Salmon Spawning & Recovery Alliance v. Gutierrez

545 F.3d 1220, 38 Envtl. L. Rep. (Envtl. Law Inst.) 20258, 67 ERC (BNA) 1876, 2008 U.S. App. LEXIS 21063, 2008 WL 4490533
CourtCourt of Appeals for the Ninth Circuit
DecidedOctober 8, 2008
Docket06-35979
StatusPublished
Cited by139 cases

This text of 545 F.3d 1220 (Salmon Spawning & Recovery Alliance v. Gutierrez) 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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Salmon Spawning & Recovery Alliance v. Gutierrez, 545 F.3d 1220, 38 Envtl. L. Rep. (Envtl. Law Inst.) 20258, 67 ERC (BNA) 1876, 2008 U.S. App. LEXIS 21063, 2008 WL 4490533 (9th Cir. 2008).

Opinion

McKEOWN, Circuit Judge:

Wild salmon and steelhead, which are listed as threatened or endangered under the Endangered Species Act, have been the subject of much litigation in the federal courts. As they swim back and forth from the Pacific Northwest to Canada, the fish have no cognizance of an international boundary, or the Pacific Salmon Treaty of 1999 (“Treaty”), an effort by Canada and the United States to manage salmon populations originating in Alaska and the Pacific Northwest.

This appeal concerns whether three conservation groups have standing to challenge the decision of federal agencies and officials to enter into, and remain a party to, that Treaty. The groups alleged that take levels permitted under the Treaty have allowed Canadian fisheries to over-harvest endangered and threatened salmon and steelhead. The district court dismissed all three of their claims for lack of standing. We reverse the district court in part because the groups have procedural standing to bring their third claim for relief. We affirm the dismissal of the first and second claims.

BACKGROUND

At the heart of this case are chinook and coho salmon and steelhead trout populations from Puget Sound, lower Columbia *1223 River, and Snake River (collectively, “salmon”). Twenty-six populations of these salmon are listed as threatened or endangered under the Endangered Species Act, 16 U.S.C. § 1531 et seq. (“ESA”). During their lifetime, these fish swim northward toward waters off the coast of British Columbia and Alaska, and then journey back through Alaskan and Canadian waters to return to their rivers of origin, where they spawn and die. Because of these unusual transboundary migration patterns, ESA-listed salmon that originate in United States waters are often caught by commercial and recreational fishers in Canada before they can make it back to their rivers of origin.

In 1985, Canada and the United States entered into the Pacific Salmon Treaty to manage salmon populations originating in Alaska, Canada, and the Pacific Northwest. That version of the Treaty set harvest ceilings for fisheries in both countries. Those ceilings remained constant from year to year. The ceilings initially proved successful at increasing salmon survival, but a drought in the early 1990s and poor survival conditions reversed that effect. In 1992, the Treaty expired. Unable to work out another agreement, the United States and Canada went back to managing their respective fisheries independently.

In 1999, the two countries entered into another Treaty, which is at the heart of this litigation. In contrast to the 1985 version, a portion of the 1999 Treaty established annual abundance-based chinook management regimes for fisheries off the coast of Southeast Alaska, Canada, Washington, and Oregon. Because Canadian, or “northern,” fisheries harvest listed salmon in substantially greater numbers than the United States, or “southern,” fisheries, the Treaty provisions focus mostly on the take levels of Canadian fisheries. Rather than setting absolute harvest ceilings that remain unchanged from year to year, the 1999 Treaty sets annual chinook harvest limits based on pre- and in-season estimates of abundance.

The Treaty is implemented through the Pacific Salmon Commission (“Commission”). The Commission collects data on harvest from the two countries, and then recommends fishery management regimes. The Secretary of State of the United States, in consultation with the Secretary of Commerce and the Secretary of the Interior, approves or disapproves regimes that are recommended by the Commission. 16 U.S.C. § 3633(a)(2). Only those fishery regimes that are approved by the Secretary of State under subsection (a)(2) are forwarded to the states and tribes for implementation. Id. § 3633(b). The Treaty provisions will expire at the end of 2008, unless the United States and Canada agree to an extension or modification.

The United States’ implementation of the Treaty provisions was conditioned on its compliance with the requirements of the ESA. Under § 7(a)(2), 16 U.S.C. § 1536(a)(2), federal agencies must consult with either the National Marine Fisheries Service (“NMFS”) or the Fish and Wildlife Service (“FWS”) to “insure that any action authorized, funded, or carried out by such agency ... is not likely to jeopardize the continued existence of any endangered species or threatened species.” Formal consultation begins with a written request by the agency planning to take action (“action agency”), and concludes with the issuance of a biological opinion (“BiOp”) by either NMFS or FWS as the “consulting agency.” 50 C.F.R. § 402.14(c), (Z)(l). NMFS or FWS opines in the BiOp whether the proposed action, taken together with its cumulative effects, is likely to jeopardize the continued existence of listed species. Id. § 402.14(g)(4).

If an action is likely to jeopardize a species, the action agency must determine *1224 whether any “reasonable and prudent alternatives” (“RPA”) exist that will avoid jeopardizing threatened species. 16 U.S.C. § 1536(b)(3)(A); 50 C.F.R. § 402.14(h)(3). If the BiOp results in a “no jeopardy” finding, or an RPA is available, NMFS or FWS will issue an “incidental take statement” with the BiOp that exempts the action agency, and those authorized by it, from the taking prohibition of ESA § 9,16 U.S.C. § 1536(b)(4).

The agency action triggering the ESA § 7 consultation process in this case was the State Department’s decision to enter into the 1999 Treaty on behalf of the United States. In effect, NMFS, as the consulting agency, studied whether Canadian take under the levels permitted by the Treaty would jeopardize listed salmon. NMFS issued a BiOp in which it concluded that Canadian take under the Treaty was not likely to jeopardize the continued existence of threatened or endangered salmon stocks. Because NMFS made a “no jeopardy” determination, it had no obligation to identify any alternatives. 16 U.S.C. § 1536(b)(3)(A); 50 C.F.R. § 402.14. NMFS included an incidental take statement to exempt the agencies from liability under ESA § 9.

In November 2005, three conservation groups — Salmon Spawning & Recovery Alliance, Native Fish Society, and Clark-Skamania Flyfishers 1 (collectively “Salmon Spawning”) — filed this action.

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545 F.3d 1220, 38 Envtl. L. Rep. (Envtl. Law Inst.) 20258, 67 ERC (BNA) 1876, 2008 U.S. App. LEXIS 21063, 2008 WL 4490533, Counsel Stack Legal Research, https://law.counselstack.com/opinion/salmon-spawning-recovery-alliance-v-gutierrez-ca9-2008.