FISHER v. SALAZARNo. 3:07cv530-WS.
656 F.Supp.2d 1357 (2009)
Paul and Gayle FISHER and Perdido Key Property Rights, Inc., a Florida corporation, Plaintiffs,
Ken SALAZAR, in his official capacity as Secretary of the Interior; U.S. Department of the Interior; United States Fish and Wildlife Service; and Rowan Gould, in his official capacity as Acting Director, United States Fish and Wildlife Service, Defendants.
Ken SALAZAR, in his official capacity as Secretary of the Interior; U.S. Department of the Interior; United States Fish and Wildlife Service; and Rowan Gould, in his official capacity as Acting Director, United States Fish and Wildlife Service, Defendants.
United States District Court, N.D. Florida, Pensacola Division.
August 4, 2009.
Nicholas M. Gieseler, Pacific Legal Foundation, Stuart, FL, for Plaintiffs.
Clifford Eugene Stevens, Jr., U.S. Dept of Justice, Washington, DC, Robert Del Stinson, U.S. Attorney, Tallahassee FL, for Defendants.
ORDER GRANTING DEFENDANTS' MOTION FOR SUMMARY JUDGMENT
WILLIAM STAFFORD, District Judge.
The plaintiffs, Paul and Gayle Fisher (the "Fishers") and Perdido Key Property Rights, Inc. ("PKPR") (collectively, "Plaintiffs"), filed this action alleging that the defendants (collectively, "Defendants"), through the United States Fish and Wildlife Service ("FWS"), designated critical habitat for the Perdido Key beach mouse "without adequate delineation or justification and without sufficient analysis of the economic and other impacts of the designation." Before the court at this time are the parties' cross-motions for summary judgment. Docs. 28 & 35. The motions have been fully briefed, docs. 29, 30, 36, 37, 40, 41 & 48; and the parties have been advised (doc. 57) that the motions would be taken under advisement as of a date certain, For reasons explained below, Defendants' motion will be granted.
The Endangered Species Act of 1973 (the "ESA" or the "Act"), 16 U.S.C. §§ 1531-1544, was enacted by Congress "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 defines the terms "conserve" and "conservation" as "the use of all methods and procedures which are necessary to bring any endangered species or threatened species to the point at which the measures provided pursuant to [the Act] are no longer necessary." Id. at 1532(3). As noted by the Fifth Circuit in Sierra Club v. United States Fish and Wildlife Serv.,
Generally regarded as "the most comprehensive legislation for the preservation of endangered species ever enacted by any nation," Tennessee Valley Auth. v. Hill,
The ESA requires the FWS to maintain a list of both endangered and threatened species. 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). A species is "threatened" if it is "likely to become an endangered species within the foreseeable future throughout all or a significant portion of its range." Id. at § 1532(20). Determinations as to
Concurrently with making a determination that a species should be listed as endangered or threatened, the FWS is required to designate—"to the maximum extent prudent and determinable"—the listed species' critical habitat. Id. at § 1533(a)(3)(A).
Id. at § 1532(5)(A). The ESA requires the FWS to make the designation decision "on the basis of the best scientific date available and after taking into consideration the economic impact, and any other relevant impact, of specifying any particular area as critical habitat." Id. at § 1533(b)(2). The FWS may "exclude any area from critical habitat if [it] determines that the benefits of such exclusion outweigh the benefits of specifying such area as part, of the critical habitat, unless [it] determines, based on the best scientific and commercial data available, that the failure to designate such area as critical habitat will result in the extinction of the species." Id.
Section 7(a)(2) of the ESA requires federal agencies to consult with the FWS—in what are known as "Section 7" consultations—to "insure that any action authorized, funded, or carried out by such agency... is not likely to jeopardize the continued existence of any endangered species or threatened species or result in the destruction or adverse modification of [designated critical] habitat of such species." Id. at § 1536(a)(2). Thus, when a species is listed and regardless of whether critical habitat has been designated, an agency must consult with the FWS when an action might "jeopardize the continued existence of any endangered species or threatened species." If critical habitat has been designated, an agency must consult with the FWS when an action might result in the "destruction or adverse modification" of that designated habitat. Actions that have no federal nexus, that are not authorized, funded, or carried out by a federal agency, do not require a Section 7 consultation.
