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Tucson Herpetological Society v. Kempthorne

United States District Court, D. Arizona
Jul 12, 2007
No. 04-CV-00075-PHX-NVW (D. Ariz. Jul. 12, 2007)

Opinion

No. 04-CV-00075-PHX-NVW.

July 12, 2007


ORDER


The court has before it Plaintiffs' Motion for Summary Judgment (doc. # 109) and supporting Memorandum (doc. # 110); Defendants' Cross-Motion for Summary Judgment (doc. # 113) and supporting Memorandum (doc. # 114); and Plaintiffs' Reply (doc. # 115).

This is the continuation of a long-running dispute about the listing of the flat-tailed horned lizard ( Phrynosoma mcallii) ("FTHL" or "lizard") under the Endangered Species Act of 1973 ("ESA" or "Act"), 16 U.S.C. §§ 1531 et seq. The Secretary of the Interior (the "Secretary"), acting through the Fish and Wildlife Service ("FWS"), proposed listing the species for protection in 1993, 58 Fed. Reg. 62624 (noting documented and anticipated population declines associated with widespread habitat loss, fragmentation, and degradation due to human activities such as agricultural development, urban expansion, off-highway vehicle ("OHV") use, energy developments, and military activities). The Secretary moved to withdraw that proposal in 1997, 62 Fed. Reg. 37852, and again in 2003, citing a changed interpretation of current and anticipated threats to extant lizard populations. 68 Fed. Reg. 331, 335/1, 348/3 (January 3, 2003) ("2003 Finding"). The Tucson Herpetological Society, other environmental groups, and concerned individuals ("Plaintiffs") turned back the withdrawal notices on the ground that the Secretary failed to consider whether the flat-tailed horned lizard was "in danger of extinction throughout . . . a significant portion of its range." 16 U.S.C. § 1532(6); Defenders of Wildlife v. Norton, 258 F.3d 1136, 1145-46 (9th Cir. 2001) (vacating 1997 withdrawal); (doc. # 59 at 8-11) (vacating 2003 withdrawal for failure to comply with Defenders).

The Fish and Wildlife Service administers the ESA with respect to species under the jurisdiction of the Secretary of the Interior, including the flat-tailed horned lizard. 50 C.F.R. § 402.01(b).

On remand, the Secretary reopened the comment period and conducted an analysis of both the size and the significance of "the lost historical habitat of the flat-tailed horned lizard." 71 Fed. Reg. 367545, 36745/2 (June 28, 2006) ("2006 Finding"). After further study, the Secretary once again resolved to withdraw the proposed listing. Id. (concluding that the lost habitat is "not a significant portion" of the lizard's range and "does not result in the species likely becoming endangered in the foreseeable future throughout all or a significant portion of its range"). Plaintiffs oppose that conclusion. The narrow question presented by Plaintiffs' Supplemental Complaint (doc. # 98) is whether the Secretary's interpretation of the phrase, "in danger of extinction throughout . . . a significant portion of its range," 16 U.S.C. § 1532(6), is consistent with the decision of the Court of Appeals for the Ninth Circuit in Defenders, and supported by the administrative record. 5 U.S.C. § 706(2)(A). The court finds that it is for the reasons set forth below.

The administrative record in this matter is composed of the record for the 2003 Finding (doc. # 40) (hereinafter "AR"), and the supplemental record for the 2006 Finding (doc. # 112) (hereinafter "Supp. AR").

I. Background

A. The Flat-Tailed Horned Lizard

The flat-tailed horned lizard is a small iguanid with a long, flattened body, a broad flattened tail, and dagger-like head spines. 68 Fed. Reg. at 331/3. The lizard ranges in color from pale gray to light rust brown dorsally, and white or cream ventrally, and is distinguished by a dark vertebral stripe and two rows of fringed scales on either side of its body. Id. The lizard most commonly inhabits sandy flats and valleys with creosote and white bursage plants, which are generally found on alluvial fans and upland slopes with well-drained soils. 71 Fed. Reg. at 36745/3; (Supp. AR doc. # 327 at 2991). Behaviorally, the FTHL differs from other iguanids in that it remains still or may bury itself in loose sand when approached. This reluctance to move when disturbed, together with cryptic coloration and flattening of the body, makes the lizard difficult to locate and study in its desert habitat. (Supp. AR doc. ## 329 at 3012 (citations omitted); 325 at 2894.)

B. The Range of the Flat-Tailed Horned Lizard, Current and Historic

The flat-tailed horned lizard "has the most limited distribution of any horned lizard species" in the United States, occurring "entirely within the Lower Colorado River Valley Subdivision of the Sonoran Desert Scrub, the largest and most arid subdivision of the Sonoran Desert." (Supp. AR doc. # 329 at 3005, 3009.) The species' historic range encompasses the extreme southwestern corner of Arizona, the southeastern corner of California, and adjoining portions of Sonora and Baja California, Mexico. ( Id. at 2999.) The 2003 Rangewide Management Strategy ("RMS"), published by the FTHL Interagency Coordinating Committee and incorporated by reference in the 2006 Finding, contains a graphic representation of the lizard's historic range and its smaller and more fragmented current range, both within the United States and south of the international border in Mexico. 71 Fed. Reg. at 36746/2; (Supp. AR doc. # 329 at 3008). The Secretary's analysis of the lost historic range in the 2006 Finding builds upon his prior assessment of the distribution, and threats to, the FTHL on its current range. 71 Fed. Reg. at 36745/2 (incorporating the 2003 current range analysis, which was previously upheld on judicial review, in the 2006 Finding). The relevant portions of the 2003 and 2006 Findings are summarized below.

The Rangewide Management Strategy provides a "framework for conserving sufficient habitat to maintain several viable populations of the [FTHL] throughout the range of the species in the United States." 68 Fed. Reg. at 334/1 (identifying five Management Areas located on federal land in California and Arizona pursuant to the 1997 Conservation Agreement, discussed in Defenders, 258 F.3d at 1139-40). FTHL habitat located outside of the Management Areas receives "a degree of protection" through mitigation, compensation, and monitoring efforts. (Supp. AR. doc. # 329 at 3028.)

1. The 2003 Finding: Analysis of the Current Range

i. Distribution of the Lizard Today

In the 2003 Finding, the Secretary found that the "distribution of the flat-tailed horned lizard is not contiguous across its range," but is rather fragmented by "large-scale agriculture and urban development" and natural geographic barriers such as the Colorado River and the Salton Sea. 68 Fed. Reg. at 332/1; (Supp. AR doc. ## 330 at 3114 (observing that the FTHL occupies "a specific microhabitat that is now patchily distributed" throughout its historic range in California, Arizona, and Mexico); 329 at 3008 (visual depiction of FTHL habitat fragmentation)).

