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<br />Draft Fmal Completion Report to UDWR for Contract #93-1070. Amendment 3 <br /> <br />28 <br /> <br />The utilized complexity index was calculated as: <br /> <br />c- Perimeter <br />2x(nxArea)1/2 <br /> <br />This index is the ratio of the perimeter of the water to the circumference of a circle of the same area. The ARC/INFO <br /> <br />software was used to calculate the shoreline length of water and the area of water and submerged sand. The shoreline <br /> <br />development index was then calculated and compared to the area of available habitat for each sampling date. <br /> <br />We used these da ta to discern if: <br /> <br />1) a significant correlation between the calculated complexity indices and the area of available habitat existed, and <br /> <br />2) given a correlation, the relationship varied from year to year with changing channel morphology. <br /> <br />The 1963 data for the 1 O-km _reach within the Ouray NWR were extracted from the larger data set of Schmidt <br /> <br />(1996, unpublished manuscript), aDd the same analysis as described above was performed. The scale of the maps <br /> <br />developed from the 1963 aerial photos was proportionally adjusted. The magnitude of the adjustment was determined <br /> <br />by comparing centerline lengths for the 10-km reach from the USGS quads and the Reclamation basemap Uunbert <br /> <br />Conformal Conic projection to the digitized 1963 maps. The USGS quad and Reclamation basemaps yielded similar <br /> <br />lengths, but it was necessary to multiply the length statistics from the 1963 maps by a factor of 1.27, and the area <br /> <br />statistics by 1.62, to maintain proper proportionality. <br /> <br />UDWR Nursery Habitat Surveys <br /> <br />UDWR conducted nursery habitat sampling three times each year. In the spring, prior to flooding, the <br /> <br />sampling assessed the location. condition and populations of fish after winter low flows. Typically, discharge at that <br /> <br />time was somewhat higher than during summer base flows. Sampling in late July and early August occurred after larval <br /> <br />fish had been transported into the study reach. The discharge during sampling was near base flow (50 m3fs). The fall <br /> <br />sampling assessed growth of the juvenile fish during the summer. <br /> <br />UDWR field crews seined fish and measured physical parameters at each sampled habitat. Physical <br /> <br />measurements included temperature, length. and width at the mouth, middle, and upper part of each backwater, The <br /> <br />depth of the water and depth to firm substrate was measured at three evenly spaced points on each width transect AU <br />