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<br />Each cluster was numbered and 9 clusters were selected from strata 1, 11 from strata 2, 3 from <br />strata 3,2 from strata 4, 12 from strata 6, and 13 from strata 8 in 1996. The rest will be sampled in <br />1997 (Table 2). <br /> <br />Table 1 . The river mile and location of sample strata (river reaches) in the Yampa River, Colorado, <br />1996. <br /> <br />I Strata I River Mile I Description I <br /> 1 0-20 Echo Park to Harding Hole <br /> 2 20-45.0 Harding Hole to Deerlodge Park <br /> ., 45.0-51.0 Deerlodge Park to Little Snake River Confluence <br /> .) <br /> 4 51.0-55.6 Little Snake River Confluence to Cross Mountain <br /> 5 55.6-58.8 Cross mountain Canyon <br /> 6 58.8-88.7 Cross Mountain Canyon to Juniper Canyon <br /> 7 88.7-91.0 Juniper Canyon <br /> 8 91.0-124.0 Juniper Canyon to Round Bottom <br /> <br />Habitat features were determined for a riffle:run sequence using cross sectional profiles. <br />Cross sections were made between headpins on both sides of the channel and measured the bed <br />profile and water surface elevations and also depth, velocity and substrate at 25 to 30 points. The <br />first cross section was placed at the most suitable hydraulic control in the cluster. Cross sections <br />upstream of the control were positioned to describe the lower run, middle run, pool or upper run, <br />lower riffle, and at the shallowest part of the rime. Cross sectional measurements were taken in <br />September during the low flow period. Only one stage-discharge measurement was taken at each <br />cross section. The range of concern for habitat availability was at flows of less than about 200 to <br />300 cfs. Therefore, as long as field readings were within this range, only one calibration flow was <br />considered necessary. <br /> <br />Habitat types were defined by a certain combination of depths and velocity. Instead of <br />assigning suitability values for depth and velocity for a species and life stage, we characterized the <br />river into six discrete habitat types. Three of these habitat types are considered usable by adult <br />Colorado squawfish and three of them are not (Table 3). Class I and Class II pools (over 2m and <br />1 m, respectively), were used by Wick and Hawkins (1986) in their habitat suitability model for <br />adult Colorado squawfish. Their determination was that adult CS were 2.5 times more likely to be <br />caught fi-om pools over 2 m deep than in pools between 1 and 2 m of depth. They also reported that <br />pools less than 25 square meters were considered unused. Habitat use information obtained by <br />radio tracking during the study was also used to validate the criteria used to define usable habitats <br /> <br />17 <br />