In the United States, surviving lizard populations are concentrated within four "geographically discrete populations" on approximately 1,376,525 acres of historic habitat. 68 Fed. Reg. at 332/1-2. In California, the lizard is found in the Coachella Valley, the west side of the Salton Sea and Imperial Valley (Borrego Valley, Ocotillo Wells area, West Mesa, and the Yuha Desert), and the east side of the Imperial Valley (East Mesa, Algodones Dunes, and the Dos Palmas Bureau of Land Management area). Id. at 331/3, 332/1. Arizona populations of the FTHL are located in the Yuma Desert south of the Gila River and west of the Gila and Butler Mountains. Id. at 332/1.

In Mexico, the lizard may be found south of California's Yuha Desert from the international border to the Laguna Salada in Baja California, and south of Arizona's Yuma Desert to the Pinacate Region and the sandy plains around Puerto Peñasco and Bahia de San Jorge, Sonora. Id. at 332/1. The precise number of acres occupied by the lizard in Mexico is unknown. In fact, "the distribution of the species in Mexico is poorly understood because few surveys have been conducted" there. Id. at 332/2. Like those in the United States, however, Mexican lizard populations have been isolated to some degree by human-mediated processes, particularly agricultural and urban development. Id. at 332/2, 345/2-3.

ii. Documented and Anticipated Threats

After delineating the lizard's current range, the Secretary evaluated the documented and anticipated threats to the species in light of the five listing factors prescribed by the ESA. The Secretary observed, "The increased use of the desert by Border Patrol, OHVs, and other development and the resulting effects on flat-tailed horned lizards has been difficult to monitor." Id. at 339/3. "Intuitively," the Secretary "know[s] these impacts cannot keep increasing without resulting in negative impacts to habitat." Id. at 339/3. "However, based on the best available information," the Secretary "determined that such possible negative impacts do not currently, or in the foreseeable future, pose a threat to the species." Id. at 339/3, 341-47 (applying the five statutory listing factors to lizard populations on public and private lands). The Secretary withdrew his proposal to list the flat-tailed horned lizard under the ESA upon concluding that "the threats to the species . . . are not as significant as earlier believed." Id. at 348/3.

The five factors the Secretary must consider when determining a species' eligibility for protection are: (A) the present or threatened destruction, modification, or curtailment of [the species'] range; (B); overutilization for commercial, recreational, scientific, or educational purposes; (C) disease or predation; (D) the inadequacy of existing regulatory mechanisms; (E) other natural or manmade factors affecting [the species'] continued existence. 16 U.S.C. § 1533(a)(1).

iii. Current Range Analysis Upheld in Full

On judicial review of the 2003 Finding, this court upheld the Secretary's site-specific review of threats to existing lizard populations on the current range in full. (Doc. # 59 at 11-15 (accepting the Secretary's "fact-based examination of the significance of the threats posed to part of the species' range to the viability of the species as a whole," which was based on "the best scientific and commercial data available").) The Secretary's application of the five listing factors to extant lizard populations will be not be disturbed here.

iv. Historic Range Analysis: The Fatal Flaw in the 2003 Finding

Though his discussion of the threats to the lizard on its current, fragmented range passed muster, the Secretary violated the command of the Ninth Circuit by failing to identify and assess the significance of the historic habitat no longer available to the species. (Doc. # 59 at 9-11.) Defenders held, in essence, that the Secretary must define the ambiguous term, "a significant portion of its range," apply that definition to the lost historic range, and explain his conclusions as to the significance of the forsaken habitat. 258 F.3d at 1145. The 2003 Finding was deficient because, after noting that entire portions of the lizard's historic range in the United States and Mexico had been lost, 68 Fed. Reg. at 332/2, the Secretary did not go on to evaluate the impact of that lost range upon the species, or make any findings as to the significance of that lost habitat whatsoever. He did not consider, for example, whether there were any attributes or specific uses of the lost habitat that made it significant to the survival of the species in any particular geographic area, or even whether the species could recover to the point where it can re-colonize some of its lost habitat. Instead, the Secretary conducted a "forward-looking analysis" that focused exclusively upon the impact of human activity upon the survival of the species as a whole on its current range. (Doc. # 59 at 9)

The Secretary necessarily has a "wide degree of discretion in delineating `a significant portion of its range,' since the term is not defined in the statute." Defenders, 258 F.3d at 1145. However, the Secretary may not close his eyes to the possibility that the lost habitat constitutes a "significant portion" of the species' total range. The Secretary may not assume, without more, that the viability of the species in some specified portion of its current range renders other geographically distinct portions of the historic range insignificant. The Secretary construed the phrase, "in danger of extinction throughout . . . a significant portion of its range," 16 U.S.C. § 1532(6), to mean "that a species is eligible for protection under the ESA if it faces threats in enough key areas of its range that the entire species is in danger of extinction, or will be in the foreseeable future." Defenders, 258 F.3d at 1141 (emphasis in original). This interpretation was "unacceptable" because it could "not be squared with the statute's language or structure." Id. at 1141. To posit "that a species in danger of extinction in a `significant portion of its range' only if it is in danger of extinction everywhere" is to render the phrase "superfluous." Id. at 1141-42. The Secretary may not exercise his discretion under the Endangered Species Act to write the phrase, "a significant portion of its range" out of the statute entirely. 16 U.S.C. § 1532(6).

The Secretary's failure to define the lizard's range so as to include some lost habitat, and his failure to determine whether that lost habitat constituted a "significant portion of its range," was fatal to the 2003 rulemaking. (Doc. # 59 at 10); see Defenders, 258 F.3d at 1145, 1154 n. 11 (deference not warranted because the court cannot "defer to what [it] cannot perceive") (citation and internal quotations omitted). Other courts have relied on Defenders to vacate listing decisions on substantially the same grounds. See Defenders of Wildlife v. Norton, 239 F. Supp. 2d 9, 20, 20 n. 7 (D.D.C. 2002) (Faulting the Secretary for adopting a "crabbed interpretation of the phrase `significant portion of its range,' which would mean that a species that had once survived in a region, but no longer did, was not entitled to the protections of the ESA," and vacating the rulemaking for failure to explain why the area in which the Canada Lynx can no longer live is not a significant portion of its range.); Defenders of Wildlife v. Sec'y, U.S. Dep't of the Interior, 354 F. Supp. 2d 1156, 1167-69 (D. Or. 2005) (Vacating Gray Wolf rulemaking because the Secretary applied the ESA's five listing factors to the species on its current range without considering or explaining the significance of the wolf's lost historic range); Nat'l Wildlife Fed'n v. Norton, 386 F. Supp. 2d 553, 564-566 (D. Vt. 2005) (vacating a different Gray Wolf listing decision on similar grounds).

This court's narrow remand order instructed the Secretary to identify an appropriate "temporal baseline" for the FTHL, and to consider "whether the lizard's lost historical habitat renders the species in danger of extinction in a significant portion of its range." (Doc. ## 59 at 10; 68 at 2.) The Secretary published the June 26, 2006 notice of withdrawal in response to this court's Order. 71 Fed. Reg. at 36745. The 2006 Finding is fully consistent with Defenders, as discussed in further detail below.

