Northwest Ecosystem Alliance v. United States Fish And Wildlife Service
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NORTHWEST ECOSYSTEM ALLIANCE; Center for Biological Diversity; Tahoma Audubon Society, Plaintiffs-Appellants,
v.
UNITED STATES FISH AND WILDLIFE SERVICE; Dave Allen, Regional director of U.S. Fish and Wildlife Service; Steve Williams, Director of U.S. Fish and Wildlife Service; Gale Norton, Secretary of the Department of the Interior, Defendants-Appellees.
No. 04-35860.
United States Court of Appeals, Ninth Circuit.
Argued and Submitted November 15, 2006.
Filed February 2, 2007.
Brent Plater, Center for Biological Diversity, San Francisco, CA, Stephanie M. Parent, Pacific Environmental Advocacy Center, Portland, Oregon, for the plaintiffs-appellants.
M. Alice Thurston, U.S. Department of Justice, Washington, D.C., for the defendants-appellees.
Appeal from the United States District Court for the District of Oregon; Owen M. Panner, Senior Judge, Presiding. D.C. No. CV-03-01505-PA.
Before GOODWIN, O'SCANNLAIN, and FISHER, Circuit Judges.
GOODWIN, Circuit Judge.
The United States Fish and Wildlife Service (the "Service") denied a petition to classify western gray squirrels in Washington state as an endangered "distinct population segment" ("DPS") under the Endangered Species Act ("ESA"), 16 U.S.C. § 1531 et seq. Plaintiff-appellants Northwest Ecosystem Alliance, Center for Biological Diversity, and Tahoma Audubon Society (collectively, the "Alliance") sought review of the Service's decision in the district court, which entered summary judgment upholding the Service's determination. The Alliance filed a timely notice of appeal. We affirm.
I. BACKGROUND
A. The Endangered Species Act
Congress enacted the ESA to "provide a means whereby the ecosystems upon which endangered species and threatened species depend may be conserved, [and] to provide a program for the conservation of such endangered species and threatened species." 16 U.S.C. § 1531(b). The ESA requires the Service to identify and list species that are "endangered" or "threatened." 16 U.S.C. § 1533. The Service may list a species, on its own initiative, through notice-and-comment rule-making. 16 U.S.C. § 1533(b)(5). Alternatively, a species may become listed through the petition process provided by the Administrative Procedure Act ("APA"), 5 U.S.C. § 553(e). Any interested person may petition the Service to add or remove a species from the list. Id.; 16 U.S.C. § 1533(b)(3)(A). Upon receiving such a petition, the Service must promptly determine whether the petition is supported by "substantial scientific or commercial information." 16 U.S.C. § 1533(b)(3)(A). If so, the Service is to "commence a review of the status of the species concerned." Id. The Service is required to make a finding on the status of the species within twelve months and publish its finding in the Federal Register. 16 U.S.C. § 1533(b)(3)(B). The Service must make its decision "solely on the basis of the best scientific and commercial data available." 16 U.S.C. § 1533(b)(1)(A). If the Service finds that a petitioned action is warranted, it must promptly publish a proposed regulation to implement its finding. 16 U.S.C. § 1533(b)(3)(B)(ii). A decision by the Service to deny a petitioned action is subject to judicial review. 16 U.S.C. § 1533(b)(3)(C)(ii).
