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<br />3 <br /> <br />Results and Discussion <br /> <br />Final map plots and acreage tabulations were hand delivered to Mr. Bob <br />Williams. GenerallYt the number and total acreage of backwaters are maxi- <br />mized at lower flows (see Appendix A and B). Howevert because only three <br />flows were studied, it is not certain what flow will produce the optimum <br />number of backwaters. This number may occur at a higher or lower flow than <br />the 1,889 ft3/s reported in this study. Additionally, the highest flow <br />studied (4,359 ft3/s) maintained larger backwaters than the lowest <br />(1,889 ft3/s) and middle (3,119 ft3/s) flows; therefore, it is possible <br />that a different high flow scenario may maximize backwaters. More flows <br />need to be studied to determine the optimum strategy. Furthermoret a <br />greater number of study sites encompassing larger river reaches should be <br />examined to reduce the variability in the data. <br /> <br />The Ouray study site maintained the greatest number and acreages of back- <br />waters at the highest flow. This may have occurred because the sandbars <br />in this study s'ite are higher in elevation, steeper, and more permanent <br />(vegetated) than the sandbars in the other areas. Thus, backwaters on <br />higher sandbars only occur at higher flows. <br /> <br />Comparing 1:4,000 and 1:2,000 scale photography indicates the former is <br />adequate for mapping backwaters. Cost savings dictate the use of 1:4,000 <br />scale photography. Color infrared photography appears superior to color <br />photography since color infrared increases the contrast between water, <br />sand, and sediment laden water. Moreover, backwater delineation is <br />simpler and more accurate using color infrared photography. <br /> <br />In our efforts to obtain a fourth set of photography, an interesting <br />observation occurred. We requested flows of 1,500 ft3/s in order to help <br />define the lower end of the graphs. More specifically we felt that with a <br />1500 cfs data set it would be possible to focus in on the range of flows <br />needed to maximize backwater habitat. A fourth set of aerial photography <br />was acquired on December 4, 1986, almost 3 months after the first low <br />flow. The Jensen Gage reading was nearly identical to the September 12, <br />1,986, It889 ft3/s flow record. It was then determined that it would be <br />unneccessary to interpret this data as results would probably be iden- <br />tical to the September 12, 1986 data set. After a brief examination of the <br />photographs, it was noted that sandbar configuration and backwaters were <br />drastically changed. Moreover, there was an average of approximately <br />30 percent loss in the area of sandbars calculated at the same flows in <br />the same study sitest 3 months apart. (see map plots and Appendix A for <br />acreage tabulation and a visual account of cover type changes). On the <br />Ouray site, an important backwater near mile 135.2 was reduced to a <br />