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nonnative predators find prey visually. In the evolutionary history of these <br />native fishes, there was little or no experience with visual predators. Given <br />the susceptibility to predation and their daytime activity, their behavior <br />would place them at risk. <br />Young Colorado pikeminnow have been stocked in streams and <br />rivers with less than satisfactory results, In one case, juvenile <br />pikeminnow were stocked in large numbers in Kenney Reservoir, near <br />Rangely, Colorado, in an effort to establish a sport fishery. In a very short <br />time, fish abundance decreased in the reservoir to the point where few <br />could be found. Sampling below the dam revealed that many of the <br />stocked fish had moved downstream and over the dam (Trammel et al. <br />1993). This fish movement can be understood in the context of our study <br />results. The young fish would be likely to move downstream in response <br />to any detectable water flow, which would lead them out of the reservoir. If <br />we are correct about this mechanism, it has important implications for <br />future stocking efforts. <br />Laboratory studies can lead to an improved understanding of the <br />behavior and ecology of these endangered fishes that would be virtually <br />impossible to obtain in the Colorado River. In addition, controlled studies <br />can suggest a need for improved field studies. As an example, our study <br />suggests that antecedent changes in river stage could influence estimates <br />of larval abundance in backwaters, and should be considered as part of an <br />ongoing fish monitoring program. This study also suggests that a better <br />understanding is needed about the downstream effect of flow regulation <br />from reservoirs; short-term oscillations in river stage may be very <br />disruptive and energetically costly if larvae respond by frequently moving <br />in and out of backwaters. <br />ACKNOWLEDGMENTS <br />This study was conducted at the Colorado River Fishes Project station at <br />Vernal, Utah with funding and support provided by the U.S. Bureau of <br />Reclamation and the U. S. Fish and Wildlife Service, which also issued <br />permits under provisions of the Endangered Species Act. Personnel from <br />the Dexter National Fish Hatchery provided larval fish. Technicians <br />involved in the construction of the test tank and collection of data from <br />trials also included J. Bigelow, J. Johnson, K. Paulin and L. Trinca. <br />LITERATURE CITED <br />Balon, E.K. 1984. Reflections on some decisive events in the early life of <br />fishes. Trans. Amer. Fish. Soc. 113:178-185. <br />Bestgen, K.R. 1996. Growth, survival, and starvation resistance of <br />Colorado squawfish larvae. Env. Biol. Fishes 46:197-209. <br />Fausch, K..D. and R.J. White. 19$3. Sinuous stream aquaria to simulate <br />lotic fish habitat. Prog. Fish Cult. 5:113-116. <br />Hamman, R.L. 1981. Spawning and culture of Colorado squawfish in <br />raceways. Prog. Fish Cult. 43:173-177 <br />Haynes, C.M., T. A. Lytle, E.J. Wick and R.T. Muth. 1984. Larval Colorado <br />534 <br />