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<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 />I <br /> <br />geomorphologic response of the bottomland to a flow-through condition is uncertain. <br />Runoff of 2003 presented the first significant flow-through connection for these <br />bottom lands since the reconfiguration. Hydrographic survey crews from Tetra Tech <br />performed monitoring surveys in July of2003. Analyses of the data showed that the <br />bottomlands experienced localized scour and deposition without indications of <br />aggradation or degradation trends. These findings suggest that the flow-through <br />condition may help to maintain the bottomlands and refresh the bed of the bottomland <br />without negatively impacting the long-term function of the bottomlands. However, data <br />is limited and monitoring is expected to continue with future connectivity to better <br />understand the geomorphic response of these habitats. <br /> <br />A Generalized Interactive Model To Predict Floodplain Habitat Area Needed To <br />Recover The Endangered Razorback Sucker In The Upper Colorado River Basin <br /> <br />Valdez, Richard A.I and Pat Nelson2 <br /> <br />I R.A. Valdez & Associates. Inc... 1 USFWS. Upper Colorado River Endangered Fish <br />Recovery Program <br /> <br />Floodplain Model was developed for the Recovery Program to estimate the amount of <br />floodplain habitat necessary to recover the razorback sucker (Xyrauchen texanus) and to <br />support recovered self-sustaining populations. This mathematical model was developed <br />on an Excel platform and is user interactive. It consists of 31 numbered steps, including <br />17 user-specified input variables and 48 automated output variables. Input variables <br />include initial population size, sex ratio, average total length (TL) of females, percent <br />hatching success, percent larval emergence, survival of larvae during drift, entrainment <br />rate oflarvae in floodplains at various river miles, time spent in floodplains, monthly <br />survival in floodplains, annual survival in the mainstem, and fish density. Automated <br />output variables include number of females based on initial number of adults and sex <br />ratio, average female fish weight, number of eggs produced, number oflarvae emerging, <br />number of larvae entrained, and number of fish surviving in floodplains. Output <br />variables also include computations of total acres and hectares of floodplains necessary to <br />support specified densities of fish, number of fish recruiting to maturity at 400 mm TL, <br />and recruitment rate as a percentage of the initial adult population. The model estimates <br />that 2,032 acres of floodplain depressions are necessary as nursery and rearing habitat to <br />support a self-sustaining population of 5,800 adult razorback sucker with average annual <br />recruitment of 30% (i.e., 1,740 adults; Recovery Goals target). <br /> <br />21 <br />