2. The 2006 Finding: Historic Range Analysis

In the 2006 Finding, the Secretary defined the lizard's range so as to include lost habitat, estimated the extent of habitat loss, and then determined whether that lost habitat constitutes a "significant portion" of the FTHL's historic range. The Secretary found that approximately 1,103,201 acres of the lizard's estimated 4,875,624 acre historic range in the United States and Mexico have been permanently lost human-mediated processes. Id. at 36749/3, 36751/1-2. The habitat loss began in the early 20th century, when agricultural and urban development started to encroach upon the lizard's habitat in the southwestern United States and northwestern Mexico. 71 Fed. Reg. at 36751/1.

At the heart of the 2006 Finding is the Secretary's conclusion that the forsaken historical habitat is not biologically, geographically or otherwise significant to the flat-tailed horned lizard. The Secretary found that the approximately 1,103,201 acres lost to agriculture, urbanization and other human-mediated processes is not a significant portion of the lizard's range because 1) the species has persisted despite without that portion of its range; 2) the lost habitat has not caused, and does not threaten to cause, lizard populations to decline throughout the species' current range in the foreseeable future; and 3) there were no particular attributes of the lost habitat that made it any more significant than any other part of the range. Id. These conclusions find ample, if not unanimous, support in the administrative record, and are otherwise reasonable. The Tucson Herpetological Society and its co-Plaintiffs believe otherwise, noting that there are major geographical areas in which the lizard is no longer viable but once was, and faulting the Secretary for not ascribing to the lost acreage the importance it deserves. The parties support their respective positions by reference to Defenders, the controlling decision in this matter. It is to that decision that the court now turns. C. The Defenders Decision

1. The Statutory Puzzle

Under the ESA, a species is "endangered" if "it is in danger of extinction throughout all or a significant portion of its range." 16 U.S.C. § 1532(6). Thus, listing is required if a species is "in danger of extinction throughout all . . . of its range," or if it is "in danger of extinction throughout . . . a significant portion of its range." 16 U.S.C. § 1532(6). The parties agree that the FTHL is not in danger of extinction, or likely to become in danger of extinction in the foreseeable future, throughout all of its range. Instead, the parties dispute whether the species qualifies for ESA protection on the basis of threats to its survival on a "significant portion" of its range, the second of the two disjunctive listing criteria. Though it is central to the definition of both "endangered species" and "threatened species," the Act provides little guidance as to what constitutes "a significant portion" of a species' range. The 1993 proposal to list the flat-tailed horned lizard, 58 Fed. Reg. 62624, and the subsequent withdrawal of that proposal in 1997, 62 Fed. Reg. 37852, presented the Court of Appeals for the Ninth Circuit with an opportunity to "puzzl[e] out the meaning of the phrase." Defenders, 258 F.3d at 1141.

A "threatened species" is one that is "likely to become . . . endangered . . . within the foreseeable future throughout all or a significant portion of its range." 16 U.S.C. § 1532(20).

2. The Defenders Analysis

In Defenders, the Court of Appeals for the Ninth Circuit observed that the dictionary definition of the word "extinct," meaning "has died out or come to an end . . . [h]aving no living representative," is at odds with the more "flexible" definition of "extinct" contemplated by the ESA. 258 F.3d at 1141, 1146. The Act is drafted to prevent species from becoming "extinc[t] throughout . . . a significant portion of its range." 16 U.S.C. § 1532(6). This is "odd phraseology" because, at least in "ordinary usage," a species has not "come to an end" when some individuals are persisting elsewhere. 258 F.3d at 1141. It is also "internally inconsistent," observed the court, "to speak of a species that is `in danger of extinction' throughout a `significant portion of its range[,]' . . . since `extinction' suggests total rather than partial disappearance." Id. After surveying the applicable legislative history, the court resolved the textual ambiguity by concluding that a species need not be threatened with "worldwide extinction" to qualify for protection under the Endangered Species Act. Id. at 1144.

Congress added the "significant portion of its range" language to 16 U.S.C. § 1532(6) to "allow the Secretary more flexibility in [his] approach to wildlife management," the court explained. Id. at 1144. To that end, the definition of "endangered species" allows the Secretary in his discretion to list a species that is threatened in a "significant portion" of its range even if the same species is thriving in other geographic areas. Id. at 1144-45. The Secretary need not formally divide the species into Distinct Population Segments ("DPSs") to accomplish a geographically tailored listing, since the authority is apparent on the face of the statute itself. Conversely, 16 U.S.C. § 1532(6) allows the Secretary to forego listing altogether where the species is experiencing healthy population levels on the "significant portions" of its range, but is in danger of extinction (or already extinct) in areas considered by the Secretary to be of no significance. In that case, the individual States, as opposed to the federal government, would have full authority to use their management skills to insure the proper conservation of the species. Id. at 1144.

The FTHL currently exists in "geographically discrete populations" patchily distributed throughout its historic range in the United States and Mexico. 68 Fed. Reg. at 332/1-2. Despite this habitat fragmentation, the FTHL has not been subdivided into distinct population segments under the FWS policy on the recognition of "discrete" and "significant" populations. Id. at 331, 336/3; 61 Fed. Reg. 4722, 4725 (DPS Policy). Therefore, the lizard could, but need not, be listed throughout all of its range if the Secretary were to conclude, contrary to the facts of this case, that the lizard is "endangered" or "threatened" throughout a "significant portion" of its range. See Edward A. Fitzgerald, Dysfunctional Downlisting Defeated: Defenders of Wildlife v. Secretary, U.S. Department of the Interior, 34 B.C. Envtl. Aff. L. Rev. 37, 65-78 (2007) (analyzing the origins of the DPS policy and FWS' application of that policy in the case of the gray wolf); see also Nat'l Ass'n of Home Builders v. Norton, 340 F.3d 835, 848 (9th Cir. 2003) (reviewing DPS as applied to the cactus ferruginous pygmy-owl in Arizona, and distinguishing the word "significant" in the DPS policy from the word "significant" in the phrase, "a significant portion of its range," 16 U.S.C. § 1532(6)).

When making his listing decision, the Secretary must always consider whether the loss of some of the species' historic range qualifies the species for ESA protection. "[A] species may be extinct `throughout . . . a significant portion of its range' if there are major geographical areas in which it is no longer viable but once was," the court concluded. Id. at 1145 (citing rulemakings in which the Secretary expressly considered whether a species qualified for listing in major geographical areas that were separated from other portions of its historic range by political boundaries, natural geographical features, agricultural or urban development, or DPS classification). If the Secretary finds in his discretion that the lost habitat is of no significance, then he "must at least explain [his] conclusion that the area in which the species can no longer live is not a `significant portion of its range.'" Id. at 1145. Such explanation is particularly important "where, as here, it is on the record apparent that the area in which the lizard is expected to survive is much smaller than its historical range." Id. at 1145.

