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<br />7 <br /> <br />which the first and second backwaters encountered in each segment were sampled <br />with two seine hauls per backwater. Minimum depth of any sample could be 0.3 <br />m, and area sampled had to comprise approximately 25% of the total area of the <br />backwater. Width and length of each seine haul was recorded, though in <br />practice the width was considered constant at 4 m. Within the seine sample <br />area, maximum depth was recorded, and also the depth halfway between each <br />shoreline and the maximum depth point. Other data recorded included river <br />kilometer location, backwater type (main- or side channel), backwater length, <br />backwater temperature, main channel temperature, and maximum depth of the <br />backwater. <br /> <br />All fish collected per seine haul were examined briefly in the field to <br />identify and enumerate common, nongame fish species and release these fish. <br />All gamefish were separated and kept for length measurements, scale and <br />stomach samples. Stomachs were removed from larger fish (>25 mm) and <br />preserved in diluted 10% formalin. Smaller fish were preserved whole. The <br />remainder of the fish sampled were preserved in formalin for identification or <br />screening at the CSU Larval Fish Lab to meet needs of the standardized <br />monitoring data base. Apart from the requirements of the standardized <br />sampling design, extra seine hauls would be made in a given backwater if the <br />presence of gamefish species warranted extra effort to increase the sample <br />size of gamefish. Also, additional backwaters located from RM 140-128 were <br />sampled in a similar manner to increase the sample size of gamefish. All <br />gamefish preserved whole for stomach content analyses were measured in the lab <br />for total length. Stomach contents of all gamefish collected in seine samples <br />were analyzed in the same manner as above. <br /> <br />Job 3: Northern pike habitat utilization. <br /> <br />With the presence of radio tagged northern pike in the Yampa River, sampling <br />trips included searching for these fish via radiotracking. Using an ATS <br />receiver and 2.5 m whip antenna to monitor the various frequencies employed, a <br />given river reach would be searched throughout for signals emitted by northern <br />pike suspected of being present within the reach. Upon detection of a <br />specific signal, continued approach toward the location would be made as <br />quietly as possible to avoid disturbing the fish. Using the ATS receiver with <br />a Smith Root directional antenna tuned to the 30-32 MHz frequency range, the <br />location of the signal would be pinpointed by triangulation from shore to <br />determine the habitat type occupied by the fish. Thereafter, the fish would <br />be monitored for 15-30 min to determine its level of activity. This would be <br />classified as stationary, active within a specific habitat, or progressive <br />movement upstream or downstream. During this time, the presence and location <br />of adjacent habitat types, cover, and aquatic vegetation would be noted. In <br />some instances several pike could be monitored in the same locality. <br />Movements of these fish in relation to each other would also be recorded when <br />possible. Searches for radio tagged northern pike were conducted from <br />approximately RM 180 (Milner, Colorado) above Hayden to the confluence with <br />the Green River, and downstream to Split Mountain north of Jensen, Utah. <br />