The definition of the term "species" is at the heart of the instant appeal. The ESA defines "species" to include "any subspecies of fish or wildlife or plants, and any distinct population segment of any species of vertebrate fish or wildlife which interbreeds when mature." 16 U.S.C. § 1532(16) (emphasis added). Thus, a population of wildlife that does not constitute a taxonomic species may nevertheless qualify for listing as a DPS. The statute does not expressly define the term "distinct population segment." The Service and the National Marine Fisheries Service ("NMFS") have jointly adopted a policy statement to guide their evaluation of whether a population group should be treated as a DPS. Policy Regarding the Recognition of Distinct Vertebrate Population Segments Under the Endangered Species Act, 61 Fed.Reg. 4722 (Feb. 7, 1996) ("DPS Policy"). The DPS Policy sets forth two factors for consideration: the "[d]iscreteness of the population segment in relation to the remainder of the species to which it belongs," and the "significance of the population segment to the species to which it belongs." Id. at 4725. Discreteness is satisfied if a population segment is "separated from other populations of the same taxon as a consequence of physical, physiological, ecological, or behavioral factors," or if a population's boundaries are marked by international borders. Id. Significance, in turn, is analyzed under four non-exclusive factors: (1) whether the population persists in a unique or unusual ecological setting; (2) whether the loss of the population would cause a "significant gap" in the taxon's range; (3) whether the population is the only surviving natural occurrence of a taxon; and (4) whether the population's genetic characteristics are "markedly" different from the rest of the taxon. Id. A population qualifies as a DPS if it is both discrete and significant. Id. If a population is deemed to be a DPS, the inquiry then proceeds to whether it is endangered or threatened. Id.
B. Western Gray Squirrels in Washington
Sciurus griseus griseus, a subspecies of the western gray squirrel,1 is the largest native tree squirrel in the Pacific Northwest. Status Review and 12-Month Finding for a Petition To List the Washington Population of the Western Gray Squirrel, 68 Fed.Reg. 34,628, 34,629 (June 10, 2003) ("Final Finding"). Members of the subspecies are "silvery-gray with dark flanks and creamy white underneath." Id. They live in trees, rarely venture into open spaces, and subsist principally on acorn and nuts. Historically, the western gray squirrel was widespread throughout Washington, Oregon, California, and western Nevada. Id. at 34,630. Today, the western gray squirrel is fairly common in California, where it is a regulated game species, with an estimated population of eighteen million. Id. at 34,631. In Oregon, the subspecies is not rare and is legally hunted, but its distribution appears to be much reduced from historical levels. Id. at 34,632. In Nevada, the western gray squirrel is rare and has been classified as a "protected species" under state law. Id. at 34,631.
In Washington, the western gray squirrel once ranged from the Puget Sound to the Columbia River, and from the Cascade Mountains to Lake Chelan. Id. at 34,632. The population has long been separated from the rest of the subspecies by the Columbia River. During the last century, its distribution has been reduced to three geographically isolated populations: the Puget Trough population, the North Cascades population, and the South Cascades population.
The Puget Trough population, which is found near the Puget Sound, lives in a transitional ecological setting. Id. at 34,633. The population's habitat of Oregon white oak woodlands is nestled between upland Douglas-fir forests and prairies. The habitat is wetter, flatter, and contains fewer mast-producing trees than the rest of the subspecies' range. Consequently, the Puget Trough population is more dependent on the Oregon white oak for sustenance than populations in ecologically more diverse habitats. "Although the western squirrel was once common on the partially wooded prairies adjacent to the Puget Sound, the surviving Puget Trough population is now centered on Fort Lewis," a military reservation. Id. "During intensive surveys in 1998 to 1999, only 6 western gray squirrels ... were detected in over 4,000 hours of survey effort." Id. Some researchers have concluded that the Puget Trough population is "at a high risk of extirpation." Id.
The North Cascades population is found in Chelan and Okanogan Counties. Id. at 34,632. Unlike the Puget Trough, the North Cascades habitat lacks oaks, the main source of winter foods for the western gray squirrel in most of its range. Id. at 34,635. Instead, the North Cascades population subsists on seeds and nuts produced by pine trees, big leaf maples, and English walnut trees. A survey in 2000 detected only three remnants out of the eighty-nine nests recorded in a 1996 survey, and found eighteen previously unreported nests. The reduced number of nests suggests a corresponding population decline.
The South Cascades population, which constitutes the largest remaining population of western gray squirrels in Washington, is found in Skamania, Klickitat, and Yakima Counties. Id. at 34,632, 34,634. One study has found western gray squirrels in Klickitat to have substantially larger body measurements than elsewhere in the subspecies' range. Id. at 34,637. The study also concluded that the Klickitat population have substantially larger home range sizes and more nests per squirrel than elsewhere. Surveys in 2000 and 2001 produced population density estimates of 0.08-0.13 squirrel per hectare in the Klickitat Wildlife Area, as compared with 1.37 per hectare in Lake County, California, or with 2.47 per hectare in Yosemite Valley in California. Id. at 34,634.
