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<br />x <br /> <br />Summary <br /> <br />The development and use of tolerance intervals is suggested <br /> <br />as an al ternative to probabil ity-of-use curves for model ing ap- <br /> <br /> <br />plications. For the rainbow and cutthroat trout in the Green <br /> <br /> <br />River, accurate modeling requires data stratification by species, <br />life stage, activ.ity, and season. It is important that predic- <br />tive models provide accurate velocities at the depths occupied by <br />the fish rather than using average column velocities. <br />For the activity of stationary swimming, fish velocity tend- <br />ed to increase and fish depth tended to decrease with increased <br />flows. For the activity of random swimming, fish often moved <br />along with changes in sheer edges as flows changed with little <br />..--- <br />resultant change in fish velocity. <br />There was a large difference between winter and summer dis- <br />tribution of the trout and in the importance of the two activi- <br />ties. Glides and rapids were the primary habitat for trout in <br />the summer. During the winter, fish were heavily concentrated in <br />.. <br />a few large pool s. Random swimming was observed infrequently <br />during summer but was common during winter. <br />Present low flow levels were the upper limit of plant bed <br />establishment. Plant beds were important in producing high in- <br />vertebrate biomass, especially Gammarus. <br />During the pre-test period in January 1982, trout occupied <br />habitats very similar to those occupied during January 1981. <br />Juvenile cutthroat trout were located higher in the water column <br />than the other life stages in 1982 and were physically isolated <br />