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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