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<br /> <br />254 <br /> <br />Figure 9.4. Various floodplain <br />habitats in the floodplain of the <br />upper Colorado River basin. <br />(a) 1993 flooding of a depression <br />wetland (Wyasket Bottom) on the <br />Ouray National Wildlife Refuge <br />along the middle Green River <br />(potential nursery habitat for <br />larval razorback suckers). <br />(b) Shallow embayment along the <br />Colorado River in Canyonlands <br />(nursery habitat for Colorado <br />squawfish). (c) A 147-ha <br />depression wetland (Old Charley <br />Wash) in the floodplain of the <br />middle Green River (larval <br />razorback suckers survived <br />through the first summer of life in <br />this wetland). (d) Flooded <br />tributary and backwater (Millard <br />Canyon) in the lower Green River <br />(ephemeral habitat for larval <br />razorback suckers). <br /> <br />Flooding and Aquatic Ecosystems <br /> <br /> <br /> <br />of chironomids than river backwaters because of a longer life cycle of <br />chironomids compared with the high turnover rate of zooplankton. <br />Even though survival of larval razorback suckers was high when zoo- <br />plankton densities were about 60 organisms per fish per day. growth was <br />less until the zooplankton density was 500 organisms per fish per day or <br />more (Figure 9.3). Reduced growth of larval razorback suckers may result <br />in higher mortality through predation by nonnative fishes (Leggett, 1986) <br />because the larvae are in poor condition (i.e., starved) with less locomotive <br />ability (Rice et aI., 1987). <br />