The Defenders court found a middle ground between the Secretary's construction of 16 U.S.C. § 1532(6), which viewed the statute as "saying the same thing twice," and Defenders' rigid, quantitative interpretation of the phrase, "a significant portion of its range." Id. at 1142-43. This "case by case" approach is faithful to the intent of Congress because it gives substantive meaning to each component of the defined terms, "endangered species," and "threatened species," and requires the Secretary to consider every factor that may militate in favor of listing a species, including the loss of "significant portions" of historic range. Id. at 1143. Because the loss of even a very small percentage of "significant" habitat triggers mandatory listing, the Secretary must explain his assessment of the lost historic range if his rulemaking is to survive judicial review.

II. Standard of Review

Section 706 of the Administrative Procedure Act ("APA") governs this court's review of agency action under the EPA. Nat'l Ass'n of Home Builders, 340 F.3d at 840-41. Under the APA, the reviewing court must set aside agency actions that are "arbitrary, capricious, an abuse of discretion, or otherwise not in accordance with law." 5 U.S.C. § 706(2)(A). An agency action is "arbitrary and capricious" if it

relied on factors which Congress had not intended it to consider, entirely failed to consider an important aspect of the problem, offered an explanation for its decision that runs counter to the evidence before the agency, or is so implausible that it could not be ascribed to a difference in view or the product of agency expertise.
O'Keeffe's v. U.S. Consumer Prod. Safety Comm'n, 92 F.3d 940, 942 (9th Cir. 1996) (quoting Motor Vehicle Mfrs. Ass'n v. State Farm Mut. Auto Ins. Co., 463 U.S. 29, 43 (1983)).

The arbitrary and capricious standard is a "narrow one," Citizens to Preserve Overton Park, Inc. v. Volpe, 401 U.S. 402, 415-16 (1971), and judicial review, even in the summary judgment phase, is "highly deferential." Friends of the Earth v. Hintz, 800 F.2d 822, 831 (9th Cir. 1986). The agency must present a "rational connection between the facts found and the conclusions made," and the "reviewing court may not substitute its judgment for that of the agency." Nat'l Wildlife Fed'n v. U.S. Army Corps of Eng'rs, 384 F.3d 1163, 1170 (9th Cir. 2004); O'Keeffe's, 92 F.3d at 942 (citation omitted). Where "a statute is ambiguous, and if the implementing agency's construction is reasonable, Chevron requires a federal court to accept the agency's construction of the statute, even if the agency's reading differs from what the court believes is the best statutory interpretation." Nat'l Cable Telecomms. Ass'n v. Brand X Internet Servs, 545 U.S. 967, 980 (2005) (citing Chevron U.S.A., Inc., v. Natural Res. Def. Council, 467 U.S. 837 (1984)). The "reviewing court should be at its most deferential in reviewing an agency's scientific determinations in an area within the agency's expertise." Natural Res. Def. Council v. EPA, 863 F.2d 1420, 1430 (9th Cir. 1988) (quoting Balt. Gas Elec. Co. v. Natural Res. Def. Council, 462 U.S. 87, 103 (1983)). The court "presum[es] the agency action to be valid and affirm[s] the agency action if a reasonable basis exists for its decision." Northwest Ecosystem Alliance v. Fish and Wildlife Serv., 475 F.3d 1136, 1140 (9th Cir. 2007) (citation and internal quotations omitted).

If the agency fails to articulate a rational basis for its decision, it is appropriate for a court to remand for reasoned decision-making. See Defenders, 254 F.3d at 1145 n. 11 (Secretary's interpretation of the ambiguous phrase "significant portion of its range" owed no deference under Chevron where agency failed to apply that term). A discretionary agency action may also be remanded for failure to adhere to the "required procedures of decisionmaking" set forth in the Endangered Species Act itself. Bennett v. Spear, 520 U.S. 154, 172 (1997).

III. Plaintiffs' Renewed Challenge

A. The Legal Framework

Congress has delegated authority to the Secretary to parse the enigmatic phraseology at the center of this lawsuit, "in danger of extinction throughout . . . a significant portion of its range." 16 U.S.C. § 1532(6). Under Chevron, the court must defer to the Secretary's construction if he fills the statutory gap in reasonable fashion. 467 U.S. at 865-866. The Secretary's authority is cabined by the Defenders decision, however. In Defenders, the Ninth Circuit held that "a significant portion of its range" has a substantive, historical dimension that the Secretary may not ignore if his rulemaking is to survive judicial review. The Secretary must study the lost historical habitat and determine whether any portion of that lost range constitutes a "significant portion" of the species' range. Defenders, 258 F.3d at 1145. If he finds in his discretion that the lost habitat is of little or no significance, then the Secretary must "at least explain [his] conclusion that the area in which the species can no longer live is not a significant portion of its range." Id. (internal quotations omitted). An explanation is required because a species can, but need not, be extinct "throughout . . . a significant portion of its range" "if there are major geographical areas in which it is no longer viable but once was." Id.

B. The 2006 Finding

The 2006 Finding complies with the ESA, the Defenders decision, and this court's remand Order. The Secretary filled the statutory gap in 16 U.S.C. § 1532(6) by construing the phrase, "a significant portion of its range" so as to encompass biological significance as well as geographical significance. (Doc. # 114 at 23.) He then cured the deficiency in the 2003 Finding by delineating the lizard's lost historical habitat and evaluating the habitat lost since the early 20th century using the criteria identified by him. The rulemaking is analyzed in greater detail below.

1. Setting the Temporal Baseline and Delimiting Lost Habitat

First, the Secretary chose a point in time at which to examine the lizard's range. He resolved to study habitat loss occurring over the past 100 years, a time frame that constitutes "the available recorded historical information" in this area. 71 Fed. Reg. at 36749/3. Over the past century, "[a]pproximately 1,103,201 [acres of historic habitat] have been lost, nearly entirely within . . . the Coachella Valley, and Mexicali and Yuma areas," the Secretary concluded. Id. at 36751/1. In the Mexicali area, agricultural development caused habitat loss extending from Mexicali south to the Gulf of California and east to the Colorado River. "This block of lost habitat is contiguous . . . with the block of lost habitat in the Yuma area," the Secretary explained. Id. at 36751/1. "The block of habitat that encompasses northeastern Baja California Note and southwestern Arizona is the largest block of lost habitat," he averred. Id. at 36751/1.

The Secretary consulted his own "knowledge of habitat preference for the species, early descriptions of habitat before development, and early museum records" to construct his "estimation of the broad-scale historical range." 71 Fed. Reg. at 36747/1.

2. The Lost Habitat Is Insignificant

After setting a temporal baseline and defining the subject area, the Secretary proceeded to evaluate the significance of the lost historical habitat. He concluded that the Coachella Valley area, including its lost associated habitat, was insignificant because of its small size relative to the overall range of the species, the high level of fragmentation due to human development, the lack of genetic, behavioral, or ecological differentiation, and the small size and importance of the population in general. Id. at 36751/1; 68 Fed. Reg. at 348/1-2 (same in 2003 Finding). The remaining parcels of lost historical habitat areas near Mexicali and Yuma were also deemed insignificant. "These habitat areas were likely converted to agriculture early in the 20th century," and are not a significant portion of the lizard's historic range because of their "small size relative to the entire range and because this area has been lost to agriculture for nearly a century and the flat-tailed horned lizard has persisted" in surrounding habitats, such as East and West Mesa, and the Yuha Basin, for generations. 71 Fed. Reg. at 36751/1. The "lost habitat was not significant enough to lead to the species' extirpation within intact habitat through edge effects or fragmentation," the Secretary observed. Id. at 36751/2.