C. Procedural History
On January 4, 2001, the Service received a petition filed by the Alliance requesting an emergency rule to list the Washington population of the western gray squirrel as an endangered or threatened species. On October 29, 2002, the Service published its initial finding that the petition presented substantial information to indicate that one or more distinct population segments of western gray squirrels may exist in Washington. 90-day Finding for a Petition To List the Washington Population of the Western Gray Squirrel as Threatened or Endangered, 67 Fed.Reg. 65,931. The Service proceeded with a twelve-month status review. An early draft decision prepared by the Service's staff scientists recommended listing the Washington population as an endangered DPS. However, the Service ultimately denied the petition in a June 2003 decision published in the Federal Register. Final Finding, 68 Fed. Reg. at 34,628. The Service determined that the Washington population was not significant, under the DPS Policy, to the taxon to which it belonged.
On November 3, 2003, the Alliance filed a complaint in the District of Oregon seeking declaratory and injunctive relief against the Service and its officials. The Alliance contended that the Service's decision was arbitrary and capricious. On August 2, 2004, the district court granted summary judgment for the Service.
This appeal presents two issues: (1) whether the Service's construction of the term "distinct population segment" is entitled to Chevron deference, and if so, whether the Service's construction is reasonable; and (2) whether the Service's denial of the petition was arbitrary and capricious.
II. JURISDICTION AND STANDARD OF REVIEW
The district court had subject matter jurisdiction under 28 U.S.C. § 1331 and 16 U.S.C. § 1540(c) & (g). We have appellate jurisdiction pursuant to 28 U.S.C. § 1291.
We review de novo the district court's grant of summary judgment. United States v. City of Tacoma, 332 F.3d 574, 578 (9th Cir.2003). As discussed below, we review the Service's interpretation of the ESA, as expressed in the DPS Policy, under the analytic framework laid out in Chevron U.S.A., Inc. v. Natural Res. Def. Council, Inc., 467 U.S. 837, 104 S.Ct. 2778, 81 L.Ed.2d 694 (1984). We review the Service's decision on the Washington gray squirrel under the APA, which provides that an agency action may be set aside only if it is "arbitrary, capricious, an abuse of discretion, or otherwise not in accordance with law." 5 U.S.C. § 706(2)(A). This standard of review is "highly deferential, presuming the agency action to be valid and affirming the agency action if a reasonable basis exists for its decision." Independent Acceptance Co. v. California, 204 F.3d 1247, 1251 (9th Cir.2000) (citations omitted). We may not consider information outside of the administrative record, Love v. Thomas, 858 F.2d 1347, 1356 (9th Cir.1988), and may not "substitute [our] judgment for that of the agency." Citizens To Preserve Overton Park, Inc. v. Volpe, 401 U.S. 402, 416, 91 S.Ct. 814, 28 L.Ed.2d 136 (1971), abrogated on other grounds by Califano v. Sanders, 430 U.S. 99, 105, 97 S.Ct. 980, 51 L.Ed.2d 192 (1977). Our task is simply to ensure that the agency "considered the relevant factors and articulated a rational connection between the facts found and the choices made." Nat'l Ass'n of Home Builders v. Norton, 340 F.3d 835, 841 (9th Cir.2003) (quoting Baltimore Gas & Elec. Co. v. Natural Res. Def. Council, Inc., 462 U.S. 87, 105, 103 S.Ct. 2246, 76 L.Ed.2d 437 (1983)); see also Blue Mountains Biodiversity Project v. Blackwood, 161 F.3d 1208, 1211 (9th Cir.1998) (court must determine whether the agency decision was "based on a consideration of the relevant factors") (citation omitted).
