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fishes at a 1.9-km-long upper Lodore Canyon site near upper Wade and Curtis Campground <br />(river kilometer (RK) 581), and a 1.6-km-long lower Lodore Canyon site near Alcove Brook (RK <br />561). To make valid comparisons with their fish composition data, we used a subset of our <br />samples collected in a 4.8 RK reach encompassing their fixed stations. Recognizing that there <br />are potential biases, we combined seine and electrofishing data for these comparisons to be <br />consistent with Holden and Crist (1981). We then assessed changes in species composition <br />between the two periods by comparing the number and relative abundance of native and <br />introduced species captured in each period. We acknowledge that differences in habitat, <br />collecting gear, and sampling effort may affect assessments of faunal differences between the <br />two periods. Therefore, our qualitative assessments of temporal change were conservative. <br />Longitudinal changes in the fish community, 1994-1996.-Longitudinal species abundance <br />patterns correlated with downstream temperature shifts may facilitate understanding of how <br />Flaming Gorge Dam influences the fish community. Analyses of longitudinal shifts in <br />community composition were conducted both for small-bodied fishes captured primarily by <br />seining and for large-bodied fishes captured primarily by electrofishing. Seine samples of small- <br />bodied fishes were collected from six mostly contiguous Green River reaches: a Browns Park <br />reach, four 8-RK reaches within Lodore Canyon, and an Island and Rainbow parks reach. <br />Lodore Canyon fish samples were divided among the four relatively short reaches to facilitate <br />detection of downstream shifts in community composition and structure. The upper terminus of <br />the first and most upstream Lodore Canyon reach extended from RK 586.9 downstream to RK <br />579. The second reach extended from RK 578.9 downstream to RK 571, the third reach from <br />RK 570.9 to RK 563, and the fourth from RK 562.9 to RK 555, the confluence of the Green and <br />Yampa rivers. Samples were also collected in a seventh reach, the lower 2 km of the Yampa <br />River. Yampa River collections were used to compare and contrast the fish community of a <br />warm, unregulated river to the fish community present in a regulated river that is affected by cold <br />water releases and altered discharge patterns. <br />9 <br />