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<br />Draft Final Completion Report to UDWR for Contract #93-1070. Amendment 3 <br /> <br />27 <br /> <br />Enumeration of Bars <br /> <br /> <br />The long-term behavior of the channel and bars were noted from the GIS maps. For summarizing the overall <br /> <br />behavior of bars, each bar was classified as a mid-channel bar. or as a point or bank-attached compound bar. While <br /> <br /> <br />some discharges may dissect bank-attached compound bars, only a small portion of the flow was carried by chute <br /> <br /> <br />channels at discharges that do not overtop the bars. <br /> <br />GIS Statistics <br />Statistics were generated from each GIS coverage in order to determine total area of each classified polygon <br />and the total length of perimeter enclosing each polygon classification for each sampling date. As shown below, the <br />contacts between geomorphic units were surrogates for topographic elevation contours. The different pseudo- <br />topographic geomorphic units are used to simulate the river condition for those discharges greater than the one flow that <br />occurred at the particular time of each photo. Areas and perimeters were calculated for each pseudo-topographic <br />elevation by melding all lower "elevation" polygons into a singie polygon. then calculating the resulting polygon's area <br />and perimeter. ihe latter calculation indicates how the topographic complexity of each bar, indicated by the area and <br />shoreline of each pseudo-topographic elevation. changed during summer low flow and from year-to-year. <br />It was possible to examine the following questions from the GIS statistics: (1) Was a greater portion of the <br />channel occupied by an equivalent discharge in 1992 than 19931; and (2) Did the area of high elevation white sand <br />increase with the passage of the 1993 flood? We also assessed the possibility of using a remotely sensed metric to <br />predict the area of available habitat. The "shoreline development" index of Wetzel (1983) was employed as a <br />complexity index. This index was used to compare the length of the shoreline to the area of water and indicate the <br />degree of convolutedness of the shoreline edge (Fig. 13). While developed for lake and reservoir systems, this type of <br />index was appropriate for discerning shoreline convolutedness for this alluvial system. Rivers are linear systems, so the <br />length of the reach greatly influences this calculated complexity index. If reaches of river of different lengths are <br />compared, normalization must be applied to this non-dimensional complexity index. Comparison of indices for reaches <br />of the same length of similar width or comparison of changes to a single reach. such as the 10-km study reach. over time <br />required no normalization. <br /> <br />~ <br />