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located in Etter's Pond near Palisade, Colorado, was determined to be dominated by potential siblings from a very small number of parents, and potentially hybridized with flannelmouth sucker (Genetics Panel, Colorado River Recovery Program, 1994). Therefore, mating crosses between two individual fish from Etter's Pond was determined to be genetically unacceptable due to inbreeding risks. The Recovery Program approved development of a "blended stock" of razorback to serve as the broodstock for the Colorado and Gunnison rivers. This . stock was fonned using razorback sucker from the Colorado River ann of Lake Powell (4 fish), the San Juan arm of Lake Powell (4 fish), riverine fish from the upper Colorado River (4 fish), and Etter Pond (3 fish). A captive spawning strategy for these fish is described in Burdick et al. (1995) following the Recovery Program's Genetics Management Guidelines (Williamson and Wydoski 1994). Bonytail are represented by only one captive broodstock that is currently kept at Dexter National Fish Hatchery in New Mexico. Some of these fish are also being held at Wahweap State Fish Hatchery in Utah for reintroduction and broodstock development purposes. Since these fish are the descendants from limited numbers of wild fish taken from Lake Mohave, and no more viable adult bonytail are currently available from the wild stock remaining in Lake Mohave, these fish represent the only genetic material left from which to base a propagation and reintroduction program. For Colorado pikeminnow, broodstock development was initiated in 1991, and 17 family lots currently exist from that effort. Due to the relatively "stable" status of Colorado pikeminnow populations in Upper Basin rivers (Czapla 1997, McAda et al. 1994, McAda et al. 1996), and the limitations of hatchery and rearing facilities within the Program over the past 6 years (Wydoski 1994, Czapla 1991), no further broodstock development has occurred within the 5 x 5 breeding matrix, nor have any stocking plans been developed to use progeny from the existing brood stock held at Horsethief State Wildlife Area near Grand Junction, Colorado. Sixteen humpback chub were collected in September 1995 at Black Rocks from the Colorado River in Colorado near the state line. The pUlpOse of this collection was to create a refugia population to safeguard genetic material in the event of a catastrophic loss in the Black Rocks population. No broodstock development or reintroduction objectives have been identified for humpback chub in the Upper Basin due to the relative stability of five existing populations in the Yampa, Desolation-Gray, Black Rocks, Westwater and Cataract Canyon sites. To date, stocking and propagation planning within the Recovery Program has proceeded on a reach by reach basis for select species. One of the recurring problems for guidance and planning within the Recovery Program has been the identification of "long- term" fish needs for propagation (beyond the upcoming year), and identification of facility requirements to meet propagation needs for anticipated restoration stocking plans. This plan is intended to describe restoration stocking needs anticipated for the listed fish species for all candidate rivers or river reaches within the Upper Basin in the state of Colorado. Stock 2