Not only has the species persisted for nearly a century in the face of the steady habitat destruction, but the size of existing lizard populations has not declined and is not likely to decline in the foreseeable future because of the loss of 1,103,201 acres of historic range, the Secretary found. Id. at 36751/2-3. After surveying the "available data concerning population abundance, trends, and threats," the Secretary concluded that yesterday's conversion of suitable habitat to agriculture in the Mexicali and Yuma areas is not significant to the survival of today's lizards. Id. at 36751/3. This is the historical analysis that Defenders and this court demanded.

The 2003 Rangewide Management Strategy suggests that "human activities have resulted in the conversion of roughly 49% of the historic FTHL habitat to other uses, such as agriculture and urban development." (Supp. AR doc. # 329 at 2999); 68 Fed. Reg. at 348/1 (similarly concluding that "[m]uch of the species' habitat has been lost, fragmented, or degraded").

Finally, the Secretary broadened his inquiry to consider whether "[t]here were [any] attributes or specific uses of the lost habitat by flat-tailed horned lizards that made it any more significant than any other habitat." Id. at 36751/2. He determined that "there was nothing of the sort." Id. at 36751/2. For example, although the lost habitat in and around Mexicali and Yuma "is situated between the Arizona-Sonora and California-Baja California Norte populations," the significance of the lost habitat as a biological corridor is minimal because "the Colorado River already isolated these populations to some degree," and "[m]uch of this habitat has been permanently lost due to urbanization and/or flooding of the Salton Sea." Id. at 36751/2. Even where the desert floor has not been paved over, recolonization is all but impossible because "most agricultural fields are isolated from existing flat-tailed horned lizard populations by irrigation canals." Id. at 36751/2. Therefore, the Secretary does "not anticipate [that] any significant amount of previously lost habitat could become viable habitat in the future." Id. at 36751/2. It is for this reason that the lost habitat is not a significant portion of the lizard's historic range, despite its location at the nexus of once connected but now permanently isolated habitat areas.

As an aside, the Secretary observed that "additional conversion of flat-tailed horned lizard habitat to agriculture" in the Imperial Valley and elsewhere along the Colorado River is not likely because of the limited "availability of water for irrigation." Id. at 36751/2.

C. Plaintiffs' Arguments for Remand

Plaintiffs specifically urge the court to vacate the 2006 Finding because of its reliance (both explicit and implicit) on the lizard's persistence in its current range, its refusal to consider new threats to extant lizard populations, and its modification of the lizard's historic range in California and in Mexico. (Doc. ## 98; 110.) These contentions are without merit. Each of Plaintiffs' arguments will be addressed in turn below.

1. Lizard Persistence is a Valid Criterion

Plaintiffs' first challenge to the 2006 Finding misses the mark entirely. Defenders prohibits the Secretary from de-listing the lizard solely because it is persisting as a whole in its current range, but it does not preclude the Secretary from taking the lizard's persistence into account when evaluating the significance of the lost habitat. Lizard persistence cannot be the only criterion of significance, but it can support a listing decision if otherwise supported and explained. Indeed, the Ninth Circuit encouraged the Secretary to consider the "viability of the species as a whole," when assessing the significance of lost habitat so as to "allow listing of species where areas of range vital to the species' survival-but not the majority of the range-face significant threats." Defenders, 258 F.3d at 1143, 1143 n. 9.

In this case, the Secretary assessed the quantum of historical range now lost to species and drew an inference about the significance of the lost habitat from the fact that the lizard has survived for almost a century in spite of that habitat destruction. 71 Fed. Reg. at 36748/1. "This continued persistence over a span of nearly 100 years [and more than 25 generations] is a strong indication that the species will continue to persist into the foreseeable future despite the loss of historical habitat," the Secretary concluded. Id. at 36751/1. This inference marked the beginning, not the end, of the Secretary's analysis. Lizard persistence was but "one portion of a broader assessment" that "ultimately led the Service to the conclusion that the lost historical habitat was not significant." (Doc. # 114 at 14-16.)

2. Beyond Lizard Persistence

Plaintiffs contend that the "broader assessment" testified to by the Secretary is unworthy of credence because it simply repackages the lizard persistence argument in different terms. Even if Defenders did prohibit the Secretary from taking the lizard's persistence into account when evaluating the significance of the lost historical range, which it does not, this argument is foreclosed by the text of the 2006 Finding itself. After his discussion of lizard persistence, the Secretary went on to assess the significance of the lost historical habitat in terms of its size relative to the species' overall range (it is "relatively small"), its capacity for re-colonization (the habitat is "permanently lost"), its contribution to gene flow (the habitat was not a likely biological corridor even before its destruction), and its impact upon the size of extant lizard populations (the lizard has not been extirpated "within intact habitat through edge effects or fragmentation," and lizard populations today have not significantly declined because of the habitat loss). 71 Fed. Reg. at 36751/2-3. The Secretary's qualitative and quantitative assessment of the significance of the lost habitat went well beyond lizard persistence. Thus, the rulemaking may stand because, consistent with the essential holding of Defenders, the Secretary has explained why in his expert judgment "the area in which the species can no longer live is not a `significant portion of its range.'" 258 F.3d at 1145. Plaintiffs have failed to generate a triable issue as to whether that conclusion was "arbitrary, capricious, an abuse of discretion, or otherwise not in accordance with law." 5 U.S.C. § 706(2)(A). The Secretary's analysis is fully consistent with Defenders and Congress' intent when enacting the ESA: to "provide a means whereby the ecosystems upon which endangered species and threatened species depend may be conserved." 16 U.S.C. § 1531(b).

The Secretary's discussion of the lizard's ability to survive habitat destruction and degradation is not the fatal flaw Plaintiffs make it out to be. In fact, it is difficult to imagine how the Secretary could have complied with Defenders without evaluating lizard population levels in the current range, which is smaller and more fragmented than the historic range. For if the Secretary had found that the loss of historic range was significant in the sense that the species is somehow threatened by its absence on its current range, then listing would be required as he candidly admits. (Doc. # 114 at 16.) The "best scientific and commercial data available" led the Secretary to this conclusion, however. 16 U.S.C. § 1533(b)(1)(A); 71 Fed. Reg. at 36751/2 ("There were no attributes or specific uses of the lost habitat . . . that made it any more significant than any other habitat."). Instead, the Secretary concluded that listing is not required because the species has adapted to the irrevocable curtailment of its historic range and is surviving in its modern-day milieu (the 2006 Finding), and the species is not likely to suffer significant habitat or population decline on its current range in the foreseeable future (the 2003 Finding). Most importantly, the Secretary explained why the area in which the lizard can no longer live is not significant to the species, whether in terms of lizard biology, desert geography, or for any other reason. This is all that the ESA and the Defenders decision requires from the agency entrusted with the listing decision.

