area),” 16 U.S.C. § 1133(c), and for “prospecting for water resources, the establishment and maintenance of reservoirs, water-conservation works, power projects, transmission lines, and other facilities needed in the public interest,” and for "road construction and maintenance essential to development and use thereof,” but only when authorized by the President, id. § 1133(d)(4).
. "Road maintenance” is defined as “[t]he ongoing upkeep of a road necessary to retain or restore the road to the approved road management objective.” 66 Fed.Reg. at 3272 (to be codified at 36 C.F.R. § 294.11).
. See, e.g., 66 Fed.Reg. at 3264 ("Reasonable access includes [ ] road construction or reconstruction for mining activities covered under the General Mining Law____”).
.
See
16 U.S.C. § 1133(d)(3) (“Subject to valid rights then existing, effective January 1, 1984, the minerals in lands designated by this chapter as wilderness areas are withdrawn from all forms of appropriation under the mining laws and from disposition under all laws pertaining to mineral leasing and all amendments thereto.”);
see also Wilderness Soc’y v. Dombeck,
. Furthermore, as the Forest Service points out, "the Wilderness Act exception [under § 1133(d)(1)] applies to a broader [and overall more restrictive] set of prohibitions.” Forest Serv. Reply Br. at 9. As it explained:
For example, given the Wilderness Act’s prohibition on "motorized equipment,” USDA could not use a chain saw to cut a fire break in advance of a wildfire that threatened property interests, but for the statutory exception permitting measures necessary to "control ... fire.” See 16 U.S.C. § 1133(c), (d)(1). In contrast, the Roadless Rule does not ban motorized equipment in the first place.
Id.
. Any argument that the Wilderness Act impliedly repealed the Forest Service's general authority to regulate NFS lands for conservation purposes — that is, short of designating de facto wilderness by administrative rule — must fail. It is undisputed that Congress did not expressly repeal the general rulemaking authority granted to the Forest Service under the Organic Act and MUSYA. To the contrary, Congress explicitly stated that "[n]othing in [the Wilderness Act] shall be deemed to be in interference with the purpose for which national forests are established as set forth in [the Organic Act] and [MUSYA].” 16 U.S.C. § 1133(a)(1);
see, e.g., Minn. Pub. Interest Research Grp. v. Butz,
. In any event, we are convinced that Wyoming was given a meaningful opportunity to participate in the scoping process. A review of the record demonstrates that the Forest Service’s sixty-day scoping period was adequate because of the substantial input the Forest Service was able to obtain during that period. The Forest Service conducted 187 public meetings, several of which were held in Wyoming, and received approximately 517,000 comments during the sixty days. It is virtually certain that this process produced more than enough information to “[d]etermine the scope ... and the significant issues to be analyzed in depth in the [EIS]." 40 C.F.R. § 1501.7(a)(2).
. Wyoming argues that the “[scoping regulations] do require that environmental information of 'high quality’ be made available to public officials and citizens 'before decisions are made and before actions are taken.’" Wyo. Br. at 16-17 (emphasis added) (quoting 40 C.F.R. § 1500.1(b)). However, because § 1500.1(b) is not a scoping regulation, and must only be satisfied “before decisions are made and before actions are taken," it is not relevant to the scoping issue.
. In reviewing a similar challenge to the Forest Service's failure to provide maps during the scoping process for the Roadless Rule EIS, the Ninth Circuit held that "the Forest Service met its obligations under NEPA for the scoping period.”
Kootenai Tribe,
. Wyoming argues that a "meaningful standard" emanates from the "policy" provision of NEPA, 42 U.S.C. § 4331, as well as from a memorandum issued by the CEQ in 1999.
See
42 U.S.C. § 4331(a) (stating that it is the “policy” of the Federal Government under NEPA to work “in cooperation with State and local governments”);
id.
