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
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