Rock Creek Alliance v. U.S. Fish & Wildlife Service

663 F.3d 439, 42 Envtl. L. Rep. (Envtl. Law Inst.) 20339, 73 ERC (BNA) 1673, 2011 U.S. App. LEXIS 22887, 2011 WL 5557426
CourtCourt of Appeals for the Ninth Circuit
DecidedNovember 16, 2011
Docket10-35596
StatusPublished
Cited by18 cases

This text of 663 F.3d 439 (Rock Creek Alliance v. U.S. Fish & Wildlife Service) is published on Counsel Stack Legal Research, covering Court of Appeals for the Ninth Circuit primary law. Counsel Stack provides free access to over 12 million legal documents including statutes, case law, regulations, and constitutions.

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Rock Creek Alliance v. U.S. Fish & Wildlife Service, 663 F.3d 439, 42 Envtl. L. Rep. (Envtl. Law Inst.) 20339, 73 ERC (BNA) 1673, 2011 U.S. App. LEXIS 22887, 2011 WL 5557426 (9th Cir. 2011).

Opinion

OPINION

PREGERSON, Circuit Judge:

Plaintiff-Appellant Rock Creek Alliance appeals the district court’s grant of summary judgment in favor of Defendant-Appellee the U.S. Fish and Wildlife Service and Intervenor-Defendant-Appellee Revett Silver Company in an action brought pursuant to Section 7 of the Endangered Species Act, which requires federal agencies to consult with the Fish and Wildlife Service before undertaking any action “authorized, funded, or carried out” by the agency that might “jeopardize the continued existence of any endangered species or threatened species or result in the destruction or adverse modification of habitat” used by any endangered or threatened species. 16 U.S.C. § 1536(a)(2). We have jurisdiction under 28 U.S.C. § 1291, and we affirm the district court’s well-reasoned opinion. 1

*442 BACKGROUND

Revett Silver Company proposes to build and operate a copper and silver mine in northwest Montana, part of which will be on land managed by the U.S. Forest Service. Because the mine may impact two species listed as threatened under the Endangered Species Act — the bull trout and the grizzly bear — the Forest Service was required to engage in formal consultations with the Fish and Wildlife Service before approving the mine. 16 U.S.C. § 1536(a)(1). As a part of those consultations, the Fish and Wildlife Service issued two biological opinions that concluded that the mine would result in “no adverse modification” to critical bull trout habitat and would result in “no jeopardy” to the local grizzly bear population. 2

In the district court, Rock Creek Alliance challenged the biological opinions, arguing that the Fish and Wildlife Service’s conclusions were arbitrary, capricious, and violated the Endangered Species Act. The district court disagreed, and granted summary judgment in favor of the Fish and Wildlife Service and Revett Silver Company. Rock Creek Alliance then appealed, arguing that: (1) the Fish and Wildlife Service improperly relied on large-scale analysis in evaluating the mine’s impact on bull trout; (2) the Fish and Wildlife Service did not adequately address the mine’s impact on bull trout recovery; (3) the methodology for calculating grizzly bear mitigation habitat was flawed; and (4) the grizzly bear habitat mitigation plan was unreasonably speculative.

DISCUSSION

We review the district court’s “grant of summary judgment de novo, reviewing directly the [Fish and Wildlife Service’s] action under the Administrative Procedure Act [ (“APA”) ]----” Ariz. Cattle Growers’ Ass’n v. Salazar, 606 F.3d 1160, 1163 (9th Cir.2010). Under the APA, we must set aside an agency’s decision if it is “arbitrary, capricious, an abuse of discretion, or otherwise not in accordance with law.” 5 U.S.C. § 706(2)(A).

We now address each of Rock Creek Alliance’s four arguments.

(1) The Fish and Wildlife Service did not err by conducting a large-scale analysis and by relying on the relative size of Rock Creek critical habitat to evaluate the mine’s impact on the bull trout. The Fish and Wildlife Service properly compared the relative size of the impacted 2.88 stream miles of Rock Creek to the overall size of the Lower Clark Fork Core Area critical habitat — 135 stream miles — to determine that the bull trout’s critical habitat would not be adversely modified. The Fish and Wildlife Service examined in detail the proposed mine’s impact on each of the critical habitat elements in the local Rock Creek environment: water temperature, substrate composition (specifically, increased sediment load), migratory corridors, channel stability, and cover. The Fish and Wildlife Service ultimately concluded that “[a]ll [critical habitat] elements in Rock Creek are expected to remain functional, albeit at a lower [functional] level,” and the most significant impacts *443 would only be temporary, lasting five to seven years. Thus, the Fish and Wildlife Service’s conclusion was not based solely on the scale of the impact, but also on the duration and the level by which the habitat’s functionality would be diminished.

Moreover, the Fish and Wildlife Service’s actions were reasonable under our decision in Gifford Pinchot Task Force v. U.S. Fish and Wildlife Service, 378 F.3d 1059, 1075 (9th Cir.2004). The agency did not attempt to hide the local impacts of the action, but considered them in detail. Contra Fed’n of Fishermen’s Ass’ns v. Nat'l Marine Fisheries Serv., 265 F.3d 1028, 1035-37 (9th Cir.2001) (finding that the National Marine Fisheries Service did not appropriately evaluate the localized impact of the project in issuing their “no jeopardy” opinion). Because there is no evidence in the record that the Fish and Wildlife Service masked “some localized risk ... by [the] use of large scale analysis,” we should “not second-guess” the Fish & Wildlife Service’s conclusion that the mine would not adversely affect the critical habitat. Gifford Pinchot, 378 F.3d at 1075.

(2) The Fish and Wildlife Service did not fail to consider the mine’s impact on bull trout recovery. The Fish and Wildlife Service explicitly addressed bull trout recovery, concluding that, “[a]t most, the rate of recovery of the core area population may slow slightly, if at all, assuming fish passage at the dams and habitat restoration continues and is successful.” The Fish and Wildlife Service also noted that “there may be a slight slowing in the rate of recovery for the core area population because of the slight loss in recruitment potential, but if current efforts to recover [migratory bull trout] ... continue to be successful and overshadow the potential loss, the recovery rate of the core area may not be affected.”

The Fish and Wildlife Service did not, however, address the bull trout recovery issue in separate, distinct sections of the biological opinion, as was contemplated by a 2006 guidance memorandum from the Director of the Fish and Wildlife Service. But the “[Fish and Wildlife Service] must be presumed to have followed the adverse modification regulation,” and to have properly considered the mine’s impact on critical bull trout recovery, “unless rebutted by evidence in the record” to the contrary. Gifford Pinchot, 378 F.3d at 1071-72 (“[W]e afford the agency a presumption of regularity.”). A fair reading of the Fish and Wildlife Service’s biological opinion, coupled with the deference due to the agency, leads to the conclusion that the Fish and Wildlife Service adequately considered the impact that the mine could have on the habitat’s value for bull trout recovery.

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663 F.3d 439, 42 Envtl. L. Rep. (Envtl. Law Inst.) 20339, 73 ERC (BNA) 1673, 2011 U.S. App. LEXIS 22887, 2011 WL 5557426, Counsel Stack Legal Research, https://law.counselstack.com/opinion/rock-creek-alliance-v-us-fish-wildlife-service-ca9-2011.