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<br />INTRODUCTION <br />The razorback sucker, Xyrauchen texanus, is an endangered fish <br />endemic to the Colorado River basin. The largest remaining <br />population of this unique species occupies Lake Mohave, a <br />mainstream Colorado River reservoir in Arizona and Nevada, where it <br />has been studied since impoundment of the lake in the 1950s <br />(Minckley 1983, Minckley et al. 1991). The adult population, <br />estimated to number about 60,000 fish (Marsh 1992), is comprised of <br />old individuals (McCarthy and Minckley 1987). Although these <br />reproduce annually and produce abundant larvae, the latter <br />disappear before attaining juvenile size and there has been no <br />detectable recruitment in nearly four decades (Minckley 1983, <br />Minckley et al. 1991). Available evidence suggests that predation <br />by non-native species on early life stages is among the factors <br />responsible for this recruitment failure (Marsh and Langhorst <br />1988). Because of its size and extraordinary genetic diversity <br />(Dowling and Minckley, in press), the Lake Mohave razorback sucker <br />population is a focal point for recovery of this critically <br />imperiled species, and attempts to prevent its extirpation-are <br />vital to survival of the taxon. <br />Augmentation is considered a viable management alternative toward <br />perpetuation of razorback sucker in Lake Mohave. Although <br /> successful propagation and rearing techniques have been developed <br /> (Inslee 1982, Hamman 1987), stocking elsewhere of young fish