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<br />a potential exists to effect density-dependant dynamics in the wild population. It is <br />recommended that if this action is performed, and is to succeed, a naturalistic rearing <br />facility and methodologies are used. Although the action, if properly performed, <br />appears to pose no serious biological risks to the wild population, the action would not <br />promote a self sustaining population, a feature required in the recovery criteria for the <br />species. In addition, this management action would likely require significant long term <br />effort and funding (years to decades) to achieve a sustained positive population <br />response. <br /> <br />Third, we address the feasibility of augmenting the Grand Canyon population of <br />humpback chub via translocation. Considered are 1) translocation of fish within the <br />LCR, and 2) translocation of fish into other tributaries (Bright Angel, Shinumo, and <br />Havasu creeks) in Grand Canyon. <br /> <br />Translocation of humpback chub within the LCR appears to offer potential for minor gain <br />in the wild census population, and may significantly expand the current spawning range <br />of the species, but may pose some potential for genetic risk to the main population in <br />Grand Canyon. These risks are related to inbreeding and depression of genetic <br />effective population size. Corrective measures to avoid these problems (should they <br />occur) appear to be available, provided monitoring and funding is emplaced to detect <br />them. <br /> <br />Translocation of humpback chub to other tributaries in Grand Canyon may offer <br />potential for augmenting mainstem aggregations, and some potential exists for creation <br />or significantexpansion of downstream aggregations. Translocation efforts to these <br />tributaries may need to be accompanied by sizeable predator removal efforts to effect a <br />change. Genetic risks to the main population of humpback chub in Grand Canyon <br />appear to be minor. <br /> <br />It is recommended that if any of these actions are pursued, they be carried out with the <br />priorities in mind of: 1) posing least potential for genetic harm to the wild population, and <br />2) having the best potential for promoting a self-sustaining wild population. This <br />suggests that translocations might be a first priority, followed by supplemental stocking <br />of wild caught age-O fish, and as a last resort the release of captive propagated fish. <br />Maintaining fish in captivity for refugium purposes poses no genetic risks to the wild <br />population, however, the release into the wild of captive reared individuals does pose <br />numerous genetic risks that need to be seriously evaluated. <br /> <br />6 <br />