Plaintiffs seek to undermine the Secretary's conclusion by pointing to scientific evidence tending to show that the lost habitat is "a significant portion of [the lizard's] range." ( See doc. # 110 at 16-17 (discussing harmful genetic and geographic isolation of extant lizard populations); Supp. AR doc. ## 232 at 1958 ("the loss of habitat . . . caused by human mediated processes is significant to the species" from a genetic perspective); 329 at 3012-13 (flat-tailed horned lizards have "unusually large home ranges for lizards their size," and studies suggest that the FTHL "may not maintain distinct home ranges, but instead shift their area of use through time")). Plaintiffs infer from these studies that the flat-tailed horned lizard, like the grizzly bear, will be unable to survive in the "detached islands of population" to which it has been relegated. Aldo Leopold, A Sand County Almanac 198 (Oxford Univ. Press 1989) (1949). Their apprehension is not unfounded. But the scientific evidence is far from conclusive, and the court is not empowered by the APA to "substitute its judgment for that of the agency." Overton Park, 401 U.S. at 416. Just as the documented threats to the lizard on its current range did not compel the Secretary to list the species in the 2003 Finding, so too is the Secretary privileged to form his own expert judgment about the significance of the lost habitat in 2006 Finding, provided his conclusions are reasonable and have been explained. Here, the Secretary assessed the available scientific evidence (including the evidence of diminished gene flow) and concluded, reasonably and with ample record support, that the lost habitat is not a "significant portion" of the lizard's range. The Secretary need not list the lizard solely because there are major geographical areas in which it is no longer viable but once was, Defenders, 258 F.3d at 1145, but he must explain why the historic acreage is not a "significant portion" of the lizard's fragmented range. 68 Fed. Reg. at 332/1 ("The distribution of the [FTHL] is not contiguous across its range, because of fragmentation by large-scale agricultural and urban development."). The 2003 Finding failed the Defenders test because it simply ignored the substantive, historical dimension of the phrase, "a significant portion of its range," and assumed without explanation that large swaths of lost habitat were of no significance at all. The 2006 Finding suffers from no such defect.

3. Record Support For Lizard Persistence

Plaintiffs next mount a two-prong attack upon the evidentiary sufficiency of the Secretary's conclusions regarding lizard persistence in its current range. One prong of the attack may be readily disposed of by reference to the court's remand Order. The second prong, which is premised upon scientific uncertainty about the population dynamics of the FTHL, misapprehends the nature of judicial review and is also without merit.

i. Failure to Evaluate New Data

Conceding for the sake of argument that lizard persistence is a valid criterion under the Defenders standard, Plaintiffs impugn the record support for the Secretary's conclusions. Plaintiffs specifically fault the Secretary for failing to "evaluate new threats, re-evaluate expanding threats, and analyze new information to assess the lizard's ability to persist in its current range." (Doc. # 115 at 6.) However, as discussed above, this court previously upheld the Secretary's application of the five listing criteria to extant lizard populations both within and outside of the five management areas. (Doc. # 59 at 11-15.) The Secretary erred in the 2003 Finding not in his assessment of threats to the species on its curtailed range, but "by failing to evaluate the lost historical habitat and whether that lost habitat was a significant portion of the range." (Doc. # 68 at 1.) The court authorized Plaintiffs to challenge the Secretary's rulemaking by way of supplemental complaint, but only "on grounds not rejected in the court's previous orders." (Doc. # 90 at 12.) Plaintiffs' attempt to revive their challenge to the Secretary's threat assessment is contrary to court order and merits no further discussion.

Though the court did not require it, the Secretary responded in the 2006 Finding to comments relating to the construction of the Yuma Area Service Highway, the All-American Canal, alternative energy proposals, increased border patrol activity, and rising incidence of OHVs, among other issues. 71 Fed. Reg. at 36748-49. This portion of the 2006 Finding supplements the Secretary's original discussion of potential threats to lizard persistence with updated data and reference to the 2003 Rangewide Management Strategy, but it does not change the substance of his analysis. The "[c]ommentators did not provide new information or data . . . on additional threats not already considered in the January 3, 2003, withdrawal," the Secretary observed. Id. at 36748/2. Having revisited the question, the Secretary remains persuaded that these factors do not pose a significant threat to the lizard in the foreseeable future. The court must defer to the Secretary's reasoned judgment. Northwest Ecosystem Alliance, 475 F.3d at 1140 (citation and internal quotations omitted). The contradictory portions of the administrative record identified by Plaintiffs, such as a dissenting email from a FWS biologist (Supp. AR doc. # 103), highlight ongoing differences in opinion but do not undermine the legal sufficiency of the Secretary's conclusion, which finds ample support in both the 2003 and the 2006 Findings.

ii. Uncertain Population Dynamics

Plaintiffs seize upon the scientific uncertainty surrounding the population dynamics of the FTHL in an effort to undermine the Secretary's conclusions regarding the viability of the lizard in the near and long term. (Doc. # 115 at 5.) This argument misapprehends the nature of judicial review of agency action under the Endangered Species Act. The ESA mandates that the listing decision be made "solely on the basis of the best available scientific and commercial data available." 16 U.S.C. § 1533(b)(1)(A). This "best available science" standard requires "far less than conclusive evidence" or "absolute scientific certainty." Defenders of Wildlife v. Babbitt, 958 F. Supp. 670, 680 (D.D.C. 1997). Rather, the standard requires the agency to consider the scientific information presently available. Id. Deference to an agency's scientific and technical expertise dictates that agency action must be upheld as long as the agency has "considered the relevant factors and articulated a rational connection between the facts found and the choice made." Baltimore Gas Elec., 462 U.S. at 105.

In this case, a flat-tailed horned lizard Population Viability Analysis ("PVA") was conducted in 1998. The results of the study were inconclusive. The PVA "provided no estimate of the minimum viable population size and did not determine whether populations contained in the [management areas] were viable." 68 Fed. Reg. at 334/3. In fact, the conservation team noted that the "greatest value of this exercise is to illuminate the paucity of population data for this species." (Supp. AR doc. # 28 at 577.) Though the scientists expressed "[u]ncertainty in the interpretation of the PVA results," the study nevertheless provided "some insight into the mechanisms of FTHL population dynamics." ( Id.; Supp. AR doc. # 329 at 3013.) For example, the PVA "illustrated the sensitivity of flat-tailed horned lizards population viability to certain factors, particularly changes in mortality and fecundity." 68 Fed. Reg. at 334/3. On the basis of these preliminary insights, the authors of the Rangewide Management Strategy opined that each of the management areas contains viable FTHL Populations. (Supp. AR doc. # 329 at 3013.)

