Laserfiche WebLink
<br />of nonnative adult red shiners on the mortality of larval Colorado squawfish decreased 5-40% as <br />growth rates of larvae increased by O,l-mm increments from 0.2 to 0.6 mm TL/d. Predation by <br />adult red shiners on larvae of native catostomids in flooded and backwater habitats of the Yampa, <br />Green, or Colorado rivers was documented by Ruppert et al. (1993) and Muth and Wick (1997). <br />Horn (1996) concluded that although nutritional limitations in Lake Mohave may directly <br />contribute to the high mortality of larval razorback suckers, a greater problem is reduced growth, <br />which keeps larvae at a size vulnerable to predation for longer period of time. He further stated <br />that apparently all razorback sucker larvae in Lake Mohave, starving or not, are consumed by <br />nonnative fish predators. <br /> <br />Management Implications <br /> <br />Most collections of wild adult razorback suckers in rivers of the upper Colorado River <br />basin have occurred in unconfined floodplain reaches (Modde et al. 1995; Muth 1995), and the <br />greatest expanse of floodplain habitat in the upper basin is in the Jensen and Ouray reaches of the <br />middle Green River (Irving and Burdick 1995), coincident with the largest extant reproducing <br />population. Floodplain wetlands inundated and connected to the main channel by spring-runoff <br />discharges appear to be important habitats for all life stages of razorback sucker (e.g., <br />Osmundson and Kaeding 1989; Tyus and Karp 1989, 1990, 1991; Modde 1996, 1997; Modde et <br />al. 1996). Floodplain wetlands are typically warmer and more productive than the adjacent river, <br />have abundant vegetative cover, and the natural integrity of large-river ecosystems is dependent <br />on interactions between the main channel and floodplain (Welcomme 1985; Junk et al. 1989; <br />Ward 1989; Stanford 1994; Ward and Stanford 1995; Brookes 1996; Wetzel and Ward 1996; <br />Wydoski and Wick 1998). <br />The seasonal timing of razorback sucker reproduction suggests an adaptation for utilizing <br />floodplain wetlands. Tyus and Karp (1990) and Modde and Wick (1997) reported that adult <br />razorback suckers in the middle Green River moved into flooded habitats (e.g., wetlands and <br />tributary mouths) shortly before or after spawning. They suggested that this movement was <br />related to temperature preferences and food abundance. Razorback sucker larvae drift <br />downstream after swimup and are transported into nursery habitats. Enhanced growth of larval <br /> <br />22 <br /> <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I' <br />I <br />I <br />I <br />I <br />I <br />