III. DISCUSSION
A. Whether the DPS Policy Is Entitled to Chevron Deference
The Alliance contends that the DPS Policy's requirement that a population be significant to its taxon is unlawfully restrictive. The Alliance does not seek to invalidate the DPS Policy on its face, but only as applied here.2
A court reviewing an administrative interpretation of a statute must first ascertain whether Congress has spoken clearly on the issue. Chevron, 467 U.S. at 842-44, 104 S.Ct. 2778. If the statute is clear, we "must give effect to the unambiguously expressed intent of Congress" regardless of the agency's view. Id. at 843, 104 S.Ct. 2778. If the statute is ambiguous, however, we do not simply impose our own independent interpretation. Id. Rather, we must determine how much deference to give to the administrative interpretation. Id.; United States v. Mead Corp., 533 U.S. 218, 227-31, 121 S.Ct. 2164, 150 L.Ed.2d 292 (2001). The precise degree of deference warranted depends on the statute and agency action at issue. Mead, 533 U.S. at 227-31, 121 S.Ct. 2164. Under Chevron's classic formulation,
[i]f Congress has explicitly left a gap for an agency to fill, there is an express delegation of authority to the agency to elucidate a specific provision of the statute by regulation. Such legislative regulations are given controlling weight unless they are arbitrary, capricious, or manifestly contrary to the statute.
467 U.S. at 844, 104 S.Ct. 2778. If Chevron deference is inapplicable because Congress has not delegated interpretative authority to the agency, the agency's views still "constitute a body of experience and informed judgment to which courts and litigants may properly resort for guidance." Skidmore v. Swift & Co., 323 U.S. 134, 140, 65 S.Ct. 161, 89 L.Ed. 124 (1944). The "fair measure of deference" may then range from "great respect" to "near indifference," depending on "the degree of the agency's care, its consistency, formality, and relative expertness, and ... the persuasiveness of the agency's position." Mead, 533 U.S. at 228, 121 S.Ct. 2164.
The ESA does not expressly define "distinct population segment," and the parties agree that the term has no generally accepted scientific meaning. Because the statutory term is elastic, we must decide whether the DPS Policy is entitled to deference under the Chevron standard, or under the less deferential Skidmore standard.
Chevron deference applies "when it appears that Congress delegated authority to the agency generally to make rules carrying the force of law, and that the agency interpretation claiming deference was promulgated in the exercise of that authority." Mead, 533 U.S. at 226-27, 121 S.Ct. 2164. "[D]elegation of such authority may be shown in a variety of ways, as by an agency's power to engage in adjudication or notice-and-comment rulemaking, or by some other indication of a comparable congressional intent." Id. at 227, 121 S.Ct. 2164. "It is fair to assume generally that Congress contemplates administrative action with the effect of law when it provides for a relatively formal administrative procedure tending to foster the fairness and deliberation that should underlie a pronouncement of such force." Id. at 230, 121 S.Ct. 2164. In the ESA, Congress expressly delegated authority to the Service to develop criteria for evaluating petitions to list endangered species. Under 16 U.S.C. § 1533(h)(2), the Service is required to publish, in the Federal Register, guidelines on "criteria for making findings ... with respect to petitions." The Service must also "provide to the public notice of, and opportunity to submit written comments on, any guideline (including amendment thereto) proposed to be established under this subsection." 16 U.S.C. § 1533(h). In substance, the formality § 1533(h) requires for policy statements is indistinguishable from notice-and-comment rulemaking under the APA. Compare 16 U.S.C. § 1533(h) with 5 U.S.C. § 553.3 This fact weighs in favor of affording Chevron deference.
