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Last modified
7/14/2009 5:02:35 PM
Creation date
5/20/2009 10:07:26 AM
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UCREFRP
UCREFRP Catalog Number
9413
Author
Osmundson, D. B.
Title
Flow Regimes for Restoration and Maintenance of Sufficient Habitat to Recover Endangered Razorback Sucker and Colorado Pikeminnow in the Upper Colorado River.
USFW Year
2001.
USFW - Doc Type
Grand Junction.
Copyright Material
NO
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May or June only). Selection of runs changed toward the end of spring when use of higher <br />velocity sites increased: slow runs declined in use from 32% (April) to 27% (May) to 13% <br />(June); during the same period, fast runs increased in use from 0-3% to 19%. <br />Summer <br />During summer, flows decline in magnitude from relatively high levels in July to the <br />yearly low in September and water temperatures are at an annual high during July and <br />August. Use of fast runs peaked in July at 26% and then tapered off to 7% in September. <br />Conversely, use of slow runs increased during this period: after reaching an annual low in <br />late spring (13%) use steadily increased through summer (26-55%) and peaked during the <br />transitional month of October (61%). Together the two run types accounted for 49-52% of <br />habitats selected during summer. Backwaters were little used during this time (3-7%) and <br />flooded gravel pits were largely unavailable. Shorelines and rapids each accounted for only <br />04% use. Annual use of riffles was highest during the summer months but use was <br />relatively low compared to other habitat types (3-10%). Colorado pikeminnow use of <br />eddies also reached a yearly high during summer (9-16%). Pools were also used (13-16%), <br />but as in spring, summer use of pools was low compared to the remainder of the year. <br />Eddies, pools and backwaters were the preferred habitat types of adult pikeminnow in the <br />15-mile reach during summers with moderate base flows (Fig. 2). During summers of low <br />flow, slow runs and fast runs were preferred. <br />Transitional periods <br />Flows and temperatures are low during October and March and changes in fish <br />habitat use indicated these were transitional months that marked the beginning and end of <br />winter. Water temperature during October is somewhat higher than during March. Pools <br />and slow runs were primarily selected during these months: pool use accounted for 32% in <br />March and 26% in October; slow runs, 43% in March and 61% in October. Large <br />backwaters were used 14% of the time in March and 9% in October. Other habitat types <br />were used little or not at all: eddies were used 4-7%; fast runs 04%; riffles, rapids, <br />shorelines were not used and flooded gravel pits were unavailable. <br />14
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