Under FWS regulations promulgated in 1986, the jeopardy standard relevant to listing—"to jeopardize the continued existence of a species—means "to engage in an action that reasonably would be expected, directly or indirectly, to reduce appreciably the likelihood of both the survival and recovery of a listed species." 50 C.F.R. § 402.02. The standard relevant to
Once a species has been listed as endangered, and regardless of whether critical habitat for that species has been designated, the ESA and the regulations promulgated thereunder prohibit certain actions taken by any person that may adversely affect the listed species. 16 U.S.C. § 1538. Among other things, the Act makes it unlawful for any person to "take" an endangered species. Id. at § 1538(a)(1)(B). The term "take" means "an act which actually kills or injures wildlife," including any act that may include "significant habitat modification or degradation where it actually kills or injures wildlife by significantly impairing essential behavioral patterns, including breeding, feeding or sheltering." 50 C.F.R. § 17.3; see also 16 U.S.C. § 1532(19).
The ESA may allow "the taking [of an endangered species] otherwise prohibited by [the Act] if such taking is incidental to, and not the purpose of, the carrying out of an otherwise lawful activity." 16 U.S.C. § 1539(a)(1)(B). If "incidental take" is expected during the development of land, whether or not the land is designated as critical habitat, the landowner must apply for a permit from the FWS. An applicant for an incidental take permit must submit to the FWS a conservation plan, specifying—among other things—the impacts likely to result from a taking, the steps to be taken to minimize and mitigate those impacts, and the funding that will be available to implement those steps. Id. at § 1539(a)(2)(A). Because incidental take becomes a factor based on a species' presence on land, the FWS has a specific protocol for determining the presence or absence of beach mice. In the words of the FWS:
Final Rule, 71 Fed. Reg. 60238, 60241 (Oct. 12, 2006). If presence of beach mice is documented on private lands where no critical habitat designation exists, private landowners are nonetheless required to minimize impacts on, the beach mouse and, where applicable, to obtain permits and perform mitigation. On the other hand, according to FWS, neither a permit nor mitigation is required for property owners who rebuild within the footprint of previous developments.
The Perdido Key beach mouse can be found in the wild only on Perdido Key, a barrier island consisting of 2,943 acres of coastal land from Perdido Pass in Alabama to Pensacola Bay in Florida. Historically, this mouse ranged the entire length of Perdido Key (16.9 miles), inhabiting burrows dug into primary, secondary, and higher-elevation scrub dunes. By 1980, the effects of human development, coupled with a 1979 category 4 hurricane, led to the extirpation of all but a single colony of thirty mice living at Gulf State Park at the westernmost end of Perdido Key.
The Perdido Key beach mouse was first listed as endangered on June 6, 1985. Critical habitat—consisting mainly of primary and secondary dunes—was designated
The FWS was petitioned to revise critical habitat on Perdido Key in 1991 by the Alabama Conservancy and again in 1999 by the Sierra Club and Biodiversity Legal Foundation. On both occasions, the FWS concluded that revision was warranted based on new information regarding the beach mouse's use of scrub habitat, habitat that had not been previously designated. See Notice of Intent, 58 Fed. Reg. 33606, 33606 (June 18, 1993); Notice of Finding, 65 Fed. Reg. 57800 (Sept. 26, 2000). On neither occasion, however, did the FWS follow through with a rule revising the designation of critical habitat. Consequently, in 2003, the Sierra Club and Biodiversity Legal Foundation filed suit in the United States District Court for the Southern District of Alabama, seeking an order requiring the FWS to revise its designation of critical habitat for the Perdido Key beach mouse. The action was voluntarily dismissed in early 2006 after the FWS published a proposed rule revising the designation. Proposed Rule, 70 Fed. Reg. 74426 (Dec. 15, 2005). A final rule designating revised critical habitat was published on October 12, 2006. Final Rule, 71 Fed. Reg. 60238 (Oct. 12, 2006).
The 2006 final rule designates 1300 acres — 991 acres of public land and 309 acres of private land—as critical habitat for the Perdido Key beach mouse. Specifically, the revised designation consists of five land units that, together, comprise a little less than half of the total acreage of Perdido Key. Numbered geographically from west to east, three of the units, PKBM-1 (Gulf State Park), PKBM-3 (Perdido Key State Park), and PKBM-5 (Gulf Islands National Seashore), consist of federal or state lands. The two remaining units, PKBM-2 (West Perdido Key) and PKBM-4 (Gulf Beach), consist of private lands.
