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2.43 to 2.89, compared to 2.42 fish/h, 95% CI = 2.24 to 2.61 with 2002 data included). Also, of <br />nine species most often captured by electrofishing, five increased in mean abundance when 2002 <br />data were excluded and four decreased. Since inclusion of that data appeared to have little effect <br />on overall abundance values, we decided to retain 2002 data in all analyses. <br />Trammel net sampling was mostly confined to Whirlpool Canyon, because that reach <br />contained deep eddy habitat most likely to support humpback chub. A few trammel net samples <br />were collected in Mitten Park and Lodore Canyon. Multi-filament trammel nets (23 in long x <br />1.8 in deep; 25-cm outer mesh, 2.5-cm inner mesh) were set in late summer or autumn when <br />water temperatures were relatively low so that fish mortality would be minimized. In autumn <br />2003 we conducted three consecutive sampling trips (passes) in an attempt to obtain an <br />abundance estimate for chubs in Whirlpool Canyon. The main sampling sites for trammel nets <br />were in upper Whirlpool Canyon just upstream and downstream of Rain Camp (river kilometer <br />(RK) 550.8), at a large eddy pool about 1 km upstream of Jones Hole Creek (RK 546.4), and at <br />Compromise Camp (RK 544). Trammel nets were usually fished during crepuscular and <br />nighttime hours, and lesser amounts in day time, and were set in low velocity habitats and in the <br />separation zone of the main channel current and eddy pools (eddy lines). The number of nets set <br />(up to six) was contingent on habitat availability and accessibility. Nets were cleared of fish <br />every 2 h. Fish captured by electrofishing and trammel nets were measured (total length [TL]) <br />and sex and reproductive condition was noted, if discernable. Large samples of small-bodied <br />fish captured by electrofishing were counted. In addition, endangered fishes and roundtail chubs <br />were individually weighed and scanned for a passive interrogated transponder (PIT) tag. If none <br />was detected, a PIT tag was implanted and the fish was released. Special care was taken to <br />identify potential catostomid hybrids. We identified these based on morphological <br />characteristics of the mouth and body that were intermediate between putative parental types and <br />on intermediate squamation patterns and scale counts in the lateral series (Hubbs and Miller <br />1953). Vouchers of some specimens, including catostomid hybrids, were preserved in 10% <br />formalin and are housed at the Larval Fish Laboratory, Colorado State University. <br />10