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<br />2.0 Planning And Development <br /> <br />2-3 <br /> <br />April 2004 <br /> <br />to enhance survival and recruitment. Monitoring drift and habitat use by larval razorback sucker <br />will provide a better understanding of the role of floodplain habitat in the life cycle of the <br />species, as well as differences between floodplain sites with respect to entrainment of larvae and <br />growth and survival. Initial management of selected Recovety Program sites will include <br />stocking and evaluation of hatchery fish (excess to meeting the State stocking plans) to guide <br />research and to supplement population augmentation efforts. Hatchery bonytail will also be <br />released in and near floodplains to describe habitat use and assess their growth and survival. <br /> <br />Hatchery culture and holding facilities for razorback sucker have been established at the <br />Ouray National Fish Hatchery, Ouray, Utah; and at the Service's Grand Junction Endangered <br />Fish Facility, Grand Junction, Colorado. Hatchery bonytail are available from Dexter National <br />Fish Hatchery, Roswell, New Mexico; Wahweap State Fish Hatchery, Big Water, Utah; and <br />Mumma Native Aquatic Species Restoration Facility, Alamosa, Colorado. <br /> <br />2.4 Role Of Floodplain Model <br /> <br />A Floodplain Model (Valdez 2004) was developed for the Recovety Program to estimate <br />the amount of floodplain habitat necessary to recover the razorback sucker and to support <br />recovered self-sustaining populations. This mathematical model is user interactive and consists <br />of 31 numbered steps, including 11 user-specified input variables (Box 2) and 20 automated <br />output variables (Box 3). Output variables include computations of total acres and hectares of <br />floodplains necessary to support specified densities of fish, number offish recruiting to maturity <br />at 400 mm TL, and recruitment rate as a percentage of the initial adult population. <br /> <br />The Floodplain Model is used in this management plan to help assess the importance of <br />river reaches and their potential for species conservation. The model considers the relationships <br />among the location of known and possible spawning sites and available floodplain habitats, both <br />managed and un-managed. The model is also used to assess the importance and role of specific <br />floodplain sites, the estimated contribution of <br />each site to recovery, identification of critical <br />and limiting factors, and identification of <br />management elements necessaty for gaining <br />full benefits of given sites. The Floodplain <br />Model estimates that 2,032 acres (823 ha) of <br />floodplain depressions that hold fish for 24 <br />months are needed to support a self- <br />sustaining population of 5,800 adult <br />razorback sucker with an average annual <br />recruitment of 30%, at average fish growth <br />and density. <br /> <br />Floodplain Model Input Variables <br /> <br />. <br /> <br />Initial population size, <br />Sex ratio, <br />Average total length (TL) of females, <br />Percent hatching success, <br />Percent larval emergence, <br />Survival rate of larvae per mile <br />Time in floodplains, <br />Survival in floodplains, <br />Fish growth rate, <br />Fish density, and <br />Annual survival in mainstem. <br /> <br />. <br /> <br />. <br /> <br />. <br /> <br />. <br /> <br />. <br /> <br />. <br /> <br />. <br /> <br />. <br /> <br />. <br /> <br />. <br />