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r <br />23 <br /> when it was most prevalent in the river, squawfish actually appeared to be <br /> attracted to it. Habitats free of frazil were nearby but refuge was not sought <br /> there. Frazil ice did not occur in backwaters, embayments and eddys. It is <br /> possible that the food items contained in the frazil were used directly by the <br /> squawfish and/or possibly squawfish were attracted to other smaller fish which <br /> were feeding on aquatic insects suspended in the frazil. <br /> Eddy habitat was utilized by radiotagged squawfish 8.7% of total <br /> observation hours (Table 5). Fish B7 and B10 used eddys extensively throughout <br /> the winter. The typical appearance of eddy habitat at ice-over is portrayed <br /> along the right side of Figure 7. This area at RMI 76.2 was used by B7. Eddy <br /> habitat provided the greatest depth observations (8.8 feet) during the study. <br /> The velocity range was quite narrow between -0.2 to 0.3 feet/second. Silt was <br /> the predominant substrate type. Reverse or revolving water currents typified <br /> eddy habitats. These currents are usually caused by projections of rocks <br /> jutting out from the shoreline. <br /> Other habitats used by radiotagged squawfish throughout the winter <br /> included shoreline (2.7%) and side channel (1.2%). <br />10 Survey potential <br />Because of their easily identifiable nature at initial ice formation, <br />major habitats used by squawfish during the winter could be effectively <br />surveyed. Areas similar in appearance to those presented in Figures 4-7 could <br />be identified from aircraft or boat at initial ice formation. Later, these <br />areas could be further examined for the appropriate range of depth, velocity, <br />and substrate parameters determined during winter radiotelemetry studies. A <br />method is needed to determine percent habitat change--as a result of changes <br />discharge. To do cura a method of relating water surface elevation <br />of discharge must be established during the winter months. <br />Diel comparisons <br />The 24 hour data set was used for comparing habitat measurements between <br />different daily time periods since the data within it was evenly distributed <br />through the four time periods. The time periods analyzed where; morning <br />(0600-1200 hrs), afternoon (1200-1800 hrs), evening (1800-2400 hrs), and night <br />(2400-0600 hrs). <br />Depth, velocity, substrate, and habit=t paramatPrc appeared aimiLar <br />between all four time periods. Mean water depths ranged from 2.25 to 2.68 <br />feet (Table 9 and Figures 8-11). Velocity at 0.6 depth was just under 0.2 <br />feet/second for each of the periods (Table 10 and Figures 12-15). Gravel- <br />gravel was the predominant substrate in each period, however less frequently <br />used substrate types differed in each time period (Figures 16-19). Backwater <br />was the predominantly used habitat type followed by run in all periods <br />(Figures 20-23). <br />Depth <br />There was ice cover over all measured depths during all trips except the <br />last (March 16 - 21), when the river was ice free. All depths reported are <br />the amount of ice-free water under the ice (Figures 2a and 2b). Mean water <br />depth in the main hole was 2.4 feet with a range between 0.5 and 8.8 feet <br />0