The Alliance contends that the DPS Policy is an informal policy statement that lies "beyond the Chevron pale." Mead, 533 U.S. at 234, 121 S.Ct. 2164; see Christensen v. Harris County, 529 U.S. 576, 587, 120 S.Ct. 1655, 146 L.Ed.2d 621 (2000) ("[I]nterpretations contained in policy statements, agency manuals, and enforcement guidelines, all of which lack the force of law[,] do not warrant Chevron-style deference."). However, one important reason for denying Chevron deference to policy statements is that they are generally exempt from the public notice-and-comment procedures required by § 553 of the APA. 5 U.S.C. § 553(b)(3)(A); cf. Mead, 533 U.S. at 232-234, 121 S.Ct. 2164 (denying Chevron deference to letter rulings adopted without public notice and comment); Christensen, 529 U.S. at 587, 120 S.Ct. 1655 (advisory opinion letter adopted without notice and comment); Reno v. Koray, 515 U.S. 50, 61, 115 S.Ct. 2021, 132 L.Ed.2d 46 (1995) (internal agency guideline adopted without notice and comment). In contrast, § 1533(h) of the ESA expressly requires public notice and comment for both the creation and the modification of the DPS Policy. These procedural rigors, combined with the express congressional command to the Service to develop guidelines,4 distinguish the DPS Policy from garden-variety policy statements that do not enjoy Chevron status.5
Notwithstanding the robust process through which the DPS Policy emerged, the Alliance submits that Chevron deference is inappropriate because the DPS Policy does not have the "force of law." Mead, 533 U.S. at 227, 121 S.Ct. 2164. The Alliance emphasizes that the Service had considered adopting the DPS Policy as a rule, but ultimately decided to adopt it as a policy statement instead.6 This argument is unpersuasive. The DPS Policy was not formulated in response to any party's petition but rather as a definitive statement of how the Service would conduct all future "evaluation[s] of distinct vertebrate population segments for the purposes of listing, delisting, and reclassifying under the Act." 61 Fed.Reg. at 4725. The Alliance has presented no evidence that the DPS Policy has ever been treated (by the Service or parties presenting petitions to list species) as anything other than legally binding. We therefore hold that the DPS Policy is entitled to Chevron deference.
B. Whether the DPS Policy Is a Reasonable Construction of the ESA
An agency interpretation that enjoys Chevron status must be upheld if it is based on a reasonable construction of the statute. Chevron, 467 U.S. at 843-45, 104 S.Ct. 2778. The Alliance argues that the DPS Policy cannot withstand scrutiny even under the deferential Chevron standard.
First, the Alliance challenges the DPS Policy's requirement that a population be both discrete and significant in order to qualify as a "distinct population segment." The Alliance asserts that the words "distinct" and "discrete" are synonyms. Webster's Third New International Dictionary 659 (2002). Thus, they contend, any requirement that a population be significant in addition to being discrete is an additional hurdle not contemplated by the statute. However, the term "distinct" is not as limited in meaning as the Alliance suggests. "Distinct" can mean "notable" or "unusual." Id. It is not inconsistent with common usage, nor is it unreasonable, for the Service to construe "distinct" to mean both "discrete," in the sense of being separate from others, and "significant," in the sense of being notable.
Second, the Alliance claims that the significance requirement conflates separate statutory definitions. The term "significant" appears in the ESA's definition of "endangered species," which is defined as "any species which is in danger of extinction throughout all or a significant portion of its range...." 16 U.S.C. § 1532(6). The DPS Policy incorporates a separate significance requirement into the definition of "distinct population segment," which is in turn part of the statutory definition of "species," 16 U.S.C. § 1532(16). The Alliance argues that the DPS Policy conflates the statutory definitions of "species" and "endangered species," reducing the latter to mere surplusage. Actually, the two significance requirements serve different functions. The significance requirement in the DPS Policy pertains to whether a population qualifies as a species, while significance in § 1532(6) relates to whether a species is endangered. The two terms overlap to some extent in application,7 but they are not identical. For example, a population may be significant under the DPS Policy if it has distinctive ecological or biological traits, but that has no bearing on whether the population is actually in danger of extinction for purposes of § 1532(6).
