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<br />1985) suggests that these non-native predators may be competing with and/or <br />preying on Colorado squawfish. Although Pimental et al. (19$5) found that <br /> <br /> <br /> <br /> <br />1 <br />1 <br /> <br /> <br />n <br /> <br /> <br /> <br />LI <br /> <br /> <br />Colorado squawfish did not prefer channel catfish as prey, incidence of <br />channel catfish lodged in throats of adult Colorado squawfish (McAda 1983, <br />Pimental et a1. 1985, Wick et aI. 1985) suggests that these introduced fish <br />may adversely affect survival of Colorado squawfish. <br />Captures of adult Colorado squawfish with lures and bait in Yampa River <br />(FWS unpublished data, Salle 1980) su~~ests that large individuals are <br />susceptible to angling pressure. FWS records (Vernal, UT) show that in some <br />years, as much as ZO% of the tagged Colorado squawfish are angler-caught. <br />Martinez (1986) has also noted several instances of incidental takes in the <br />White River, Increases in fis'ning pressure and incidental ta'ces could <br />significantly impact Colorado squawfish abundance. <br />Reproductive success of Colorado squawfish is dependent upon a number of <br />interdependent factors including number of spawning adults (particularly <br />numbers of ripe females), river dischar~~, ~N~.liment load, temperature, and <br />photoperiod. Loss of successful reproduction in one or more years could <br />result in significant declines of Colorado squawfish, and aid proliferation of <br />non-native competitors. <br />Because Colorado squawfish eggs are ad'nesive and attach to substrate <br />surfaces, availability of cleaned cobble and boulder surfaces in spawning <br />areas may be limiting, if spring/early summer scouring action from high <br />sediment loads is curtailed by a reduction in spring peak flows. A gradual <br />decrease in summer flows aids in preventing siltation of cobble bars, and this <br />flushing flow is potentially Limiting. <br />33 <br /> <br />