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<br />predation at that time by minnows since other food organisms are scarce to the <br />abundant nonnative minnows. <br /> <br />Potential Role of Comoetition on Survival of Fish Larvae. Although competition <br />for food among larval and juvenile fishes in the Upper Colorado River Basin has <br />not been documented (Hawkins and Nesler 1991), documentation of competition is <br />difficult because proof is often lacking that food resources are limiting fish <br />numbers. <br /> <br />Competition by two species occurs when food is limited, the food is shared, and <br />one of the two species is adversely affected by sharing food (Moyle et al. 1986; <br />Li and Moyle 1993). Low numbers of zooplankton occur in the main channel and <br />backwaters of rivers (i.e., food is limited for early life stages of fish) in the <br />Upper Colorado River Basin (Tables 1 and 2; Cooper and Severn 1994a, b, c, d; <br />Grabowski and Hiebert 1989; Mabey and Schiozawa 1993). Dietary overlap was <br />reported between nonnative and native fishes (i.e., food is shared) in the Upper <br />Colorado River (Jacobi and Jacobi 1981; Grabowski and Hiebert 1989; Muth and <br />Snyder 1995). Nonnative fishes expanded rapidly in the Upper Basin between 1986 <br />and 1994 as indicated from the Interagency Standardized Monitoring Program where <br />they constitute 96.7 to 99.6% of the tot a 1 numbers of fi sh collected from <br />backwaters by seining (McAda et al. 1994a, 1994b, 1995). Native and nonnative <br />fish share the same backwater habitats. Although direct competition among <br />endangered fi shes by nonnat i ve fi shes has not been documented, 1 i mited food <br />resources, sharing of the food resources, and use of the same habitats with low <br />water velocity supports the belief that competition may have contributed to the <br />decline of some native Colorado River fishes. Red shiners and fathead minnows <br />were found to constitute 90.4% of 149,489 fish collected by seines between 1986 <br />and 1994 from primary backwaters of the Colorado and Green rivers during the <br />Interagency Standardized Monitoring Program (McAda et al. 1994a, 1994b, 1995). <br />These minnows feed on the same foods items that are used by juvenile endangered <br />fishes (Grabowski and Hiebert 1989; Jacobi and Jacobi 1982) and, more than <br />likely, compete with the endangered fishes -- particularly during the early <br />spring when food organisms are scarce in the high and turbid upper basin rivers. <br /> <br />Sand shiners (Notroois stramineus) are also abundant in the backwaters of the <br />Colorado and Green rivers (McAda et al. 1994a, 1994b, 1995) but this species is <br />not been reported to feed on fish larvae. Sand shiners are generalists that feed <br />on a variety of aquatic or terrestrial insects and crustaceans (Muth and Snyder <br />1995). Although sand shiners may not be predators upon the endangered Colorado <br />River fishes, they could be potential competitors with them. <br /> <br />XI. LOSS OF CRITICAL LOW WATER VELOCITY HABITATS <br />SUCH AS <br />FLOODED BOTTOM LANDS IN THE UPPER COLORADO RIVER BASIN <br /> <br />Flooded bottomland habitats occurred in low gradient river reaches with <br />unrestricted meanders that occur in broad valleys. In the Upper Colorado River <br />Basin, these reaches have been channelized by levee development to contain the <br />river near population centers and agricultural areas (Bestgen 1990; Fradkin 1983; <br />Quartarone 1993). It is hypothesized that the loss of flooded bottomlands is one <br />factor has adversely affected the food base required by larval endangered fishes. <br />The lack of recruitment of the endangered Colorado River fishes is also linked <br /> <br />11 <br />