PKBM-1, or unit 1, includes 115 acres in southern Baldwin County, Alabama, on the westernmost end of Perdido Key. While beach mouse habitat in this unit—the Gulf State Park unit—consists of primary, secondary, and scrub dunes, scrub habitat is separated from the frontal dunes by a highway, reducing the accessibility of such habitat. Gulf State Park was occupied by the beach mouse at the time of listing and, by 1986, contained the only known existing population of the subspecies. In 1986, mice from Gulf State Park were used to re-establish the Perdido Key beach mouse population in PKBM-5, the Gulf Islands National Seashore unit. This re-establishment project ultimately saved the Perdido Key beach mice from extinction as the population at Gulf State Park was considered extirpated in 1998 due to tropical storms and predators.
PKBM-2, or unit 2, consists of 33 acres, including primary, secondary, and scrub dunes, in southern Baldwin County, Alabama, and 114 acres in southern Escambia County, Florida. Although this unit was not occupied by the beach mouse at the time of listing, the FWS determined— based on observations of beach mouse burrows
PKBM-3, or unit 3, the Perdido Key State Park unit, consists of 238 acres of primary, secondary, and scrub dune habitat in southern Escambia County, Florida. Perdido Key beach mice were known to inhabit this unit in 1979. Hurricane Frederic (1979) impacted the population, however; and no beach mice were captured in the park during extensive surveys in the early 1980s. The unit was accordingly considered unoccupied at the time of listing in 1985. In 2000, the beach mice were successfully reestablished in this unit as part of the FWS's recovery efforts.
PKBM-4, or unit 4, consists of 162 acres of private land in southern Escambia County, Florida. Primary, secondary, and scrub dunes are present in this unit. Although the unit was not known to be occupied at the time of listing, the presence of beach mice was confirmed in 2004 by live-trapping efforts. Like unit 2, this unit is considered by the FWS to be essential to the conservation of the species because it provides connectivity between two existing populations of beach mice (Perdido Key State Park and Gulf Islands National Seashore) and because it provides essential habitat for expansion, natural movements, and re-colonization.
PKBM-5, or unit 5, the Gulf Islands National Seashore unit, consists of 638 acres at the easternmost end of Perdido Key. Beach mouse habitat in this unit consists mainly of primary and secondary dune habitat. Perdido Key beach mice were known to inhabit this unit in 1979, before Hurricane Frederic hit the island. Because no beach mice were captured at this location during extensive surveys in the early 1980s, the unit was considered unoccupied at the time of listing. In 1986, Perdido Key beach mice were re-established in this unit as part of FWS's recovery efforts. In 2000 and 2001, beach mice captured from this unit served as donors to re-establish the mice at Perdido Key State Park (unit 3).
The ESA does not alone impact development on Perdido Key. The State of Florida regulates development in coastal areas through the Beach and Shore Preservation Act (the "BSPA"). Fla. Stat. §§ 161.011.45. Among other things, the BSPA requires the Florida Department of Environmental Protection ("FDEP") to establish coastal construction control lines ("CCCL") on a county basis along the sand beaches of the state. Id. at § 161.053(1)(a). Such lines are established "so as to define that portion of the beachdune system which is subject to severe fluctuations based on a 100-year storm surge, storm waves, or other predictable weather conditions." Id. While new construction and alterations to existing structures seaward of the CCCL may be allowed, these activities require a CCCL permit from the FDEP. Id. at § 161.053(5). As a condition for issuing such permits, the FDEP may "require mitigation, financial, or other assurances acceptable to the department as may be necessary to assure performance of the conditions of a permit." Id. at § 161.053(5)(f). With limited exceptions (including exceptions for single-family dwellings and for maintenance and repair activities to existing structures and structures pre-dating the control line), permits for construction seaward of the CCCL are not allowed if the construction will also be
Like the federal government, the State of Florida has an Endangered and Threatened Species Act. Fla. Stat. § 379.2291. By rule, the Florida Fish and Wildlife Conservation Commission ("FFWCC") has listed the Perdido Key beach mouse as an endangered species and has provided that "[n]o person shall pursue, molest, harm, harass, capture, possess, or sell [the Perdido Key beach mouse], or parts thereof or their nests or eggs except as authorized by specific permit, permits being issued only when the permitted activity will clearly enhance the survival potential of the species." Fla. Admin. Code r. 68A-27.003(1)(x) (2009). Like the federal ESA, which requires incidental take permits for lands actually inhabited by beach mice, the state rule requires permits for lands that are, in fact, occupied by the mice.