§ 4331(b) (stating that "it is the continuing responsibility of the Federal Government to use all practicable means, consistent with other essential considerations of national policy, to improve and coordinate Federal plans, functions, programs, and resources”); Aplee. Supp.App. at 153-55 (Memorandum from George T. Frampton, Council on Envtl. Quality, to the Heads of Federal Agencies, dated July 28, 1999) ("urg[ing] agencies to more actively solicit in the future the participation of state, tribal and local governments as ‘cooperating agencies' in implementing the [EIS] process under [NEPA]” (citing 40 C.F.R. § 1508.5)). However, this argument fails for two reasons. First, neither § 4331 nor the memorandum set out "clear and specific directives” for the agency or the court to apply.
See Solis,
. The Tenth Circuit has repeatedly held that agencies may limit their alternatives to the no-action alternative and alternatives that meet the defined purpose or objective of the
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proposed action.
See, e.g., Utah Envtl. Cong. v. Bosworth,
. Specifically, these six other "categories” of alternatives included: (i) "processes other than rulemaking for attaining the purpose of this action”; (2) "land use designations”; (3) "prohibitions”; (4) "geographical definitions”; (5) "durations for prohibitions and procedures”; and (6) "exemptions and exceptions.” FEIS at 2-15.
. The district court complained that "the Forest Service stated that it did not consider various components of the alternatives ... because it would create an ‘unmanageably large number of alternatives.’ ”
Wyoming,
. The district court itself characterized these forest management activities as the "environmental status quo” that had been in place "for decades.”
Wyoming,
. For the first time on appeal, CMA argues that the Forest Service violated NEPA by failing to "fully evaluate the adverse economic and social effects of the proposed action.” CMA Br. at 18-23; see 40 C.F.R. § 1508.8 (defining "effects” of a proposed action to include "ecological ..., aesthetic, historic, cultural, economic, social, or health, whether direct, indirect, or cumulative” (emphasis added)). However, this argument is without merit. The Forest Service addressed CMA's concerns about socio-economic impacts regarding mineral extraction and leasing in the EIS. See, e.g., FEIS at 2-8 to 2-9 (addressing "social and economic mitigation measures”); id. at 3-308 to 3-324 (evaluating the social and economic impacts that the proposed rule would have on "energy and non-energy minerals” development); id. at 3-252 to 3-264 (addressing the impacts of the proposed rule on "minerals and geology”); see also id. at 3-326 to 3-350 (evaluating the social and economic impacts of the rale on "forest-dependent communities”). Furthermore, in response to concerns regarding the impacts of the Roadless Rule on mineral extraction, the Forest Service included an exception to allow road construction "in conjunction with the continuation, extension, or renewal of a mineral lease.” 66 Fed.Reg. at 3256 (to be codified at 36 C.F.R. § 294.12(b)(7)); see id. at 3265 (“Existing mineral leases are not subject to the [Roadless Rule's] prohibitions, nor is the continuation, extension, or renewal of an existing mineral lease.... Additionally, road construction or reconstruction may be authorized for new leases on these same lands in the event that application for a new lease is made prior to termination or expiration of the existing lease.”); see also FEIS at 2-9 (stating that the mineral-lease exception "was added in response to comments regarding the impacts the prohibition on road construction may have on future mineral leasing”).
. Briefly stated, the 2000 Planning Regulations, 65 Fed.Reg. 67,514, revised the regulations governing the development, adoption, and amendment of forest plans for the NFS; the 2001 Road Management Rule, 66 Fed. Reg. 3206, amended existing rules governing the management, use, and maintenance of the National Forest Transportation System; and the 2001 Transportation Policy, 66 Fed.Reg. 3219; 66 Fed.Reg. 65,796, governed Forest Service officials' decisions regarding the construction, reconstruction, or decommissioning of roads, among other things.
