Laserfiche WebLink
<br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br /> <br />INTRODUCTION <br /> <br />Flaming Gorge Dam on the Green River of northeastern Utah became <br />operational in November of 1962. A rainbow trout fishery was <br />established in the first 26 miles of the dam's cold tailwaters in Utah. <br />From 1963 until 1967 this section of river was considered one of the <br />best cold water fisheries in the U.S. This fishery declined signifi- <br />cantly in the late 1960's and 1970's and overly~cold water temperatures <br />were hypothesized to be the reason (Mullan et ale 1976). The dam, with <br />its reservoir and cold tailwaters, along with a pre-impoundment fish <br />eradication program, has been implicated as a major decimating factor of <br />native Green River fish populations, especially those of the Colorado <br />squawfish (Ptychocheilus lucius) and humpback chub (Gila cypha), pre- <br />sently considered "endangered" (Miller 1963, Seethaler 1978). <br />Modifications of the penstock inlets of Flaming Gorge Dam were installed <br />in early 1978 for the purpose of warming the tail waters so the trout <br />fishery could be improved. It was also anticipated that the warmer <br />flows would enhance the conditions necessary for successful reproduction <br />of the rare fish populations in Dinosaur National Monument, especially <br />Colorado squawfish. These modifications became operational on June 30, <br />1978. The Water and Power Resources Service funded two studies to moni- <br />tor the effects of the inlet modification. The Utah Division of <br />Wildlife Resources (DWR) studied the trout fishery from the dam to the <br />Utah border (29 miles below the dam, hereafter MBD); BID/WEST, Inc., <br />studied macroinvertebrates for 85 miles below the dam and the fishes for <br />75 mi 1 es be 1 ow the Utah DWR trout fi shery study area for three years. <br />