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5. <br />Colorado River - Middle of the Black Rocks area in Ruby Canyon <br />(immediately below fish collection site F). This reach is <br />unique and does not represent other portions of the canyon above <br />or below Black Rocks. Numerous squawfish and humpback chubs <br />have been captured in this exceptionally deep area (Sealing, <br />et al. 1975). <br />METHODS <br />Aquatic habitat within the trend zones was assessed in two distinct <br />ways. First, a float trip was conducted through each trend zone and general <br />geomorphologic,land use and riverine features noted. This procedure allowed <br />detailed visual assessment of areas and activities which might change in scale <br />or nature such as irrigation, gravel mining, mechanical stream channel changes, <br />road maintenance, grazing, bankside stabilization or urban development. Also, <br />the general vegetative covEr on alluvial islands and both streaw banks was <br />characterized by density and type. Stream depths were measured continuously <br />during float trips, and notations made of areas providing especially deep or <br />critically shallow waters. Very shallow areas were marked for possible future <br />assessment by single-cross section instream flow methodologies such as that <br />used by the Colorado Division of Wildlife. <br />All observations made during float trips were recorded on Xerox copies <br />of topographic maps (Fig. 2-6) and each trend zone was further documented <br />with color slides (Appendix C). <br />The second habitat assessment technique involved the measurement of <br />certain representative river reaches within all but one trend zone by standard <br />river-channel surveying methods. At each "habitat measurement area" five <br />channel cross-sections and their water surface elevations were surveyed. <br />. Each cross-section contained a minimum of nine segments in which substrate