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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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2002 to 2004 study period also had a more stable, albeit slightly higher than historical, summer- <br />winter base flow pattern because power generation fluctuations at Flaming Gorge Dam were <br />minimized. In Lodore Canyon, drought in 2002 to 2004 resulted in low base flows, and thermal <br />regimes in the study area were more similar to those in the pre-dam era than during any other <br />post-impoundment period. This ensured a close match of Green and Yampa River water <br />temperatures during drought years when Colorado pikeminnow larvae were drifting downstream <br />from the Yampa River in summer. <br />Green River peak flows in Whirlpool Canyon in the pre-impoundment period showed a <br />typical dome-shaped hydrograph, with low late-summer, autumn, winter, and early-spring base <br />flows, rising to a peak in late spring and early summer. Post-impoundment Green River peak <br />flows in Whirlpool Canyon were lower and arrived earlier than historically, an effect of Flaming <br />Gorge Dam. Whirlpool Canyon flow peaks during 2002 and 2004 were lower than the historical <br />average while the 2003 peak flow exceeded the average historical condition (1946 to 1962). <br />Base flows in Whirlpool Canyon in the 2002 to 2004 period matched the historical average <br />pattern reasonably closely. Thermal regimes in 2002 to 2004 were similar to historical ones <br />because dam-related cooling was probably overwhelmed by enhanced warming during low <br />flows. <br />We used raft-based electrofishing gear, seines, drift nets, and trammel nets to sample <br />Green River fishes from Browns Park downstream to Island-Rainbow Park. When data <br />obtained with all gears were combined, native fishes in the 2002 to 2004 period comprised only <br />10.3% of total catch and non-natives were 89.3%; the remaining 0.4% were hybrids. Fish <br />species richness was lowest in upstream reaches and cold-water or cool-water tolerant species <br />were more abundant in electrofishing samples. Predominant taxa included brown trout, white <br />sucker, fathead minnow, and mountain whitefish. Species richness was higher in downstream <br />v
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