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Anita M. Martinez <br />3 <br />The razorback sucker (Xyrauchen texanus), an endemic Colorado River catostomid, <br />is in danger of extinction due to habitat loss (Carlson and Muth 1989.; Tyus and Karp 1989; <br />Tyus and Karp 1990; Osmundson and Kaeding 1991), possible competition and predation <br />by non-native species (Minckley 1983; Marsh-and Brooks 1989; Bestgen 1990), and lack <br />of recruitment (Tyus 1987; Papoulias 1988; Lanigan and Tyus 1989; Tyus. and Karp 1990). <br />Hybridization between native, sympatric catostomid species may also be contributing to <br />the demise of this monotypic genus (Buth and Murphy 1984; Buth et al. 1987; Tyus and <br />Karp 1990) although this theory has been questioned (Minckley et al. 1991). The <br />razorback sucker is listed as endangered by the Endangered Species Act of 1973 and is <br />protected by state statutes in Arizona, California, Colorado, Nevada, New Mexico, Utah, <br />and Wyoming. A cooperative agreement between the Colorado Division of Wildlife <br />(CDOW) and U.S. Fish and Wildlife Service in 1993 and 1994 initiated hatchery <br />production at the CDOW Fish Research Hatchery (FRH) to establish a refugia and a <br />source of razorback suckers for possible augmentation of wild populations. <br />Razorback suckers have been reared extensively in earthen ponds containing <br />plankton and other natural foods (Hamman 1987) and in isolated backwaters of Lake <br />Mohave (Mueller et al. 1993). Tyus and Severson (1990) examined growth and survival <br />of intensively cultured larvae age 5 to 45 days fed five commercial fry diets. These <br />perFormance investiga#ions were continued up to age 126 days by Severson et al. (1992). <br />Though a recommended diet (Tyus and Severson 1990; Severson et al. 1992) was fed to <br />razorback sucker larvae reared at the FRH in 1993, approximately 65% of the larvae <br />