. The CEQ Regulations define "cumulative impact,” in full, as
the impact on the environment which results from the incremental impact of the action when added to other past, present, and reasonably foreseeable future actions regardless of what agency (Federal or non-Federal) or person undertakes such other actions. Cumulative impacts can result from individually minor but collectively significant actions taking place over a period of time.
40 C.F.R. § 1508.7.
. The Ninth Circuit rejected a virtually identical claim challenging the Forest Service’s cumulative-impacts analysis in the Roadless Rule EIS.
See Kootenai Tribe,
. We have jurisdiction over the site-specific analysis issue, even without a cross-appeal, because an appellee is generally permitted to "defend the judgment won below on any ground supported by the record without filing a cross appeal.” S.
Utah Wilderness Alliance v. Bureau of Land Mgmt.,
. The specific case Wyoming primarily relies upon in asserting that NEPA requires the Forest Service to include a site-specific analysis for every affected area,
California v. Block,
is unpersuasive. The
Block
case concerned a challenge to the Forest Service's RARE II program. Specifically, the plaintiffs in
Block
challenged the Forest Service’s allocation of several forest areas as "nonwilderness,” which meant that such areas would be "managed for purposes other than wilderness preservation.”
Id.
at 762. The EIS prepared by the Forest Service did not analyze the "site-specific impact of this decisive [nonwilderness] allocation decision.”
Id.
at 763. The Forest Service argued that the EIS for RARE II — which was a "programmatic EIS describing the first step in a multistep national pro
*1256
ject” — “need not contain the type of detailed site-specific information normally contained in an EIS prepared for a more narrowly focused project such as a dam or a federal mineral lease.”
Id.
at 760-61. The court disagreed with the Forest Service’s contention that a more general analysis was all that was required given the "national scope of [RARE II's] impact,” and concluded that a site-specific analysis regarding each individual area was required before the Forest Service could irreversibly and irretrievably "commit th[o]se areas for nonwildemess uses.”
Id.
at 760, 763. However, in reaching its decision, the Ninth Circuit relied primarily on the 1973 CEQ Guidelines applicable to the RARE II EIS on appeal.
See id.
at 763 & n. 5 ("The prescribed content of the EIS is delineated in the [CEQ] Guidelines in effect at the time of the EIS’s issuance,” which "were supplanted by the CEQ Regulations adopted November 29, 1978.” (citing 43 Fed.Reg. 55,990 (1978) (codified at 40 C.F.R. §§ 1500-08 (1981)))). Unlike the CEQ Regulations governing the EIS presently before the court, the 1973 Guidelines did not expressly permit an agency to "[gjenerically” evaluate "broad Federal actions such as the adoption of new agency programs or regulations.” 40 C.F.R. § 1502.4(b) — (c)(2). There is also an important factual distinction between the proposed action before the Ninth Circuit in
Block
and the Roadless Rule: the challenged action in
Block
was the allocation of forest areas as "nonwilderness” — thereby opening such areas up to possible development and other uses that could lead to substantial environmental degradation — as opposed to the Roadless Rule, which generally prohibits such "non-wilderness” uses. Lastly, it is worth noting that the court’s holding in
Block,
which could be read to require agencies to undertake site-specific analysis in an EIS for all areas covered by a broad nationwide rule, has been called into doubt or at least qualified by the Ninth Circuit’s subsequent decision in
Kootenai Tribe,
. It is worth noting that neither Wyoming nor CMA put forth any argument on appeal in regard to the shifting of the procedural aspects to the 2000 Planning Regulations. Although "we may not neglect [an issue] simply because an appellee fails to defend adequately the district court's decision,”
Hernandez
v.
Starbuck,
. As we slated in
New Mexico ex rel. Richardson,
"[w]e consider [the CEQ Forty Questions Guidance] 'persuasive authority offering interpretive guidance' regarding the meaning of NEPA and the implementing regulations.”
. In the final Roadless Rule, the so-called stewardship exception states:
[Tjimber may be cut, sold, or removed in inventoried roadless areas if the Responsible Official determines that one of the following circumstances exists....
