Laserfiche WebLink
<br />1 <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 />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 bony tail. <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 HighIine 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 biological uncertainties that <br />were identified during its preparation. These include: <br />. All aspects of the life history and habitat needs of bonytall. <br />. Survival rates of stocked fish in the wild. <br />. Variability in age of maturity for female 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 />