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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 />. <br /> <br />years to meet the objective of a multi-age group adult population at the designated <br />population abundance level. <br /> <br />2) Monitoring of stocked fish should be initiated after release, and conducted at a frequency <br />adequate to determine survival, distribution, density, and causes for mortality (e.g. <br />predation, starvation). <br /> <br />3) PIT tagging prior to stocking should be conducted for all stocked Colorado pikeminnow, <br />razorback sucker and bonytail. <br /> <br />4) Production of hatchery-raised fish and stocking numbers should be revised as necessary <br />to achieve best survival and post-stocking objectives based on monitoring results. <br /> <br />5) Stocking in a given reach should be discontinued if monitoring shows significant <br />abandonment of the target reach via downstream movement. Monitoring. of this displaced <br />cohort of stocked fish should be continued to document distribution and survival. <br /> <br />6) Translocation of late juvenile! early adult Colorado pikeminnow in the size range observed <br />for Colorado pikeminnow using the Redlands passage structure should be implemented as <br />a supplementary approach to stocking in both the Gunnison and Colorado rivers to <br />facilitate colonization and augmentation of populations in river reaches above existing <br />instream barriers. <br /> <br />7) Artificial passageways should be installed at Price-Stubb and Highline diversion dams to <br />facilitate movement of wild Colorado pikeminnow upstream in the Colorado River. <br /> <br />8) The scope of propagation facilities necessary to meet the stocking needs identified in this <br />plan should be estimated as quickly as possible, and consider priorities by species and river <br />reaches, to determine if shortfalls in production capacity exist. <br /> <br />Uncertainties <br /> <br />Implementation of this plan may be affected by the following biologicaI uncertainties that <br />were identified during its preparation. These include: <br />· All aspects of the life history and habitat needs of bonytail. <br />· SurvivaI rates of stocked fish in the wild. <br />· Variability in age of maturity for femaIe fish in the wild as a function of growth. <br />· Retention of stocked Colorado pikeminnow at Age 3 + in target reaches of upstream adult <br />habitat. <br />· Acquisition of natural migratory and spawning behaviors and effective production of <br />fertilized eggs in the wild by hatchery-raised fish, especially Colorado pikeminnow. <br /> <br />17 <br />