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Last modified
7/14/2009 5:02:37 PM
Creation date
5/24/2009 7:10:54 AM
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UCREFRP
UCREFRP Catalog Number
9678
Author
Tyus, H. M. and C. A. Karp.
Title
Habitat Use and Streamflow Needs of Rare and Endangered Fishes
USFW Year
1990.
USFW - Doc Type
Flaming Gorge Studies - Draft Consolidated Report Preliminary.
Copyright Material
NO
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T <br />to 1.37 m, and mean column velocity of 0 to 0.3048 mps. ...The areas used by <br />the fish (razorback sucker) were characterized by average water depth of <br />0.6096 to 1.37 m, and mean column velocity of 0.03 to 0.335 mps. <br />Overwintering adult Colorado squawfish rested in midchannel slow runs and <br />slackwaters and fed in eddies and backwaters. Average gross movement rate of <br />adult Colorado squawfish in eddies and backwaters (48.20 m/h) was <br />significantly greater than in slow runs and slackwaters (21.71 m/h), <br />indicating a foraging behavior in the former habitats and a resting mode in <br />the latter. These observations suggest that overwintering adult Colorado <br />squawfish rest in deep midchannel habitats with low velocity and feed in <br />shoreline eddies and backwaters. <br />...Significantly greater local movement was exhibited by adult Colorado <br />squawfish and razorback suckers exposed to fluctuating river levels that <br />exceeded 5 cm/h. ...Microhabitats used by these fish were altered or shifted <br />by the fluctuating flows, causing the fish to move. We concluded from these <br />observations that flow fluctuation rates greater than 5 cm/h caused about 190 <br />percent greater movement in adult Colorado squawfish and 39 percent greater <br />movement in adult razorback suckers. <br />Movement of adult Colorado squawfish and razorback suckers under <br />fluctuating flows was increased when shifting and floating ice masses occurred <br />during periodic breakups. ...A subsequent increase in flow often dislodged <br />and transported the ice downstream, causing fish to move to dodge the ice <br />masses. Thus, maximum flow fluctuations caused ice buildup and transport in <br />January and February and caused additional movement by the radiotagged fish. <br />...Flow fluctuations of sufficient magnitude to cause fish to move <br />extended as far downstream as Bonanza Bridge, about 192 km downstream of <br />Flaming Gorge Dam. We concluded that these adult endangered fish in the upper <br />88 km of their distribution in the Green River can be expected to move more <br />frequently than fish further downstream in order to remain in suitable <br />microhabitat. The effect of this energy expenditure on survival, growth, and <br />reproductive potential is unknown. <br />Flow release scenarios from Flaming Gorge Dam ... of 22.64 m3/s followed <br />by a maximum release of 118.86 m3/s for 8 hours resulted in a stage change <br />sufficient to cause fish movement as far downstream ~s the Bonanza Bridge, 192 <br />k~ from Flaming Gorge Dam. A flow release of 22.64 m /s followed by 118.86 <br />m /s for 4 hours resulted in a stage change rate of 5 c~/h or greater as far <br />downstream as Jensen. Flow release of 22.64 to 118.86 m /s for 2 hours did not <br />produce a stage change rate greater than 5 cm/h within the current known <br />distribution of adult Colorado squawfish and razorback suckers (abstracted <br />from Summary of Findings). <br />Report 4- Winter Habitat Use of Young Colorado squawfish (Tyus, in prep.) <br />Shoreline habitats and general river conditions were studied during the <br />winters of 1987-88 and 1988-89. Weather conditions differed between the two <br />winters, but ice cover generally formed by mid-December. Few fish were <br />captured using baited minnow traps, but 5 young Colorado squawfish were <br />collected in one backwater in December 1987 and one hatchery-reared juvenile <br />razorback sucker was captured in 1988. Fluctuating flows in 1987-88 caused <br />shoreline scouring in the Jensen area by moving blocks of ice, and alternate <br />flooding and dewatering of low-lying areas at Ouray due to ice jams. Lower, <br />more stable flows in 1988-89 resulted in shallower backwaters but less <br />shoreline scouring (Preliminary abstract). <br />8 <br />
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