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<br />NAU Sand Bar Studies <br /> <br />Final Report <br /> <br />MANAGEMENT IMPLICATIONS <br /> <br />, <br />~ <br /> <br />As controlled flooding becomes a tool for regulated river resource management, predicting the <br /> <br /> <br />outcome of floods under a range of antecedent conditions is important. Greater understanding is <br /> <br /> <br />needed of the basic physical processes that control sediment transport following tributary sand inputs <br /> <br /> <br />because limitations in sediment supply during flooding control main-channel concentrations (Rubin et <br /> <br /> <br />al" 1998; Topping et al" 1999) and eddy bar deposition rates (Wiele et al" 1999), In addition to <br /> <br /> <br />sediment availability and discharge, the volume of sand occupying the depositional site prior to <br /> <br /> <br />flooding (antecedent storage) is an important factor in determining the magnitude and persistence of <br /> <br /> <br />flood-related deposition (Hazel et al., 1999; Wiele et al" 1999), Prediction of change is further <br /> <br /> <br />complicated by variability in channel and debris fan geometry (Webb et al" 1989; Schmidt and Graf, <br /> <br /> <br />1990; Melis, 1997), the cumulative downstream nature of the limited sand supply (Topping et ai" <br /> <br /> <br />2000a, 2000b), and in the spatial and temporal variability of study sites utilized for monitoring <br /> <br />(Schmidt et al" 1999b; Grams and Schmidt, 1999), <br /> <br /> <br />The 1997 Test Flow was the first attempt by the Glen Canyon Dam adaptive management group to <br /> <br />implement a release closely timed with tributary floods on the Paria River. The potential benefit of <br /> <br /> <br />floods timed closely with tributary inputs is that in the presence of finer sediment, sand concentrations <br /> <br /> <br />will be higher resulting in higher rates of deposition in eddies (Topping et al" 1999), As a result, <br /> <br /> <br />planned floods can be shorter in duration and lessen the economic cost associated with loss of <br /> <br /> <br />hydropower generation and altered water-release patterns (Harpman, 1999), Because of these <br /> <br /> <br />associated costs it was important for ri ver managers to know if a peak power plant discharge, the 1997 <br /> <br /> <br />Test Flow, could prolong the residence time of sediment supplied by the Paria River, Our data <br /> <br /> <br />suggests that this management goal was not achieved, and we conclude that the discharge of future <br /> <br /> <br />planned floods designed to redistribute sediment to high elevation will need to be at least similar to the <br /> <br /> <br />magnitude of the 1996 Controlled Flood, if not greater. Controlled floods designed to prolong the <br /> <br /> <br />residence time of newly input sand in Marble Canyon need to take into account where storage <br /> <br /> <br />environments are available, especially at higher elevations, as well as the antecedent conditions of sand <br /> <br /> <br />storage on the bed with respect to volume, grain size, and spatial distribution, <br /> <br /> <br />Timing future floods to coincide with years or months of above average sediment delivery by the <br /> <br /> <br />Paria River is a critical resource issue (Schmidt, 1999). Large floods on the Paria River typically occur <br /> <br /> <br />during the late summer or early fall (Topping, 1997). Coordination of high releases at this time of year <br /> <br /> <br />is difficult because flows in excess of power plant capacity can only be released to avert hydrologic <br /> <br /> <br />emergencies, a situation that is most likely to occur in late spring or early summer when inflow to Lake <br /> <br />C' <br /> <br />..~ <br />:..,. <br />,;t <br />K <br />t. <br /> <br />;-, <br /> <br />" <br />". <br />, <br /> <br />r: <br /> <br />" <br /> <br />.'?:; <br /> <br />,.:, <br /> <br />-, <br /> <br />;:. <br />~L <br /> <br />:.",. <br />':. <br />~~ <br />~;~ <br /> <br />:.:... <br />f <br /> <br />32 <br />