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on the mainstream Colorado River produce perpetually cold (10 <br />°C) tailwater habitats and upstream lacustrine environments, <br />both better suited io more iiiai~ .~~ ~~«<~~~~~~ ~r--•-- =- ° - <br />than to the 30 + native species (Minckley 1973). The abnormally <br />cold waters of the river reaches between dams are perpetuated <br />by the constritted canyon walls that prevent solar warming (Cole <br />and Kubly 1976). The few remaining semipristine riverine hab-. <br />itats of the Colorado River, principally in canyons like Desolation, <br />Grand, and Westwater, still retain a few o f the native fish species. <br />However, even these remote habitats are jeopardized by the <br />cold water, large number of non-native fishes, proposed dams, <br />and the threat of dewatering. Similar impacts have occurred on <br />the other major river system in the Southwest, the Rio Grande. <br />Presently, the typical Southwestem desert stream is dammed, <br />diverted, pumped, and polluted to the extent that it either is dry <br />or flows only irrigation return water and sewage effluent during <br />much of the year. <br />Another rapidly disappearing Southwestem aquatic habitat <br />type is the desert spring. These springs vary in flow from mere <br />seeps to hundreds of cubic meters per minute. Endemic fish and <br />invertebrate species have evolved in many of these habitats in <br />response to isolation and stable environmental conditions (Dea- <br />con 1979). Dewatering of these "aquatic islands" via ground- <br />water pumping may result within the next 20 years in the greatest <br />faunal loss in North America. $eme (1975) describes .e p'ght <br />of Texas springs this way: <br />Texas originally had 281 major and historically significant springs, <br />other than saline springs. Of these, four were originally very large <br />springs (over 100-cubic-feet-per-second flow); however, only <br />two, Comal and San Marcos, remain in that class today. Sixty- <br />three springs, many with important historical backgrounds, have <br />completely failed. <br />The purpose of this paper is not to reiterate the contents of <br />numerous scientific articles that adequately discuss dwindling <br />water resources and the decline of native fishes (Miller 1961; <br />Minckley and Deacon 1968; Minckley 1973; Pfister 1974 and <br />1981; Deacon and Minckley 1974; Naiman and Soltz 1981). <br />Instead we proposed to delineateQresent actions being taken <br />to recover the disappeanng resource known as Southwestem <br />is es. and to su est directions t at future conservation efforts <br />may take. We believe that recovery of t ese species and their <br />habitats is closely associated with, and will be dictated by, the <br />federal Endangered Species Act of 1973, as amended. Prior to <br />addressing recovery actions, a review of that legislation and its <br />implementation seems appropriate. <br />ENDANGERED SPECIES ACT <br />In the early 1960's, the people of the United States began to <br />recognize that many of the native fish, wildlife, and plant species <br />had been so depleted in numbers that they were in danger of <br />or were threatened with extinction. This awareness resulted in <br />several legislative attempts to protect disappearing species <br />(Endangered Species Preservation Act of 1966, Endangered <br />Species Conservation Act of 1969) and culminated in Congress's <br />enacting the Endangered Species Act of 1973 (Act-. In 1978 <br />and again in 1979, the Act was amended, perhaps indicating a <br />change in the people (or at least in Congress), or a dissatisfaction <br />with the way the Act was being implemented. Reauthorization <br />in 1982 will either confirm or put to rest the theory that the <br />American public still retains a strong interest in the conservation <br />of endangered species. <br />The purpose of the Act is to conserve e~~dangered crr~ t4reat- <br />ened species and the ecosystems upon which they depend. Ail <br />federal agencies are required to conserve such species and to <br />utilue their authorities to further that purpose. Private citizens <br />are prohibited from taking listed species without a pem~it and <br />are subject to fines and/or imprisonment for violations. Citizens <br />are also given the right to commence a civil suit on their own <br />behalf to enjoin any person or agency, including the United <br />States, alleged to be in violation of the Act. <br />Implementation of the Endangered Species Act <br />The U.S. Fish and Wildlife Service implements the Act within <br />the coastal boundaries of the United States. Listing, protection, <br />and recovery are the three principal areas of emphasis in the <br />Service program. <br />Listing <br />The Act defines an endangered species as ":..any species <br />which is in danger of extinction throughout all or a significant <br />portion of its range..: ," and a threatened species as " ...any <br />species which is likely to become an endangered species within <br />the foreseeable future throughout all or a significant portion of <br />its range...." In the United States, there are presently a total <br />vi izv verteb:=te Srer°== ):fit='~ `"° 2^.da^^ororj and 33 listed ds <br />threatened; of those, 32^and 12 respectively,-are fishes (USDI <br />1982). Listing a species as threatened or endangered involves <br />an extensive serves of steps, including status surveys, economic <br />and environmental assessments, public meetings, inquiries from <br />local, state, and federal entities, and two publications in the. <br />Federal Register. Habitats necessary to the survival of listed <br />species are protected from adverse federal alteration or destruc- <br />tion by the designation of critical habitat. <br />Protection <br />Protection comprises two major areas of emphasis: (1) Section <br />7 consultation reviews federal agency aciions that might affect <br />listed species and their critical habitats, and (2) special agents of <br />the Fish and Wildlife Service enforce the prohibition on taking <br />listed species by individual citizens. The most likely result of <br />consultation is the early identification of a potential conflict dur- <br />ing the planning phase of a federally sponsored project and the <br />provision of reasonable and prudent alternatives that minimize <br />or eliminate the potential adverse impact to the species and its <br />habitat. In the decade that the Act has been in operation, 1,632 <br />consultations have been reviewed in Arizona, New Mexico, Texas, <br />and Oklahoma. Only 13 of these consultations have determined <br />that the proposed federal project would jeopardize a listed spe- <br />cies, and in those cases, alternatives were suggested to alleviate <br />the impact. Law enforcement agents investigate domestic vio- <br />lations ofthe Act in order to prevent illegal taking of listed species. <br />Since survival of a listed species is more dependent. upon pre- <br />vention of an illegal action than upon arresting a perpetrator <br />after he has destroyed an irreplaceable individual or gene pool, <br />emphasis of the enforcement program is to deter taking of <br />endangered species rather than to arrest and convict violators. <br />Recovery <br />Listing and protection are activities that generally slow the <br />decline or maintain the status quo of tenuous species. By com- <br />parison, recovery actions are designed to actively reverse declin- <br />ingtrends. Recovery actions to date have ranged from appoint- <br />July -August 1982 <br />