Like the federal and state governments, Escambia County, Florida, (the "County") regulates endangered species. In particular, the County has enacted an ordinance requiring persons who propose to impact "threatened or endangered species habitat" ("TE habitat") to submit an application that provides written documentation demonstrating that impacts to TE habitat have been avoided and/or minimized to the maximum extent possible. Escambia County Land Development Code § 7.13.01. TE habitat is defined as:
Id. at § 3.00.01. If an applicant demonstrates adequate minimization of unavoidable impacts to TE habitat, then the applicant must submit a mitigation plan for review and consideration by County officials. Mitigation procedures are required in any case where development may degrade TE habitat. Id. at § 7.13.03.C.
In December of 2005, a year before the FWS issued its final rule revising the designation of critical habitat, the Board of County Commissioners entered into an agreement with the FFWCC and the FWS to establish a unified process for mitigating impacts to the Perdido Key beach mouse. Wanting to establish a single administrative mechanism for managing and spending funds generated from various sources for beach mouse conservation, the parties established a conservation fund— the Perdido Key Conservation Management Fund—into which both state and federal permitting applicants may voluntarily contribute funds as a means of mitigating the effects of development on the beach mouse. The three governmental parties agreed to a unified mitigation fee of $100,000 per acre of impact, plus a recurring fee of $201 per development unit per year. The availability of this unified contribution approach was expected to streamline the permitting process, thereby reducing costs and delays, by simultaneously meeting the requirements of all three levels of government (county, state, and federal).
Paul and Gayle Fisher allege in their complaint that they are property owners and residents of Perdido Key, Escambia County, Florida. In 2004, Perdido Key was devastated by Hurricane Ivan, a category 3 hurricane. The Fishers maintain that they "have been unable to rebuild after their homes were destroyed by Hurricane Ivan." Compl. at ¶ 5. Without elaboration, they assert that "[their] ability ...
PKPR, a Florida corporation, is a civic organization, the members of which own real property or have a bona fide interest in real property on Perdido Key. PKPR maintains that the "ability of PKPR shareholders to use their land, including the restoration of property destroyed by Hurricane Ivan, is undermined by the designation of critical habitat for the Perdido Key beach mouse." PKPR alleges no other particulars about its members, their properties, or their injuries.
Among other things, Defendants raise the issue of standing in their motion for summary judgment. According to Defendants, Plaintiffs have fallen far short of identifying any injury-in-fact "that is concrete and particularized, as well as actual or imminent, that causally is connected to the critical habitat designation, and that is likely to be redressed by a decision in [their] favor."
In response to Defendants' motion for summary judgment, the Fishers each submitted a very brief affidavit, attesting to nothing more than that the FWS's designation of critical habitat "undermined" his/ her ability to use his/her property. Having provided no "specific facts" about their properties or their injuries as required under Bischoff v. Osceola County, Florida,
As to the three units located on public lands, Plaintiffs have made no attempt at all to establish standing to challenge the designation of those units as critical habitat. Consequently, to the extent, if any, that Plaintiffs seek to invalidate the critical habitat designation of PKBM-1 (Gulf State Park), PKBM-3 (Perdido Key State Park), and PKBM-5 (Gulf Islands National Seashore), their suit must be dismissed for lack of standing.
In their respective affidavits, Paul and Gayle Fisher state that he/she is "a property owner of a residence on Perdido Key" who has "been unable to rebuild after ... Hurricane Ivan." Neither provides any other particulars, including whether their residence(s) was/were in unit 2 or 4,
The same is true of the corporate plaintiff, PKPR. Having provided no information about its members or where the members' property is/was located, the court is unable to decide whether PKPR has standing to challenge the designation of unit 2, unit 4, or both.
Even if the court were to assume, for the sake of argument, that Plaintiffs do have standing to challenge the designation of unit 2, unit 4, or both, the court finds that they have not demonstrated that the FWS's designation is invalid.