In the 2006 Finding, the Secretary evaluated the inconclusive results of the PVA in light of "recent estimates of [FTHL] population sizes" conducted both within and outside of the five management areas. 71 Fed. Reg. at 36751/2-3. He concluded on the basis of these estimates that "the species remains viable throughout most of its current extant range" in California, Arizona, and Mexico. Id. at 36751/3. The Secretary explained his finding as follows,

[T]he available data concerning population abundance, trends, and threats do not suggest, outside the Coachella Valley, that flat-tailed horned lizard populations are declining in any of the geographic areas, or that because of [] habitat loss and degradation the species is likely to become endangered within the foreseeable future. . . . Recent estimates of population sizes . . . [show] no large decline in population size occurred between 2003 and 2005 in areas for which we have more than one year of data.

71 Fed. Reg. at 36751/2-3.

Plaintiffs do not suggest that more conclusive scientific data on FTHL population dynamics are presently available. Rather, they direct the court's attention to the dissenting opinions of peer reviewers, 68 Fed. Reg. at 340-41, and lizard experts such as Dr. Wendy Hodges, a Plaintiff in this action, who believes that "the loss of habitat . . . caused by human mediated processes is significant to the species" from a genetic perspective. (Supp. AR doc. # 232 at 1958.) That some experts have concluded that the lizard is not viable in its current range because of the habitat loss does not preclude the Secretary from finding that lizard is viable, provided he presents a "rational connection between the facts found and the conclusions made." Nat'l Wildlife Fed'n, 384 F.3d at 1170; Marsh v. Oregon Natural Resources Council, 490 U.S. 360, 378 (U.S. 1989) ("When specialists express conflicting views, an agency must have discretion to rely on the reasonable opinions of its own qualified experts even if, as an original matter, a court might find contrary views more persuasive."). The ESA does not require conclusive evidence of minimum viable population size. Unanimous scientific consensus is not a prerequisite to lawful rulemaking. Though some may disagree with his conclusions, the Secretary's assessment of inconclusive data relating to the lizard's viability on its current range is supported by the "best available science" and has been adequately explained on this record.

4. Exclusion of California Habitat and Inclusion of Mexican Habitat

Finally, Plaintiffs challenge the Secretary's decision to modify the species' historic range by excluding approximately 1,309,409 acres in the vicinity of California's Salton Sea, and adding two blocks of uncertain acreage in Mexico. 71 Fed. Reg. at 36745/3; 36749/3-36750/1. Plaintiffs charge the Secretary with "arbitrarily" changing "direction in the midst of the administrative process," decreasing "the percentage of lost historical habitat," and "creating the appearance that lost habitat is insignificant" thereby. (Doc. # 115 at 8.) The 2006 Finding marks the first time that the Secretary has defined the species' historic range in this particular manner. But a change of direction is not fatal to a rulemaking where, as here, the modifications are reasonable and have been explained.

The Secretary has discretion to delimit the historic range of the FTHL in accordance with his expert judgment and the "best available science" standard. Defenders, 258 F.3d at 1145. The court must determine whether the Secretary's delineation is "based on a consideration of the relevant factors and whether there has been a clear error of judgment." Overton Park, 401 U.S. at 416. Where the agency reverses course, it "will be required to show not only that its new policy is reasonable, but also to provide a reasonable rationale supporting its departure from prior practice." Seldovia Native Ass'n v. Lujan, 904 F.2d 1335, 1345 (9th Cir. 1990) (citing Motor Vehicle Mfrs., 463 U.S. at 29). "[I]f the agency adequately explains the reasons for a reversal of policy, change is not invalidating, since the whole point of Chevron is to leave the discretion provided by ambiguities of a statute with the implementing agency." Nat'l Cable Telecomms. Ass'n, 545 U.S. at 980 (citation and internal quotations omitted). "Unexplained inconsistency is . . . reason for holding an interpretation to be an arbitrary and capricious change from agency practice under the Administrative Procedure Act," but a reasoned departure from prior practice in response to evolving scientific consensus or changed factual circumstances is not. Id. ("An initial agency determination is not instantly carved in stone. On the contrary, the agency . . . must consider varying interpretations and the wisdom of its policy on a continuing basis.") (citations and internal quotations omitted). Therefore, neither the ESA nor the APA prohibits the Secretary from "changing direction in the midst of the administrative process," as Plaintiffs mistakenly contend. It would be strange indeed to fault the Secretary for refining his estimation of the lizard's historic range when this is precisely what the court required of him on remand.

i. The Exclusion of the Salton Basin

a. Not Historical Habitat

The Secretary has determined that 1,309,409 acres of previously included habitat within and surrounding the Salton Sea (the "Salton Basin") was not historical habitat at all. 71 Fed. Reg. at 36749/3-50/1. The available historical information indicates that the Salton Basin has been flooded by water from the Colorado River on at least 15 occasions since 700 AD. Id. at 36745/3-46/1; 36750/1. The water overflowed into the Salton Basin area to form historic Lake Cahuilla. Id. at 36750/1. "Flat-tailed horned lizards were likely killed during floods as water rushed into the basin and recolonization occurred as the water evaporated." Id. at 36750/1. The Secretary goes on to observe, "Even when the lake was dry, a large portion of the dry lakebed was likely unsuitable habitat for flat-tailed horned lizards." Id. at 36750/1. "Much of the area within the former Lake Cahuilla lakebed was not only intermittent, but low-quality habitat for the . . . lizard, particularly the central salt deposits and saltier, less sandy portions of the Atriplex community." Id. at 36750/3. The Secretary excluded the Salton Basin acreage because it provided only intermittent, low-quality habitat for the species. Id. at 36750/1. The change of course, which was foreshadowed to some extent by the Secretary's discussion in the 2003 Finding about the "ephemeral" nature of this habitat, is reasonable and has been adequately explained. 68 Fed. Reg. at 332/2.

b. The Habitat Was Not Significant

Even if the Salton Basin were considered historical habitat, the Secretary avers that the region would still be excluded from the lizard's range because of its limited ability to support viable FTHL populations. Scientists have found it difficult to study historic Lake Cahuilla. They have struggled to define, for example, "the precise proportion of the lakebed that historically was habitat, and the quality of that habitat," due to unknowns such as the precise proportions of specific plant communities in the Salton Basin and the patterns of windblown sand deposition. 71 Fed. Reg. at 36750/3. "Despite the difficulty in accurately determining historic conditions in the dry lakebed," the Secretary found "that it contained only a limited amount of suitable habitat, most of which is likely to have been marginal at best. " Id. What is more, the Secretary observed that "recent work on the genetics of the flat-tailed horned lizard suggests that gene flow across the lakebed between the east and west sides of the Salton [Basin] was low even before the current fragmentation due to development and agriculture." Id. The lack of "substantial gene flow across the Imperial Valley since the drying of Lake Cahuilla . . . and prior to human development" tends to support the Secretary's conclusions about the significance of this area. Id. "Thus," the Secretary reasonably concluded, "even if the lakebed were considered historical habitat, it would not be significant to the species." Id. The Secretary's decision to include low-quality habitat of a different character in areas such as the Yuha Basin, Ocotillo Wells, or Borrego Badlands, does not preclude him from excluding the marginal acreage at issue here. (Doc. # 115 at 12-13.) Congress vested the Secretary with authority to make such scientific judgments. The Secretary's conclusions will not be disturbed if, after searching inquiry, the court finds the policy reversal to be reasonable and adequately explained. Having reviewed all portions of the original and supplemental record identified by Plaintiffs, the court finds that the Secretary's exclusion of the Salton Basin as providing only "intermittent, low-quality [lizard] habitat" was not arbitrary or capricious or otherwise in violation of the ESA or the APA. 71 Fed. Reg. at 36750/1.

