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Endangered Species Act (ESA) Jeff Wade Center for Governmental Responsibility University of Florida Levin College of Law Definitions & Principles Basic definition for biological diversity: "the full range of variability among living organisms and the natural communities in which they occur." Four hierarchical components: regional ecosystem diversity; local ecosystem diversity; species diversity; and genetic diversity. 1 Interrelated Components Regional ecosystem diversity encompasses the pattern of local ecosystems across the landscape. Local ecosystem diversity involves the diversity of all living and nonliving components within a given area and their interrelationships. Local ecosystems are the critical biological operating units in nature. Species diversity describes the variety of individual species within a local ecosystem. Genetic diversity refers to the variations within a species, providing a measure of the species' ability to adapt to changing environments. Conserving biodiversity involves identifying and managing the factors that contribute to the decline of biodiversity. Direct physical alteration resulting from resource development and changing land use is the most pervasive cause of biodiversity loss. Physical impacts of development on habitat areas can destroy, simplify, or fragment an ecosystem and thereby reduce the diversity within and made available by the ecosystem. Other significant contributors to biodiversity impairment include habitat pollution, over-harvesting of species or introduction of non-native species. 2 So the fundamental goal of biodiversity conservation is fairly evident: "to maintain naturally occurring ecosystems, communities, and native species." ESA adopted in 1973 The strongest legislative statement of the importance of biological diversity Recognizes that habitat protection is vital to the preservation of species Administered by the U.S. Fish and Wildlife Service and National Marine Fisheries Service 3 Generally Provides broad protection for species of fish, wildlife and plants that are listed as threatened or endangered in the U.S. or elsewhere. Provisions are made for listing species, designating critical habitat for listed species, and for establishment of recovery plans. The Act outlines procedures for federal agencies to follow when taking actions that may jeopardize listed species, and contains exceptions and exemptions. Purposes and Policy Sections The purpose and policy sections of the Act contain specific support for the “means whereby the ecosystems upon which endangered species and threatened species depend may be conserved,” and for Congressional policy that all federal agencies “...seek to conserve endangered ...and threatened species.” 4 Basic Approach 1. listing of endangered and threatened species; 2. designating critical habitat needed to preserve the listed species; 3. requiring the executive branch to develop recovery plans for listed species (Fish and Wildlife Service); 4. prohibiting any action carried out, funded or authorized by a federal agency that is likely to jeopardize the continued existence of a listed species, including the destruction or adverse modification of critical habitat; and 5. prohibiting private actions detrimental to listed species, including the “taking” of such species, or possession or delivery of listed species, unless permitted in exceptional cases where incidental takings of a species will not appreciably reduce the likelihood of survival. Section 4: Listing Process The Act requires the Secretary of the Interior to list species as endangered or threatened based on any of a number of factors, including habitat destruction, overutilization, disease or predation, inadequacy of regulatory mechanisms, or other natural or man-made factors. Listing determinations must be made solely on the basis of the best scientific and commercial data available, after a review of the status of the species and taking into account any efforts being made to protect such species by other jurisdictions. 5 Listing Process Proposals for listing may be made by the Fish and Wildlife Service and the National Marine Fisheries Service, or by petition from any interested person. Earlier listing procedures only addressed single species, and often “charismatic” species, such as wolves, bears and large birds. In the 1990s, the FWS agreed to take a “multi-species, ecosystem approach” to the listing of endangered and threatened species. Critical Habitat "Critical habitat" is defined as the specific geographic areas, occupied by a species, that have the essential physical and biological features for conservation of the species and that may require special management protection. The designation is made on the basis of the best scientific data available and taking into consideration the economic impact and any other relevant impact of specifying a particular area. An area may be excluded if it is determined that the benefits of exclusion outweigh the benefits of designation, unless the Secretary determines that exclusion will result in extinction of the species. 