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<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 />conditions were determined with the aid of a literature review, as well <br />as portions of the 1978 data. <br />Field sampling was conducted in March, June, August, and October of <br />all years. A July sample was added in 1978 in an attempt to increase <br />the amount of "before" data. Macroinvertebrates and fish samples were <br />both taken during each sampling period. Yampa River samples were taken <br />only in June, August, and October of 1978, and the Lower Yampa station <br />was not sampled in March of 1979 and 1980 due to inaccessibility. <br />Macroinvertebrates <br />Macroinvertebrates were sampled in cobble-rubble substrates in a <br />stratified random sampling design at each of the six stations. A Hess <br />type invertebrate sampler was used to obtain a one square foot sample. <br />Four samples were taken at each station. The samples were preserved in <br />70% ethyl alcohol in Whirl-Pak bags, and transported to BID/WEST's lab <br />for analysis. High water samples were avoided in the Green River above <br />Echo Park by proper timing of collection, except at Wade and Curtis. <br />Samples containing fewer than 400-500 organisms were sorted in their <br />entirety. Samples with larger numbers of organisms were initially <br />sorted to remove large organisms such as stoneflies and any uncommon <br />smaller organisms. The sample was then subdivided by a rotary device <br />which portions the sample into eight equal subsamples. Subsamples were <br />randomly chosen and counted. The number of subsamples enumerated was <br />dependent on the numbers of organi sms. Generally, the 1 arger the num- <br />bers of invertebrates in a sample, the fewer the number of subsamples <br />necessary. In each case, at least ~ of each sample was picked to avoid <br /> <br />-7- <br />