(1) The cutting, sale, or removal of generally small diameter timber is needed for one of the following purposes and will maintain or improve one or more of the roadless area characteristics as defined in § 294.11.
(i) To improve threatened, endangered, proposed, or sensitive species habitat; or (ii) To maintain or restore the characteristics of ecosystem composition and structure, such as to reduce the risk of uncharacteristic wildfire effects, within the range of variability that would be expected to occur under natural disturbance regimes of the current climatic period[.]
66 Fed.Reg. at 3273 (to be codified at 36 C.F.R. § 294.13(b)(1)) (emphasis added). In the FEIS, the Forest Service had analyzed this exception under Alternative 3 to the proposed action, but had not explicitly included the language "generally small diameter timber” in the exception. FEIS at 2-7.
. See also DEIS at 3-57 tbl.3-11 (indicating that the management activity of “[t]hinning of small diameter trees in the understory'' in order "to reduce fire risk or to enhance old growth” was a common practice); id. at 3-100 (stating that fire hazard is reduced in forests "by disposing of ... the small diameter trees”); id. (demonstrating that "small diameter trees” create a fire hazard in forests); id. at 3-109 ("Forest health treatment activities, such as thinning and fuels reduction, carried out under [Alternative 3] would ... [less often] be done using timber sale contracts because the lower values of the smaller diameter trees removed would likely ... result in fewer economically viable timber sales.” (emphasis added)).
. Furthermore, the district court based its conclusion on a finding that the Forest Service made these "substantial” changes "without giving the public notice or an opportunity to comment on the changes.”
Wyoming,
. As with the site-specific analysis issue, we have jurisdiction over the predetermination issue, even though Wyoming did not file a cross-appeal because "an appellee may generally, without taking a cross appeal, urge in support of a decree any matter appearing in the record.”
Barnhart,
. The district court also expressed concern about the political motivation behind the Roadless Rule.
See Wyoming,
. To the contrary, the evidence demonstrates that the Roadless Rule in fact evolved throughout the NEPA process, which suggests that the agency had not irretrievably and irreversibly committed itself to a predetermined outcome prior to conducting its NEPA analysis. See U.S. Forest Serv., U.S. Dep't of Agriculture, Changes from Proposed to Final Rule (Jan. 5, 2001), http://fs.usda.gov/Internet/ FSE_DOCUMENTS/stelprdb5137365.pdf (enumerating the changes that had occurred from the proposed rule to the final Roadless Rule). Compare FEIS at xi-xiv ("Summary of Changes Between Draft and Final EIS”), with Part II.C.7 (discussing changes in the proposed Roadless Rule that occurred between the issuance of the DEIS and the Final Rule). In fact, and perhaps most importantly, during the NEPA process the Forest Service decided to switch the preferred alternative from Alternative 2 in the DEIS to Alternative 3 in the FEIS. Compare DEIS at 2-4, with FEIS at 2-13.
. Because the record is sufficient to allow us to rule on Wyoming’s MUSYA claim, we conclude that the issue is properly before us on appeal.
See Nielander v. Bd. of Cnty. Comm’rs of Republic, Kan.,
. In any event, even if the Roadless Rule did in fact mandate “identical treatment” of IRAs, Wyoming cites no authority for the proposition that MUSYA prohibits common regulation of similarly situated tracts of land in the NFS.
. As with the MUSYA claim, we find that this claim is properly before the court on appeal. See supra note 33.
. Wyoming relies on a statement in the Senate Report on the NFMA that "[w]hile planning guidelines will apply at all levels, there is not to be a national land management prescription.” S.Rep. No. 94-893, at 30 (1976),
reprinted in
1976 U.S.C.C.A.N. 6662, 6694. However, this single statement does not evidence a clear expression of “an intent to withhold th[e] authority” granted under the Organic Act.
Am. Hosp. Ass’n,
