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to <br />Boat electrofishing was the only technique which proved effective <br />for sampling the adult riverine fishes. Passive gill net sets and <br />active gill net sweeps were attempted in 1984 but proved ineffective. <br />In 1984 and 1985, electrofishing was conducted with a 2500 watt <br />generator and a Coffelt VVP-15 mounted in a 14' jon boat powered by a <br />- 15 horsepower outboard. Electrofishing effibiency varied greatly with <br />-- river stage and conductivity. Following completion of each consecutive <br />0.8km section, all fish were measured, weighed and released. <br />Electrofishing effort (time pursuing fish, not including transitory <br />movement) was also recorded. <br />Electrofishing data were collected regularly from early July <br />through September, 1984 and between April and September, 1985. <br />Sampling was concentrated in the 8km above the reservoir basin, 8km <br />immediately below the dam axis, and in the four 0.8km Recovery stations <br />(R1-R4); the first located at Rangely, Colorado (RK I51.2) and the <br />remaining three at 8km intervals downstream. <br />A]1 tests for statistical significance were done using the Minitab <br />program and consisted primarily of analysis of variance and associated <br />F-tests unless otherwise stated. <br />In 1985, 1.6km of riverine habitat above the anticipated upper end <br />of Kenney Reservoir was inundated by the filing reservoir. For this <br />reason, the upstream study area was reduced from B.Okm to 6.4km <br />following impoundment. Due to the similarity of fish collections <br />from the recovery stations, data from these four sections were combined <br />and referred to collectively. <br /> <br />