6 Critical Habitat A regulation designating critical habitat for the species being listed must be published at the same time as the listing of the species, "to the maximum extent prudent and determinable." Using this language, the FWS has declined to designate the critical habitat of about 80% of listed species. If not published at the time a species is listed, critical habitat must be designated within two years, however in practice, this has meant that only an extremely small number of listings have included concurrent designation of critical habitat. There are serious delays in the designation of critical habitat. The typical time between filing a petition for listing and Secretarial action is two or three years. Section 7 The section most clearly protecting habitat and generating most litigation is Section 7: Requires federal agencies to consult with FWS to insure that any action authorized, funded, or carried out by an agency is not likely to jeopardize the continued existence of an endangered or threatened species or result in the destruction or adverse modification of “critical habitat” of such species. 7 Section 7 After initiating the required consultation, an agency or permit applicant may not make any “irreversible or irretrievable commitment of resources...which has the effect of foreclosing the formulation or implementation of any reasonable and prudent alternative measures.” Section 7 Federal agencies are involved in the construction, licensing, financing or authorization of a very large number of projects throughout the country. The duty to insure that such activity will not destroy or adversely modify critical habitat has the potential to restrict many types of development activities affecting listed species. 8 TVA v. Hill (1978) The most famous Section 7 case, T.V.A. v. Hill stopped construction of the almost completed Tellico Dam when it was discovered that the only known habitat of the endangered Tennessee snail darter fish would be destroyed if the dam were closed. The U.S. Supreme Court said that Section 7 required much more than a simple consultation, emphasizing that if a project jeopardized a listed species, the project would not be allowed. National Wildlife Federation v. Coleman (1976) The restrictions also extend to federal actions with more indirect effects than those in Hill. Coleman case involved an interstate highway authorized by the Federal Highway Administration (FHWA). Would have directly removed about 125 hectares of nesting, roosting and feeding ground for approximately 40 Mississippi sandhill cranes, members of an endangered sub-species whose only habitat was in that region. The FHWA had decided that the highway would not jeopardize the species or its habitat because the loss of acreage was relatively small, and FHWA control of access to the highway would eliminate any other threat to the crane. 9 Court stopped the project: “a far more subtle calculation than merely totaling the number of acres to be asphalted” is necessary where the environmental impact of a project is at issue. “Although it is clear that the crane can survive the direct loss of 300 acres of habitat, the evidence...shows that it is questionable whether the crane can survive the additional loss of habitat caused by the indirect effects of the highway, coupled with the excavation of and drainage caused by borrow pits.” Private development always accompanies major highway projects; this additional development would be the primary impact on the crane. The relevant consideration is the total impact of the project on the species. Section 5 FWS and NMFS can implement more direct habitat conservation measures through their authority under section 5 to "establish and implement a program to conserve fish, wildlife, and plants, including those which are listed as endangered species or threatened species," principally by acquiring land and waters containing the species' habitat. However, appropriations have not met funding requirements, and there is little indication that under current federal policies the situation will improve. 10 Exemptions to Section 7 If a proposed project will be in unavoidable conflict with a listed species, the agency, state governor or applicant can apply for an exemption. The Endangered Species Committee (or “God Squad”), composed of six cabinet level administrators and a representative from each affected state, can grant an exemption if it determines that: (1) there are no reasonable and prudent alternatives; (2) the benefits of the action clearly outweigh the benefits of alternative courses of action consistent with the ESA; (3) the agency action is in the public interest; (4) the action is of regional or national significance; and (5) neither the agency nor the applicant has made an irreversible or irretrievable commitment of resources. The ESC must also establish reasonable mitigation and enhancement measures, to minimize adverse effects on the species. Section 9 When there is no federal involvement in a project, the most relevant section of the ESA is Section 9, which prohibits any person subject to the jurisdiction of the United States from “taking” an endangered fish species or a wildlife species which is endangered or threatened. “Person” is broadly defined as “an individual, corporation…or any other private entity; or any officer, employee…of the Federal Government, of any State…or any foreign government; …or any other entity subject to the jurisdiction of the United States.” The word “take” means: “to harass, harm, pursue, hunt, shoot, wound, kill, trap, capture, or collect, or to attempt to engage in such conduct.” 