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<br />5 <br /> <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 />;1 <br />I <br />I <br />I <br />I <br />I <br />I <br /> <br />Bestgen et al. (1998) and Schmidt (1996) for drifting larvae Colorado pikeminnow into main <br />channel backwaters. The result of this sub-model provides an estimate of the proportion of <br />larvae produced at a spawning site that drift downstream and become entrained in floodplain <br />habitats at varying distances downstream from the spawning site. <br />Objective 3: Estimate growth and survival of larval and young razorback sucker <br />in floodplain habitats. <br />Growth and survival oflarvae, age-D, age-I, and age-2 razorback sucker is estimated in <br />floodplains inundated by high river flows in spring. This aspect of the model uses the output of <br />Objective 2 (i.e., number oflarvae entrained in floodplains) and computes numbers and sizes of <br />fish in the floodplain with user-specified input of number of months in the floodplain and annual , <br />survival rate. The numbers of fish surviving in the floodplain is computed for low, moderate, <br />and high fish growth rates, in all possible combinations with low, moderate, and high fish <br />densities. Survival and growth rates of young razorback sucker were taken from various studies <br />(Modde 1996, 1997; Muth and Wick 1997; Muth et al. 1998). Additional information on <br />survival and growth of young razorback sucker is available from lower basin studies (Minckley <br />et al. 1991). Estimates of food availability were taken from various trophic energetic studies in <br />flooded bottomlands and main channel backwaters (Grabowski and Hiebert 1989; Mabey and <br />Shiozawa.1993). Using the combination oflow, moderate, and high growth rates and low, <br />moderate, and high fish densities, total area of floodplains is computed as acres and hectares. <br />Objective 4: Estimate recruitment to adults of naturally-produced razorback <br />sucker necessary to achieve and sustain recovery criteria. <br />The numbers of razorback sucker escaping from the floodplain into the mainstem at low, <br />moderate, and high growth rates are provided by Objective 3. The model provides total lengths <br />for each growth rate and computes the number of months required for the fish to reach size of <br />recruitment at 400 rom total length (TL). Fish may reach recruitment size in the floodplain, <br />depending on the number of months specified by the user. An annual mainstem survival rate is a <br />user-specified input variable and the numbers of razorback sucker that recruit is computed, along <br />with the recruitment rate. Sustainable recruitment rate is estimated at 0.30, which is equal to the <br />average annual mortality rate of adult razorback sucker. <br />