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<br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br /> <br />Behavioral acclimation may also be a factor. Of the 14 Lake Powell fish that remained in the <br />study area for more than one month, we encountered twice as many cove held fish (64%) as <br />those simply released and not held for 3 days (Figure 6). The sample size was small and might <br />simply reflect normal variability, however, it appears that holding does not deter fish from <br />remaining in the general area and might encourage it. The data collected from Lake Mohave <br />were inadequate to draw any conclusions. <br /> <br />Habitat Use <br /> <br />Juvenile or subadult razorback suckers were found using the same broad, shallow, shoreline <br />habitats as adults. They were seldom found in narrow, deep, canyon habitat. While adults are <br />generally found in open areas along the shoreline (Mueller et al. 1998), juveniles are more <br />secretive, being found in the back of coves or flooded washes hidden in vegetative or rocky <br />cover. Fish were typically found within 10m of shore and depths were less than 2 m. <br /> <br />Our findings support earlier observations in rearing ponds that young suckers were nocturnal and <br />effectively concealed themselves in submergent vegetation during the daytime (Mueller and <br />Marsh 1993). These shallower habitats naturally provide warmer temperatures and more food <br />production; important factors in rapid growth. Surface water temperatures ranged 1-3 degrees C <br />higher in these backwaters than the main lake. This mimics earlier information we collected in <br />Lake Mohave (Mueller et al.1998). Body temperature data collected for 10 adults and one <br />juvenile suggests the two-year old fish normally inhabited a thermal regime equal to, or greater, <br />than the maximum temperature range used by adults (Figure 7). <br /> <br />Juveniles had a strong preference for flooded backwater complexes at Castle Creek Canyon and <br />Mike's Canyon. These two sites afforded fish the largest, shallow, flooded habitats in the San <br />Juan Arm, next to Piute Farms when lake elevations exceed 1,120 m (3,680 ft). These areas are <br />similar to areas where juvenile razorbacks have been found in the Green River at Old Charley <br />Wash (Modde 1996 and 1997). Dispersal appears to be strongly influenced by habitat/cover <br />availability. The rapid dispersal observed in riverine systems suggests that habitat conditions <br />did not attract and hold young fish. The physical changes brought about by channelization, loss <br />of backwaters and oxbows, fluctuating hydroelectric releases, and the decline of large snags and <br />other woody debris, have undoubtedly effected cover availability. <br /> <br />External Attachment Technique <br /> <br />Attachment of transmitters to the dorsal keel worked well as a short-term approach and is <br />possibly the only practical method of studying the movements of juvenile suckers. We observed <br />no initial mortality and all 55 fish left the release sites. We feel attaching transmitters to the <br />dorsal keel is less intrusive than the common dart tag which is generally inserted into the dorsal <br />musculature and is less stressful than surgery for short-term, behavioral studies. <br /> <br />15 <br />