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Last modified
7/14/2009 5:02:35 PM
Creation date
5/17/2009 10:51:31 PM
Metadata
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UCREFRP
UCREFRP Catalog Number
9410
Author
Wydoski, R. S. and E. J. Wick.
Title
Ecological Value of Floodplain Habitats to Razorback Suckers in the Upper Colorado River Basin.
USFW Year
1998.
USFW - Doc Type
Denver.
Copyright Material
NO
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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 />
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