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<br />measured using a Marsh-McBirney Model 201 current meter. Negative velocity <br />was recorded if direction of current flaw deviated more than 90 degrees from <br />that of the main channel current. Substrate was identified visually or by <br />'feel' by probing with the depth rod. substrate was categorized as a <br />ccaabinaticn of primary and secondary couponents of clay, silt, sand, gravel, <br />cobble, or boulder. cover designations included vegetation, brush, and <br />boulder. ' <br />Three sets of measurements were taken at each site; one set was at the <br />triangulated fish location (main site) with additional sets taken 1-2 m, <br />nine toward shore and "but" away from shore. Velocity measurements at the main <br /> <br />site were taken at 0.2, 0.6, and 0.8 depths from the water surface when ice ' <br />free or from the bottom of the ice during ice cover. At the in and out <br />measurement sites, velocity was measured at 0.6 depth. During ice cover, <br />habitat measurements were taken through holes drilled in the ice. Boles were ' <br />drilled using either an 8-inch strikemaster hand auger or 7-inch Strikemaster <br />gasoline powered auger. Additional measurements were then taken to determine <br />ice-free water depth (effective depth). These included solid ice thickness <br /> <br />(ice below the water surface in the hole), frazil ice thickness, and total ' <br />depth (water depth in the hole). Water depth below the surface of the ice was <br />then calculated by subtracting ice thickness from total water depth (Figure <br /> <br />4). Tien frazil ice was present under the hard ice cover, its thickness was ' <br />determined by lowering the velocity probe to the bottom, getting a positive <br />velocity reading, and then slowly raising the probe until the frazil could be <br />felt touching the probe and velocity decreased to 0.0 feet per second (ft/s). <br />The compact, non-moving, frazil ice deposits were treated as solid ice in <br />making water depth and velocity measurements (Figure 5). Winter discharge <br />measurements recorded at the United States Geological Survey (USGS) gaging <br />station near Maybell, Colorado, were used during Winter 1 to provide a record <br />of flow conditions. <br />Habitat Measurements Winter 2 <br />During Winter 2, habitat mats were made at fish locations where <br />fish spent 15 minutes or more. Velocity was measured at 0.6 depth only. In <br />and out measurements were not taken unless extreme variation was suspected in <br />a habitat. <br />Th obtain accurate discharge data, a cross section station was <br /> <br />established at RU 81.1 near Maybell, and flow determinations were made on ' <br />each biweekly trip. Fence posts wpxe driven into each bank to mark the <br />location. Holes were drilled through the ice 5 feet apart near the same <br />location each trip for water depth, ice thickness, and velocity moments. ' <br />Velocity was measured using a Marsh McBirney model 201 Current meter. <br />cross sections were also established through embayment and backwater <br />habitats at III 81.1 and 95.7. Measurements of water depth and ice thickness <br />were taken from the same locations biweekly to determine how these habitats <br />changed throughout the winter under various flow and tagmratrure conditions. <br />In addition, all cross section measurements were referenced to known bencrmiark <br /> <br />elevations at each site by means of survey level to record elevation changes ' <br />of the ice surface, water surface, and river bed throat the winter. <br />A series of dissolved oxygen measurements was taken during mid-winter to <br />determine if oxygen depletions were occurring as a result of heavy SHOW ' <br />covering the ice for an extended period. Measurements were taken by lowering <br />12 ' <br />