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Last modified
7/14/2009 5:02:36 PM
Creation date
5/22/2009 7:28:33 PM
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UCREFRP
UCREFRP Catalog Number
9556
Author
Bestgen, K. R., K. A. Zelasko and C. T. Wilcox.
Title
Non-native fish removal in the Green River, Lodore and Whirlpool canyons, 2002-2006, and fish community response to altered flow and temperature regimes, and non-native fish expansion.
USFW Year
2007.
USFW - Doc Type
115,
Copyright Material
NO
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abundance and CPUE indices tracked each other closely so we present mostly relative <br />abundance data here. <br />RESULTS AND DISCUSSION <br />Effects of~Flaming Gorge Dam on Green River discharge and temperature patterns, <br />Lodore Canyon.-We present extensive information on historical and present-day streamflow <br />and temperature patterns of the Green River because we believe they are a significant influence <br />on fish distribution and abundance patterns for the associated time period. Further, detailed <br />understanding of dam operations may also allow predictions to be made about effects of flow <br />and temperature regimes to the extent that such may be useful to manage distribution and <br />abundance of fishes. Summaries are also available in Bestgen and Crist (2000) and Bestgen et <br />al. (2006), but are brought up to date and presented here for the convenience of the reader. Four <br />major dam-related events affected physical habitat and the fish community of the upper Green <br />River: dam installation in 1962, penstock modification in 1978, flow re-regulation beginning in <br />1992, and higher peak flows, lower base flows, and drought events since 1997. Prior to <br />construction of Flaming Gorge Dam, discharge patterns of the Green River exhibited high spring <br />peaks followed by lower, stable base flows in other seasons, particularly winter (Fig. 2). Water <br />temperature ranged from a low of 0°C in winter to over 22°C in summer (Fig. 3) and turbidity <br />increased seasonally from inputs of fine inorganic silts (Vanicek et al. 1970). Immediate dam <br />effects included inundation of riverine habitat in the reservoir zone. Downstream, naturally <br />variable and relatively high spring discharge maxima were reduced (Fig. 4). Power plant <br />operations increased base flow levels and daily discharge fluctuations. Naturally turbid water <br />was cleared when virtually all sediment was trapped behind the dam. Water drawn from the <br />hypolimnion of the reservoir reduced temperature of summer releases to about 6°C after <br />reservoir filling was completed in 1967. Downstream warming occurred but mean monthly <br />summer water temperatures reached a maximum of about 14°C in the post-dam period in Lodore <br />14 <br />
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