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<br />I <br />I <br />I <br />I <br />I <br />I' <br />t <br />I r <br />I I B. <br />I l <br />I t <br />! t <br />'r <br />" <br />,I <br />I <br />I <br />J <br />I <br /> <br />bottom so that such ponds drain as high streamflows subside to provide <br />ephemeral floodplain habitats rather than permanent ones. <br /> <br />Four floodplain terraces and four floodplain depressions were reconnected <br />with the middle Green River as part of the Recovery Program Habitat <br />Enhancement/Restoration Subprogram. Nonnative minnows dominated the <br />catches of fyke/trammel net catches from these sites in 1997. Fathead <br />minnows composed between 14.9 and 76.2% of these catches and red shiners <br />accounted for 3.1 to 30.8% in the four terrace sites (G. Birchell, 1998, <br />personal communication). In one site, sand shiners dominated at 48.1% of <br />the catch but this species made up only a small portion (1.1 to 9.1%) of <br />the catches at the three other terrace sites. In the four floodplain <br />depressions that were reconnected with the middle Green River, fathead <br />minnows composed between 28.5 to 70.2% of fyke/trammel net catches in 1997 <br />(G. Birchell, 1998, personal communication). Red shiners were not very <br />abundant in the reconnected depressions with catches that ranged between 0 <br />and 9.5%. Green sunfish composed over one-fourth (25.2 and 26.5%) of the <br />catches at two depression sites but formed a relatively small portion of <br />the catches (2.6% and 9.8%) at the other two sites. Black bullheads <br />(Ictalurus melas) also made up from one-fourth to nearly one-third (24.3% <br />and 31.9%) at the same two sites where green sunfish were numerous but <br />were absent from one of the other reconnected depressions and made up 9.4% <br />of the catch at the remaining site. Carp composed nearly one-third of the <br />catch in one reconnected depression (29.3%) but were nearly absent at the <br />other three sites (0, 1.1, and 1.4% of the catches). <br /> <br />Competition. Although competition for food among larval and juvenile <br />fishes in the Upper Colorado River Basin has not been well documented <br />(Hawkins and Nesler 1991), the main reason is because competition among <br />freshwater fish species is often difficult to document due to the lack of <br />specialization in food habits by freshwater fish, resulting in much <br />overlap in their food habits (Larkin 1956). However, the extremely low <br />densities of zooplankton in backwaters during the spring runoff where <br />larval razorback suckers are now found and the high percentage of <br />nonnative fishes provides evidence that competition may also be an <br />important factor in the Upper Basin. Competition would probably be <br />reduced if productive floodplain habitats, with higher densities of <br />alternate food organisms occur, are reconnected with the main channels. <br /> <br />Beyers et al. (1994) documented in the laboratory that competition between <br />larval Colorado squawfish and larval fathead minnow occurred where growth <br />of both species was reduced through competition. Beyers et al. reported <br />that the "negative competitive effects were quantitatively greater and <br />more frequent for Colorado squawfish than for fathead minnows". Adult <br />nonnative minnows and juvenile razorback suckers feed on the same food <br />organisms so that nonnative minnows are not only predators on larval <br />razorback suckers but may also be important competitors with juvenile <br />razorbacks. <br /> <br />Competition by two species occurs when food is limited, the food is <br />shared, and one of the two species is adversely affected by sharing food <br />(Connell 1983; Crombie 1947; Elton 1946; Hardin 1960; Larkin 1956; Li and <br />Moyle 1993; Moyle et al. 1986; Schoener 1982; Tilman 1982; Underwood <br />1986). Species that are more efficient at capturing and converting food <br />into biomass will persist for a longer time as food resources become <br />scarce (Schoener 1982; Tilman 1982). Such competitive interactions can <br />change the structure of a fish community (Werner 1984). Density-dependent <br />processes are often reflected in reduced growth rather than direct <br />mortality in juvenile and adult fish (Schoenherr 1977) . <br /> <br />Dietary overlap was reported between nonnative and native fishes in the <br />Upper Basin (Jacobi and Jacobi 1982; Grabowski and Hiebert 1989; Muth and <br /> <br />25 <br />