Laserfiche WebLink
ABSTRACT <br />Flaming Gorge Reservoir is located in southwest Wyoming and northeast Utah <br />and is jointly managed by the two states. The reservoir has a maximum surface <br />area of 42,000 acres and is 91 miles long at a maximum elevation of 6,040 feet <br />above sea level. The reservoir has been divided into three distinct areas based <br />upon topography, geology, hydrographic features, limnology, and distribution of <br />fishes: Inflow Area, Open Hills Area, and Canyon Area. <br />Before the gates on the reservoir were closed and the reservoir began <br />impounding water in November 1962, the Green River was chemically treated with <br />rotenone to control undesirable fish species. Rainbow trout were initially <br />planted in the reservoir and provided an excellent fishery. Creel rates and <br />harvest peaked in 1965. A general decline of the rainbow fishery has occurred <br />since that time, primarily because of establishment and expansion of Utah chub <br />and white sucker populations. Brown trout were stocked in the Inflow Area in <br />1966 to utilize Utah chubs. By the late 1970's, Flaming Gorge was a.nationally <br />acclaimed trophy brown trout fishery. By 1980, a developing lake trout fishery <br />was also"recognized. Lake trout had become established through downstream drift <br />from the Finger Lakes in the upper Green River drainage. In 1982, management of <br />the reservoir was changed to recognize the trophy fishery represented by the <br />large brown and lake trout. <br />A total of 20.9 million trout were planted in the reservoir during the study <br />period (July 1, 1977-June 30, 1983). Most of the trout planted (75 percent) <br />were rainbow and 14.4 percent were brown trout. Two strains of cutthroat trout <br />and lake trout accounted for the rest. Most of the trout were barge-planted to <br />insure uniform distribution. Other game fish planted included kokanee salmon, <br />channel catfish and smallmouth bass. Forage fish introductions included the <br />Bear Lake sculpin and Bonneville cisco. <br />Over 3 million trout were marked during the study period to provide data on <br />movement, survival, longevity, growth, and return to the creel. Identification <br />of marked trout was done during creel surveys and trend sampling (gill nets and <br />purse seine). <br />Year-round programmed creel surveys were conducted in 1978 and 1982, using <br />angler interviews and aerial c9unts. During 1979, 1980, and 1981, creel surveys <br />were run from April-September and consisted of angler interviews only. Harvest <br />and use estimates are presented and compared with creel data from 1964-1977. <br />The data document the continued decline of the harvest, led by the collapse of <br />the rainbow fishery. <br />Analysis of the programmed creel data indicates a harvest of 155,755 fish in <br />695,817 man-hours at a rate of 0.22 fish per hour in 1978 and a harvest of <br />161,528 fish in 670,891 man-hours at a rate of 0.24 fish per hour in 1982. <br />Rainbow trout continued to lead the harvest followed by lake and brown trout, <br />smallmouth bass, kokanee salmon and cutthroat trout. The reservoir yielded an <br />average annual harvest of 4.7 pounds/acre during the project period. <br />Harvest of lake trout has increased dramatically since 1975. In 1979, about <br />2.4 pounds/acre of lake trout were harvested and an annual average of 1.6 <br />-i-