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1 <br />The native fish fauna of the Colorado River is characterized by a high level of <br />endemism. Of the 46 native fishes (species and subspecies) present in recent times, <br />38 are endemic (Miller 1958, Stanford and Ward 1986b). The high level of endemism <br />was heavily influenced by the Quaternary history of the intermountain area of western <br />~ North America. Populations were isolated by desertification, and faunal composition <br />was changed by local extinctions during the Pleistocene (Smith 1978, Stanford and <br />Ward 1986b). At one point, native Colorado River fishes consisted of only 32 to 36 <br />species, depending on taxonomic interpretation (Stanford and Ward 1986b, Carlson <br />and Muth 1989). River systems of similar size elsewhere (e.g., Missouri River) typically <br />~ have an order of magnitude more fish species. <br />Present Distribution and Abundance <br />~ Four of the big river fishes, the Colorado pikeminnow (Plychocheilus lucius), razorback <br />sucker (Xyrauchen texanus), humpback chub (Gila cypha), and bonytail (Gila <br />e/egans)(Frontispiece), once populated warmwater reaches of the mainstream rivers of <br />the Colorado River basin from Wyoming to Mexico. The abundance and distribution of <br />these fishes have been drastically reduced, and the species are now threatened with <br />~ extinction. As part of the effort to recover these species, government agencies have <br />invested heavily in surveys establishing the present distribution and abundance of each <br />species. The results of these surveys provide the basis for assessing essential <br />aspects of Iffe history needs (e.g., habitat preference, migrations, etc.), and, in time, <br />progress toward recovery goals. <br />~ Beginning in-1979, the USFWS initiated an ambitious program for monitoring the <br />abundance of endangered fish species throughout the UCRB. Not only was spatial <br />coverage thorough in a statistical sense, but several types of sampling gear were used <br />to optimize collection of all species and life history stages. Sampling efficiency was <br />optimized by selecting river reaches (strata) representing different habitat <br />~ characteristics. The results of this comprehensive program, summarized in W.H. Miller <br />et al. (1982d), provide an excellent baseline record of fish abundance in the UCRB. <br />Subsequent monitoring efforts have been less comprehensive in terms of spatial <br />coverage and sampling gear, but can detect major trends in abundance (McAda et al. <br />~ 1994). However, identifying trends in fish abundance has been hampered by high <br />variability in capture data among years, because local changes in the riverine <br />environment and stochastic events can affect population size. In addition, elucidation <br />of trends in the UCRB is complicated by the migratory habits of species like the <br />Colorado pikeminnow, and by the difFculties of identifying early life history stages of the <br />~ endangered species, especially when those stages may be segregated spatially from <br />the adults. <br />A number of investigators have used standardized methods to sample fish populations <br />in the various rivers of the UCRB and have described the physical habitat in which the <br /> <br />4 <br /> <br />