Third, the Alliance argues that the DPS Policy reflects an impermissibly narrow understanding of the ESA's purpose and focuses excessively on conserving genetic resources. In the Alliance's view, the Service's attention to genetic resources is inappropriate in light of Congress's finding, expressed in the ESA's preamble, that wildlife have "esthetic, ecological, educational, historical, recreational, and scientific value." 16 U.S.C. § 1531(a)(3). The DPS Policy actually describes the ESA's purposes as follows: "The Services understand the Act to support interrelated goals of conserving genetic resources and maintaining natural systems and biodiversity over a representative portion of their historic occurrence. The draft policy was intended to recognize both these intentions, but without focusing on either to the exclusion of the other." 61 Fed.Reg. at 4723. That statement is not inconsistent with the ESA's expressly stated goal of providing "a means whereby the ecosystems upon which endangered species and threatened species depend may be conserved." 16 U.S.C. § 1531(b). In addition, the significance requirement (which is the only portion of the DPS Policy to which the Alliance objects) may be satisfied not only by evidence of genetic differences but also by a population's persistence in unusual ecological settings, its status as the only natural surviving occurrence of a taxon, or evidence that its loss would result in a significant gap in its taxon's range. These are not the hallmarks of a policy that focuses on the conservation of genetic resources at the expense of all the other goals of the ESA.8
Fourth, the Alliance argues that the Service, in formulating the DPS Policy, improperly considered congressional policy preferences expressed after the enactment of the ESA. After the ESA was amended to encompass distinct population segments, the General Accounting Office proposed that Congress repeal the amendment to prevent a proliferation of endangered species listings. Although Congress declined to adopt the proposal, a Senate committee report cautioned that it was "aware of the great potential for abuse" of the Service's DPS authority. S.Rep. No. 96-151, at 7 (1979). The report further stated an expectation that the Service would "use the ability to list populations sparingly and only when the biological evidence indicates that such action is warranted." Id. (emphasis added). The DPS Policy expressed an intent to follow that instruction. 61 Fed.Reg. at 4722. The Alliance contends that the policy views of a subsequent Congress should not be considered in interpreting a statutory term. The Alliance's position might be more persuasive if we were construing the statutory term on a blank slate, but that is not the situation here. We are reviewing an agency determination under the deferential Chevron standard. So long as the agency action is not manifestly contrary to the statute, it is not improper for the agency to consider the views of the elected branches in interpreting an ambiguous statutory term. See Chevron, 467 U.S. at 866, 104 S.Ct. 2778 ("[F]ederal judges — who have no constituency — have a duty to respect the legitimate policy choices made by those who do."). Here the committee report's language was not in obvious tension with the statutory text and the Service did not err by relying on it in part.
Fifth, the Alliance contends that the DPS Policy has been applied inconsistently, pointing to National Association of Home Builders as support for its claim. However, the western pygmy-owl's preliminary listing in that case took place before the DPS Policy was issued in 1996 and thus cannot be used to show inconsistency in the policy's application. 340 F.3d at 839. Similarly, the bald eagle, grizzly bear, and gray wolf listings that the Alliance cites all took place well before 1996 (the last of the three was in 1978) and hence shed no light on the faithfulness of the Service's adherence to the DPS Policy.9 The Alliance also offers recent examples of discrete, endangered populations that were not granted protection by the Service (because they failed the significance requirement) — but, crucially, offers no examples of populations that were granted protection under the DPS Policy despite being found insignificant to their taxon.
For all these reasons, the DPS Policy is a reasonable construction of "distinct population segment."
C. Whether the Service's Denial of the Petition Was Arbitrary and Capricious
Applying the DPS Policy, the Service found that western gray squirrels in Washington constitute a discrete population, but are not significant to the taxon. It therefore denied the petition. The Alliance vigorously challenges the Service's determination on the "significance" prong.
We note that the Service's internal draft finding of May 16, 2003 recommended granting the petitioned action. The Alliance complains that the Service's final finding reached the opposite conclusion without citing any new data. However, the Service may change its mind after internal deliberation. See Southwest Ctr. for Biological Diversity v. Bureau of Reclamation, 143 F.3d 515, 523 (9th Cir.1998). The only question before us is whether the Service, in reaching its ultimate finding, "considered the relevant factors and articulated a rational connection between the facts found and the choices made." Nat'l Ass'n of Home Builders, 340 F.3d at 841.
The DPS Policy sets forth the following four factors to be used to determine a population's significance to its taxon:
1. Persistence of the discrete population segment in an ecological setting unusual or unique for the taxon,
2. Evidence that loss of the discrete population segment would result in a significant gap in the range of a taxon,
3. Evidence that the discrete population represents the only surviving natural occurrence of a taxon that may be more abundant elsewhere as an introduced population outside its historic range, or
4. Evidence that the discrete population segment differs markedly from other populations of the species in its genetic characteristics.