In challenging the FWS's critical habitat designation, Plaintiffs have invoked both the ESA's citizen suit provision, 16 U.S.C. § 1540(g)(1), as well as the Administrative Procedure Act ("APA"), 5 U.S.C. §§ 701-706. Claims under both statutes are reviewed under the APA's arbitrary and capricious standard, which provides that a court shall set aside an agency's decision only if it is "arbitrary, capricious, an abuse of discretion, or otherwise not in accordance with law." Id. at § 706(2)(A). An agency rule is arbitrary and capricious "if the agency has relied on factors which Congress has 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." Motor Vehicle Mfrs. Ass'n of U.S., Inc. v. State Farm Mut. Auto. Ins. Co.,
Miami-Dade County v. United States EPA,
The burden of proof under the arbitrary and capricious standard is on the party challenging an agency's decision. Cape Hatteras Access Preservation Alliance v. United States Dep't of Interior,
In defining critical habitat, the ESA differentiates between geographical areas that were occupied by the species at the time of listing and those that were not occupied by the species at the time of listing. For areas that were occupied by the species at the time of listing, critical habitat is limited to those areas containing "physical or biological features (I) essential to the conservation of the species and (II) which may require special management consideration or protection." 16 U.S.C. § 1532(5)(A)(i). For geographical areas that were not occupied by the species at the time of listing, critical habitat is limited to "areas essential for the conservation of the species." Id. at § 1532(5)(A)(ii).
Here, the parties agree that, of the five areas now designated as critical habitat for the Perdido Key beach mouse, four areas (units 2 through 5) were either not known to be occupied, or were confirmed to be unoccupied, at the time of listing. Unit 1, the Gulf State Park Unit, is the only unit which was known to be occupied by the beach mouse at the time of listing. Accordingly, the first part of the critical habitat definition applies only to unit 1. Because Plaintiffs have not demonstrated their standing to challenge unit 1, the court need not consider whether the FWS adequately identified "those physical or biological features (I) essential to the conservation of the species and (II) which may require special management considerations or protection."
As to units 2 and 4, the units containing private lands, the FWS was required to show only that those areas "are essential for the conservation of the species." The FWS explained in its final rule, dated October 12, 2006, that both units are essential for the conservation of the beach mouse because they connect adjacent habitat units and because they provide habitat needed for storm refuge, expansion, natural
Regarding the need for connectivity, the FWS summarized the conclusions it reached—based, among other things, on various scientific studies—as follows:
Id. at 60248 (citations omitted).
According to the FWS, the designation of units 2 and 4 as critical habitat not only helps to assure that the beach mouse's
In challenging the FWS's designation of units 2 and 4 as critical habitat, Plaintiffs argue that the FWS failed to adequately identify and/or define PCEs, failed to describe how the stated PCEs will serve the FWS's conservation goals, failed to determine that the stated PCEs are essential to meeting those conservation goals, and failed to identify the specific areas that may require special management considerations or protection. In so arguing, Plaintiffs rely on that part of the critical habitat definition that applies to geographical areas known to be occupied by the species at the time of listing, the part that defines critical habitat as containing "those physical or biological features (I) essential to the conservation of the species and (II) which may require special management considerations or protection." 16 U.S.C. § 1532(5)(A)(i). For units 2 and 4, neither of which was known to be occupied at the time of listing, the FWS was not required to identity PCEs. Instead, the FWS was required to find that units 2 and 4 are "areas essential for the conservation of the species." This the FWS did, and Plaintiffs have altogether failed to demonstrate that the FWS's essential-for-conservation decision was "arbitrary, capricious, an abuse of discretion, or otherwise not in accordance with law."
The ESA requires the FWS to designate critical habitat "on the basis of the best scientific data available and after taking into consideration the economic impact, the impact on national security, and any other relevant impact, of specifying any particular area as critical habitat." 16 U.S.C. § 1533(b)(2). Neither the statute nor the regulations prescribe any particular method for determining the economic impact of a designation. Moreover, in the statute's legislative history, Congress explained that "[t]he Secretary is not required to give economics or any other `relevant impact' predominant consideration in his specification of critical habitat." Instead, "[t]he consideration and weight given to any particular impact is completely within the Secretary's discretion." H.R.Rep. No. 95-1625, at 16-17 (1978), as reprinted in 1978 U.S.C.C.A.N. 9453, 9467.
