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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 />have much lower densities of nonnative fish for the first year. The fish populations in <br />these depressions are reset to zero during these dry cycles. This study was designed to <br />evaluate if large numbers of razorback sucker larvae that entered a "reset" tloodplain <br />depression could overwhelm nonnative fish predation, survive, grow and reenter the river <br />during future spring floods. This situation was experimentally created by pumping water <br />from the river into a dry floodplain and introducing larval razorback suckers and <br />nonnative fish into partitioned portions of the floodplain depression. Survival of many <br />razorback sucker larvae was detected, reaching lengths of up to 115mm by mid-summer. <br />Continued monitoring of this floodplain during future spring floods will determine when <br />these razorback suckers enter the river. To continue building on the successes of these <br />studies, we evaluated survival at lower stocking densities to identify the lower stocking <br />threshold needed to enable detection of surviving larvae. This evaluation took place in a <br />"reset" floodplain that connected with the river during spring high flows and was re- <br />invaded by nonnative fishes. Twelve lI8-acre experimental enclosures were constructed <br />at the Baeser floodplain site. Larval razorback sucker were stocked into the enclosures at <br />six densities ranging from 36,000 to 800 larvae/acre. Survival of razorback sucker was <br />detected in the lowest and the highest density enclosures. However, survival among all <br />enclosures was quite variable. The highest survival (11 %) was observed in the highest <br />density (36,000 larvae/acre) enclosure. On average, the four enclosures with the lowest <br />density of stocked razorback sucker had the lowest estimated survival rate, indicating that <br />survival of larval razorback sucker in the presence of nonnative predators is density <br />dependent. <br /> <br />Field application of the 'floodplain reset' approach to enhance survival of bony tail <br />and razorback sucker in the middle Green River, Utah. <br /> <br />Modde, Tim <br /> <br />u.s. Fish and Wildlife Service, Vernal, UT <br /> <br />Floodplains provide nursery habitat for endangered fishes but also support residual <br />nonnatives that prevent survival of native fishes. In an effort to reduce predator pressure, <br />the use of resetting, or draining floodplains, prior to stocking was evaluated as a method <br />of enhancing larval bonytail and razorback sucker survival. <br /> <br />Bonytail and razorback sucker were stocked into Green River floodplains in June 2003. <br />Bonytaillarvae were stocked at a rate of 1,430 larvaelha into the three largest floodplains <br />and adult bonytail were stocked all five floodplains. Razorback sucker were stocked in <br />all five floodplains between 4 and 16 June at a rate of 1,945 tish/ha. All floodplains were <br />connected to the Green River by high flows between 21 May and 5 June 2003. <br />Nonnative tish accessed all study floodplains and reproduced. At the conclusion of the <br />study, nonnative fishes dominated fish numbers and biomass. However, the minimum <br />number ofbonytail estimated in floodplains during July ranged between 0 and 112/ha. <br />Bonytail reproduction was observed in three of the tive floodplains. Razorback sucker <br />surviving through the end of July was much lower, ranging between 1.3 and 5,6 tishiha. <br /> <br />~3 <br />