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Last modified
8/11/2009 11:32:58 AM
Creation date
8/10/2009 5:03:59 PM
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UCREFRP
UCREFRP Catalog Number
9549
Author
Bestgen, K. R., K. A. Zelasko, R. I. Compton and T. Chart.
Title
Response of the Green River Fish Community to Changes in Flow Temperature Regimes from Flaming Gorge Dam since 1996 based on sampling conducted from 2002 to 2004.
USFW Year
2006.
USFW - Doc Type
115,
Copyright Material
NO
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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
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