At one time, the FWS considered only those economic impacts that would not occur but for the critical habitat designation. Any economic impacts also attributable to other factors, such as the listing of a species, were excluded. This approach, known as the baseline approach, "involves comparing the state of the world without or before the designation, the baseline, with the state of the world with or after the designation." Cape Hatteras Access Preservation Alliance, 344 F.Supp.2d at 127. The difference between the two worlds represents the impact of the designation.
The FWS long ascribed to the theory that little actual impact flows from the critical habitat designation, that impacts instead flow primarily from listing decisions.
The Fifth and Ninth Circuits have rejected the "functional equivalence theory" and have invalidated the regulation that defines "destruction or adverse modification" as "a direct or indirect alteration that appreciably diminishes the value of critical habitat for both the survival and recovery of a listed species." 50 C.F.R. § 402.02. See Gifford Pinchot Task Force v. United States Fish & Wildlife Serv.,
Gifford Pinchot, 378 F.3d at 1070. The Fifth Circuit provided a similar explanation:
Sierra Club, 245 F.3d at 441-42.
Without considering the validity of the regulatory definitions, the Tenth Circuit rejected the baseline approach in New Mexico Cattle Growers v. United States Fish & Wildlife Service,
Other courts have since declined to follow the Tenth Circuit's co-extensive approach. See Arizona Cattle Growers' Asso. v. Kempthorne,
Arizona Cattle Growers' Ass'n, 534 F.Supp.2d at 1035.
The courts in Cape Hatteras, Arizona Cattle, and Center for Biological Diversity, all determined—and this court agrees— that the baseline approach is a reasonable method, consistent with the language and purpose of the ESA, for assessing the actual costs of a particular critical habitat designation. Congress specified that, when deciding whether or not to designate critical habitat, the FWS shall take into consideration "the economic impact ... of specifying any particular area as critical habitat." 16 U.S.C. § 1533(b)(2) (emphasis added). In the words of the Cape Hatteras court: "[T]o find the true costs of a designation, the world with the designation must be compared to the world without it." 344 F.Supp.2d at 130. Costs that exist independently of the critical habitat designation cannot be costs "of specifying any particular area as critical habitat." Such independent costs represent a baseline that must not influence the decision to designate or not designate areas as critical habitat. To the extent the Tenth Circuit's co-extensive approach permits consideration of costs not attributable to the designation, it is inconsistent with the mandate of the ESA.
In this case, the FWS hired Industrial Economics, Inc., to prepare a report analyzing the economic impacts of critical habitat designation on Perdido Key and elsewhere. The consultants' report—dated September 8, 2006—describes the framework for analysis in some detail, relevant parts of which include:
A.R. 2844-45, 2848-49, 2871.
In its final rule designating critical habitat on Perdido Key, the FWS explained that, because of the Fifth and Ninth Circuits' decisions in Gifford and Sierra Club, the meaning of "destruction or adverse modification" was determined not on the basis of the regulatory definition but, instead, "on the basis of whether, with implementation of the proposed Federal action, the affected critical habitat would remain functional ... to serve the intended conservation role for the species." 71 Fed. Reg. at 60255. The FWS also explained that its economic analysis was "consistent with the ruling of the 10th Circuit Court of Appeals in N.M. Cattle Growers Ass'n v. USFWS." in that it considered "the economic efficiency effects that may result from the designation, including habitat protections that may be co-extensive with the listing of the species." Id. at 60262. On the other hand, the FWS noted:
In challenging the FWS's economic analysis, Plaintiffs first contend—without elaboration—that the FWS erred by using the baseline method rejected by the Tenth Circuit in New Mexico Cattle Growers. Plaintiffs point to language in the report prepared by Industrial Economics, Inc., explaining that the company's economic analysis took "into account the cost of conservation-related measures that are likely to be associated with future economic activities that may adversely affect the habitat within the proposed boundaries." A.R. 2844. Plaintiffs maintain that, by relying on costs associated with "future economic activities," the consultants necessarily pushed costs attributable to "past conservation efforts" below a baseline, thereby improperly ignoring them. While acknowledging that the consultants stated in their report that they employed the Tenth Circuit's co-extensive analysis, Plaintiffs suggest that, in fact, no such co-extensive analysis was conducted. Specifically, Plaintiffs assert that the consultants failed to assess the impacts attributable to the mouse's listing and to the "existing regulatory environment." According to Plaintiffs, the FWS—in reliance on the report of its consultants—violated the ESA by employing a baseline analysis rather than a co-extensive analysis.
