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INTRODUCTION <br />Native fishes of the upper Colorado River (UCR) basin have declined in distribution and <br />abundance. Alteration of the natural riverine environment during the last 100 years is <br />the most likely cause of their decline, principally by human actions that resulted in <br />physical habitat loss and the introduction of nonnative species. Construction of water <br />development projects began in the UCR basin in the early 1900s (Fradkin 1984, <br />Carlson and Muth 1989), and by the 1960s, more than 50 dams and major diversions <br />had been constructed on mainstream rivers (Figure 1). Impoundment by these <br />structures converted many river reaches into lacustrine habitat, and operation of dams <br />has altered the natural timing, duration, and magnitude of annual flood flows. Flow <br />regulation and the presence of structures also have caused changes in water <br />temperature, sediment load, nutrient transport, and other facets of water quality <br />(Carlson and Muth 1989). In some reaches, sediment load has been reduced 90% <br />(Fradkin 1984). Most existing mainstream habitats are now different than the historic <br />habitats in which the native fishes evolved, and some have been modified so <br />extensively that native fish can no longer survive in them. <br />The historic riverine habitat also has been changed by the introduction and proliferation <br />of nonnative fish species, including many that are predaceous, highly competitive, and <br />harmful to the native fish fauna (reviewed by Hawkins and Nesler 1991, Lentsch et al. <br />1996, Tyus and Saunders 1996). Although the native fishes were well adapted to their <br />natural environment, alterations to the physical habitat may have created corrditions <br />that are now more favorable to many of the introduced species. Even where physics! <br />habitat has been altered relatively little, nonnative fish abundance has increased, and <br />the abundance of native fishes has been reduced. As a result, most of the native fish <br />habitat is occupied now by introduced species (Minckley 1982, Tyus et al. 1982x, <br />Carlson and Muth 1989). <br />Physical and biological changes to the river system have resulted in endangerment of <br />four native fish species: Colorado pikeminnow Ptychocheilus Lucius (formerly Colorado <br />squawfish), humpback chub Gila. cypha, bonytail G. elegans, and razorback sucker <br />Xyrauchen texanus. These and other fishes native to the main channels of the <br />Colorado River system ("Big River Fish Community") were once widespread and <br />abundant (e.g., Jordan 1891, Jordan and Evermann 1896, Quartarone 1993), but they <br />have disappeared from most of their original habitat. Their endangerment is <br />attributable to a suite of environmental factors that is essentially the same for all four <br />species.. The problem exists at the ecosystem level because an entire fish community <br />is threatened, and threats include biotic and abiotic factors. <br />Successful recovery of all four of the endangered "big river' fishes in the upper <br />Colorado River basin will depend on the maintenance and expansion of present <br />endangered fish populations, and in some cases the establishment of new populations. <br />In both cases, expansion of the occupied range of the existing populations will be a <br />requirement for recovery to aless-endangered status (U.S. Fish and Wildlife Service <br />