ii. Addition of Mexican Habitat

In the 2003 Finding, the Secretary described the lizard's Mexican habitat as extending "from the international border in the Yuha Desert in California, south to the Laguna Salada in Baja California, and from the international border in the Yuma Desert in Arizona, south and east through the Pinacate Region to the sandy plains around Puerto Peñasco and Bahia de San Jorge." 68 Fed. Reg. at 332/1. The 2006 Finding contains a substantially identical description of the Mexican habitat, except that the Secretary changed his description of the range south of the Yuha Desert by extending the species' habitat "along the west side of Laguna Salada" in Baja California. 71 Fed. Reg. at 36745/3. The precise number of acres appended to the species' Mexican range is not disclosed on the face of the 2006 Finding.

Rather than explaining the change in policy directly, as he did with the Salton Basin, the Secretary justified the change to the Mexican habitat by way of a citation to the Rangewide Management Strategy. Id. at 36746/2, 36749/3. The Secretary relied upon the 2003 RMS because it "contain[s] updated information on the current and historical range of the species in the United States and Mexico . . . in geographical information system (GIS) format," and represents the "most recent analysis of the species' range in the United States and Mexico." Id. at 36746/1-2; ( see Supp. AR doc. # 329 at 3008 (depicting the lizard's current and historical Mexican range); 3006 (describing the Mexican range)). An early draft of the 2006 Finding explains that "approximately 50 miles" of new acreage "south of the northern lobe of Laguna Salada," along with "approximately 10-20 miles" of new range "south and east along the coast of the Gulf of California past Puerto Peñasco," were added to the lizard's range because of a sighting of the species in each area, and because of the presence of suitable habitat." (Supp. AR doc. # 126 at 1141.) This language does not appear in the final version of the 2006 Finding, however.

Plaintiffs oppose this conclusion by observing that the "leading Mexican study" from 2002 "concludes there is a [probable] absence of lizard in the Gran Desierto," and also "reject[s]" the idea that the lizard's distribution extends south of the Laguna Salada. (Doc. # 115 at 9) (citing Supp. AR doc. # 297 at 2603).) However, the conflicting assessment offered by the Mexican study is of little moment where, as here, the Secretary has adequately explained his decision to credit the "updated information" contained in the 2003 Rangewide Management Strategy instead. A consistent theme in the Secretary's rulemakings is that "the distribution of the species in Mexico is poorly understood because few surveys have been conducted" there. 68 Fed. Reg. at 332/2. That the scientific community's understanding of the lizard's historic and current range in Mexico "could benefit from further surveys and/or modeling," does not preclude the Secretary from drawing reasonable inferences from the best available data, in this case the 2003 Rangewide Management Survey. (Supp. AR doc. # 329 at 3007.)

While the Secretary explained his reliance upon the 2003 Rangewide Management Strategy to support his delineation of the species' Mexican range in general, 71 Fed. Reg. at 36749/3, he did not explain why, or by how much, he extended the Laguna Salada range in the 2006 Finding, and he did not disclose the addition of new habitat along the Gulf of California at all. Instead, the court was required to comb through the administrative record, including prior versions of the 2006 Finding and email correspondence between FWS biologists, to understand the extent of the new acreage and the specific reasons for its inclusion. (Doc. ## 110 at 18-20; 115 at 9-10.) The court cannot "be compelled to guess at the theory underlying the agency's action; nor can a court be expected to chisel that which must be precise from what the agency has left vague and indecisive." SEC v. Chenery Corp., 332 U.S. 194, 196-97 (1947). The Secretary's failure to explain the changes to the Mexican habitat on the face of the 2006 Finding prevents the court from upholding that portion of his rulemaking. The court "cannot supply a reasoned basis to make up for deficiencies in the agency's decision," nor can it "defer to the FWS when its path of reasoning is not clear." Nat'l Ass'n of Home Builders, 340 F.3d at 849.

However, the Secretary's failure to explain the addition of new Mexican habitat is not material to the 2006 Finding because the Secretary's overall assessment of the size of the Mexican range relative to that north of the international border did not change when the new territory was included. In the 2003 Finding, which does not include the new acreage in the vicinity of the Laguna Salada and the Gulf of California, the Secretary found that "approximately 59 percent of the species['] range occur[s] in Mexico. 68 Fed. Reg. at 332/2. The 2007 Finding, which includes that range by reference to the 2003 RMS, contains the same assessment. 71 Fed. Reg. at 36746/1. The expansion of the Mexican range in the 2007 Finding was not substantial enough to cause the Secretary to alter his estimation of the relative size of the Mexican habitat. What is more, the challenged acreage south of the international border played no discernible role in the Secretary's assessment of the significance of the Mexican range or of the lost historical range as a whole. Id. at 36750-51. Therefore, the unexplained inclusion of the new Laguna Salada and Gulf of California territory, though to be disregarded, does not warrant remand.

Plaintiffs observe (apparently for the first time) that the Secretary in two prior rulemakings contradictorily averred, "About 29 percent of the lizard's historic range is in Mexico." 58 Fed. Reg. at 62624 (1993 proposed rule); 62 Fed. Reg. at 37853/1 (same in 1997 withdrawal with citation to Johnson and Spicer (1985)). The inconsistency between this figure and the 59 percent figure referenced in the 2003 and 2006 withdrawal notices is explained on the record, though not in the rulemakings themselves. FWS biologist Jim Rorabaugh explained that the 29 percent figure can be attributed to out-dated reports and speculation, while the 59 percent figure is more solidly grounded on empirical analysis and the Rangewide Management Survey. (Supp. AR doc. # 125 at 1133.)

IT IS THEREFORE ORDERED that Plaintiffs' Motion for Summary Judgment (doc. # 109) is denied and Defendants' Cross-Motion for Summary Judgment (doc. # 113) is granted.

IT IS FURTHER ORDERED, based on this Order and the Order of August 30, 2005 (doc. # 59), that the Clerk enter judgment in favor of Defendants and that Plaintiffs take nothing. The Clerk shall terminate this action.


Summaries of

Tucson Herpetological Society v. Kempthorne

United States District Court, D. Arizona
Jul 12, 2007
No. 04-CV-00075-PHX-NVW (D. Ariz. Jul. 12, 2007)
Case details for

Tucson Herpetological Society v. Kempthorne

Case Details

Full title:Tucson Herpetological Society, et al., Plaintiffs, v. Dirk Kempthorne, et…

Court:United States District Court, D. Arizona

Date published: Jul 12, 2007

Citations

No. 04-CV-00075-PHX-NVW (D. Ariz. Jul. 12, 2007)