In fact, the record suggests that the FWS assessed the economic impacts of its 2006 critical habitat designation using a mixed-model, employing both baseline and coextensive analyses. Plaintiffs have
Plaintiffs next contend that the FWS failed "to combine the effects of the designation with the effects of all other non-ESA regulations to ascertain whether the designation may prove to be the regulatory straw that breaks the local community's economic back." Doc. 28 at 17. To support their argument, Plaintiffs note that the National Environmental Policy Act ("NEPA"), 42 U.S.C. §§ 4321-4370f, requires agencies to consider the cumulative effects of unrelated actions when engaging in a NEPA analysis. Plaintiffs cite to no authority that suggests, much less holds, that the FWS is required to consider the impacts of other regulatory schemes—including, as suggested by Plaintiffs, the Clean Water Act, the Beach and Shore Preservation Act, the Florida Endangered Species Act, the Coastal Barrier Resources Act, and the Coastal Zone Protection Act—when deciding whether or not to designate critical habitat. The ESA and its regulations require consideration of the economic and other impacts of a critical habitat designation, nothing more. See Arizona Cattle Growers' Ass'n, 534 F.Supp.2d at 1036 (rejecting the plaintiffs attempt to graft NEPA's cumulative-impacts analysis into the context of critical habitat designation).
Plaintiffs next contend that the FWS significantly understated costs associated with (1) the delay in obtaining regulatory approvals, and (2) the processing of state and local permits. In particular, Plaintiffs contend that the FWS failed to account for the delays and permit costs experienced by individual property owners wanting to rebuild after Hurricane Ivan devastated Perdido Key in 2004.
Id. at 2884-85. It is also noted that some of the delays and permitting problems were—and would likely continue to be— caused by unresolved home insurance claims and the need for new and/or expanded insurance coverage. Id. at 2887. In addition, the consultants reported that, given the unified mitigation approach that was approved in 2005 by federal, state, and county governments, an approach that was intended to streamline the cumbersome permitting process that was in place when Hurricane Ivan blew through Perdido Key in 2004, designation-related delay and permitting costs were expected to be minimal.
Plaintiffs fall far short of demonstrating that the FWS's failure to quantify delay and permitting costs was arbitrary and capricious. To be sure, Plaintiffs cite to the comments of a county administrator who stated, on July 14, 2006, that "[a]t a minimum there have been lengthy time delays ... and these delays are ongoing." While opining that "[t]he economic impacts of these and other factors clearly should have been included in the analysis," A.R. 2378, the county administrator provides no specifics whatsoever. Indeed, neither the administrator's comments nor any other evidence cited by Plaintiffs demonstrates that, contrary to the conclusion of the economic consulting firm, the FWS could have accurately determined or quantified the delay and permitting costs, if any, attributable to critical habitat designation as opposed to other causes. Without more, the court has no basis for finding that the FWS's decision with regard to delay and permitting costs was arbitrary and capricious.
Finally, Plaintiffs make an argument— albeit a confusing one—that the FWS failed to adequately consider the distributional effects of the critical habitat designation, particularly the effects on small businesses. As explained in the consulting firm's final report, a distributional-effects analysis focuses on the question of how potential economic impacts of a critical habitat designation are likely to be distributed among particular groups or economic sectors. A.R. 2846. In this case, the analysis focused on seven categories of activities
Plaintiffs disagree with the methods and results of the consulting firm's distributional-effects analysis, but they altogether fail to establish that the FWS's reliance on that analysis was arbitrary and capricious. As mentioned above, an agency decision is arbitrary and capricious "if the agency has relied on factors which Congress has 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." Motor Vehicle Mfrs. Ass'n of U.S., Inc., 463 U.S. at 43, 103 S.Ct. 2856. Plaintiffs here have demonstrated nothing of the sort.
To survive Defendants' motion for summary judgment, Plaintiffs must submit sufficient evidence (1) to establish their standing to sue, and (2) to establish a genuine issue of material fact with regard to whether the FWS's 2006 designation of critical habitat was arbitrary and capricious. Because Plaintiffs have done neither, it is ORDERED:
1. Defendants' motion for summary judgment (doc. 35) is GRANTED.
2. Plaintiffs' motion for summary judgment (doc. 28) is DENIED.
3. The clerk is directed to enter judgment accordingly.
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