11 Definition of “Harm” The ESA does not define the word “harm.” However, FWS regulations define harm as, “an act which actually kills or injures wildlife. Such act 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.” The U.S. Supreme Court has upheld the regulation; detrimental modification of a listed species’ habitat is prohibited. Taking a threatened or endangered species in the course of development can lead to civil fines of up to $25,000 per occurrence, and criminal penalties (fine of up to $50,000 and/or up to 1 year in prison). Palila v. Hawaii Department of Land and Natural Resources (1979) The most famous case which affirmed this definition was Palila v. Hawaii Department of Land and Natural Resources, a Section 9 case involving a state program which maintained feral goats and sheep in native forests, for the benefit of sport hunters. The palila bird, an endangered, non-migratory member of the Hawaiian honeycreeper family, is specifically adapted to and dependent on the mamane forest ecosystem, which was being slowly destroyed by the browsing game animals. In 1977, the remaining ten percent of the bird's original range had been designated as critical habitat, though this was also being threatened by the herds of goats and sheep. 12 The court noted that the ESA defines “take” to include “harm,” and that the FWS defines “harm” to include “significant environmental modification or degradation.” The court held that the “undisputed facts bring the acts and omissions of defendants clearly within these definitions.” The Ninth Circuit Court of Appeals affirmed the decision in 1981, approving the district court's interpretation of the Act as being consistent with Congressional findings that “the greatest threat to endangered species is the destruction of their natural habitats.” Exceptions The ESA provides for a few limited exceptions to the taking prohibitions under Section 9 The most controversial is the Incidental Take Permit (ITP) which allows an “incidental take of a listed species that results from, but is not the purpose of…an otherwise lawful activity conducted by the federal agency or applicant.” In order to obtain an ITP, an applicant must meet all criteria for an ITP including adopting a Habitat Conservation Plan. 13 Habitat Conservation Plan Applicants for an ITP must submit a habitat conservation plan that indicates: After a “public comment period” on the plan, Secretary must find that the probable impacts from the project; plans to minimize and mitigate such impacts, including funding plans; alternatives that would not result in takings, and the reasons they are not being utilized; and other requirements considered necessary or appropriate by the Secretary of the Interior. the taking will be incidental, the applicant will mitigate impacts of the taking “to the maximum extent practicable,” the funding of the plan will be adequate, and the taking will not “appreciably reduce” the likelihood of the survival and recovery of the species in the wild. Problems: Mitigation is a term that, as applied in wetlands permitting cases, can have a wide variety of definitions, and an equally wide measure of effectiveness. Requiring mitigation only “to the maximum extent practicable” allows consideration of economic variables that can certainly reduce the likelihood of species survival. 14 Over 400 habitat conservation plans now cover about 15 million hectares, and applications in process could increase that to over 40 million hectares. Problems with HCPs Fish and Wildlife Service, doesn't know whether the plans are shielding creatures from further decline or speeding them toward extinction. No “benchmarks”. Many plans open the door to permanent damage of wild places before scientists know how to best protect vulnerable animals. Most fail to predict how many creatures will be killed or harmed. Few spell out an exit strategy if things go wrong. 15 Local governments often help developers by allowing existing parkland to count as "preserves" or defraying their costs often using federal dollars. The public, including independent scientists, often has little voice in the plans—even some covering vast acreages—until they are essentially completed. HCPs focus on setting aside land to save it from the bulldozer or chain saw, but sometimes they do not include enough funding to maintain the preserves. Limitations of the ESA Listing of species very slow process; politically influenced; delays have allowed extinction of about 40 species which were nominated but never listed. Critical habitat must be concurrently listed “to the maximum extent prudent and determinable.” definitional limitations; the process does include economic considerations; does not include entire habitat range of the species; very long delays in designating critical habitats, and some have never been designated. Recovery plans required for listed species. Preparation of plans has been even slower than the listing process. FWS only has recovery plans for approximately half of the listed species. 16 Section 7 applies to federal agencies. Any action must not jeopardize listed species or critical habitat. Very little communication or coordination among large bureaucratic federal agencies on whether actions will have affects on listed species. Section 9 prohibits any "person" to "take" a listed species. If there is an "incidental take" of a species under a development plan, provisions may allow this if "habitat conservation plans" are created for that species. However, very few have been attempted and have not been very successful. ESA represents a basically reactive, not proactive, approach Only addresses a situation when it has reached crisis proportions. Is activated only when species populations and habitat have been reduced so much that heroic efforts are needed to save them. Not very successful; usually waits too long for a species to have good chance of recovery. Requires drastic and expensive curative measures when earlier preventive measures might save more species at lower cost. 17