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<br />numbers needed over the next five years were estimated according to biologically-based <br />population objectives, and thereby permit the estimation of propagation facilities required to <br />meet these stocking objectives. The plan will present required objectives, justification and <br />risk assessment for each species' proposed stocking scenario. <br /> <br />Stocking Objectives and Relation to Recovery Objectives <br /> <br />1) To restore populations of razorback sucker, bonytail, and Colorado pikeminnow to <br />unoccupied river reaches within Colorado, <br />2) To augment very small populations of razorback sucker and Colorado pikeminnow in <br />occupied river reaches in Colorado, <br />3) To establish populations of these three fish species comprised of at least three age <br />groups at a desired population abundance level (fish/mile). <br /> <br />Recovery of these fish species is described as a number of self-sustaining populations within <br />species' recovery plans. Specific quantification of recovery criteria for downlisting and <br />delisting each species remains an incomplete task. The Recovery Program's Genetics <br />Management Plan (Wydoski 1995) and Interim Management Objectives (Lentsch et al. 1998) <br />provide preliminary direction for species and reach priorities and abundance targets for each <br />population. This plan further specifies target objectives for distribution, abundance, and <br />composition of stocked populations of three of the four federally-listed Colorado River fiSh <br />species for river reaches within Colorado. With achievement of the three objectives above, <br />the fundamental building block for naturally-functioning and self-sustaining populations will <br />have been established. This will contribute to recovery via expanded distribution and greater <br />abundance of these species in presently unoccupied or isolated habitats and further reduction <br />of extinction probability. Presence of these stocked populations will contribute to recovery <br />by making it possible to identify limiting factors pertaining to spawning, reproduction, <br />sUlVival, and recruitment that cannot be assessed under the present circumstances of low to <br />non-existent population numbers. Attempted spawning and the production of viable eggs and <br />larvae by these stocked populations will constitute the frrst step in conversion to desired <br />natural function and self-sustaining status for these stocked populations. <br /> <br />For razorback sucker and bonytail, no other recovery action provides an effective and <br />timely means of restoring wild populations in those river reaches designated within the <br />Genetics Management Plan. Success in achieving these stocking objectives could result in <br />the establishment of 1-2 bonytail populations where there are presently none; and 1-3 <br />razorback sucker populations in the Colorado River to complement the existing two in the <br />middle and lower reaches of the Green River. For Colorado pikeminnow, success would <br />result in an expanded Colorado River population with potentially new distinct spawning <br />aggregations in Debeque Canyon of the Colorado River; Dominguez Canyon in the Gunnison <br />River, and Dolores Canyon in the Dolores River. Constnlction of fish passage stnlctures. on <br />the Colorado River to achieve connection and dispersal similar to that obselVed at Redlands <br />on the Gunnison River remains a critical component of recovery actions necessary to <br />complement restoration stocking. <br /> <br />3 <br />