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CONCLUSIONS <br />• Estimated larval razorback sucker survival in the experimental enclosures ranged <br />from 0 - 58% and growth rates averaged 0.6 mm/day in 2003 and 0.6 mm/day in <br />2004 in the presence of nonnative predators. <br />• Larval razorback sucker survival was detected 88 days following introduction at a <br />density as low as 4001arvae/acre. <br />• Bonytail larvae introduced sympatric with razorback sucker larvae at a density of <br />8,000 larvae/acre had an estimated survival of 16 - 17% in 2004 and a growth rate <br />of 0.6 mm/day in 2003 and 0.4 mm/day in 2004. <br />• Larval Bonytail survival was detected 106 days following introduction in 2003. <br />• Larval Bonytail survival was detected 66 days following introduction <br />sympatrically with razorback sucker larvae in 2004 at a density of 8,000 <br />larvae/acre. <br />RECOMMENDATIONS <br />• Actions to identify monitor and manage variables and conditions necessary to <br />achieve entrainment of at least 4001arvae/acre should be implemented. <br />• Continue to manage floodplains based on the reset theory. Even with abundant <br />nonnative fish predators, these habitats are important to endangered fish and <br />should be used for recovery. <br />• During an average to high flow year, introduce larval razorback suckers into <br />floodplain sites that have reset to test this theory under more natural conditions. <br />This should include introducing larval razorback sucker at a density of at least <br />4001arvae/acre. <br />22 <br />