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construction in the upper basin increased dramatically in the 1950's and 1960's <br />with the Colorado River Storage Project (CRSP). Regulated flows from high dams <br />t and diversion structures upstream of historic bottomland areas remove water from <br />the river for municipal, industrial, and agricultural uses. These activities <br />have affected the main channel and, in some instances, eliminated off-channel <br />habitats such as backwaters, embayments, and bottomlands as nursery areas for <br />some of the endangered fishes. The most noticeable change has been the reduction <br />in historic peak flows. <br />The Gunnison River is influenced greatly by upstream water diversions, <br />operations of the Aspinall Unit, and other projects that were constructed at <br />about the same time as the Aspinall Unit. The greatest change caused by the <br />' Aspinall Unit is the reduction of spring runoff. Peak discharge has steadily <br />declined since continuous flow records began in the early 1900's. McAda and <br />Kaeding (1991) analyzed and compared stream flow data on the Gunnison River for <br />' three water development periods: pre-development (1914-1938), middle development <br />(1939-1965), and post-Aspinall development (1966-1988), and identified several <br />changes in magnitude, timing, and duration of streamflow. Mean maximum annual <br />discharge (average of the mean-daily flow for the highest day of the year) for <br />' the Gunnison River declined about 47% between the early development and post- <br />Aspinall periods. Mean monthly flows have also changed over the three <br />development periods. In general, spring and early summer flows have declined, <br />and fall and winter flows have increased (Figure 2). Mean-monthly flows in May <br />and June, the peak months of runoff, have declined 43 and 47%, respectively, in <br />the Gunnison River. <br />' The mean total annual flow for the pre-Aspinall water development period <br />(prior to 1965) and the post-Aspinall water development are very similar (1.8 <br />million acre feet). However, the hydrograph has dramatically changed. McAda and <br />t Kaeding (1991) estimated the effect of the Aspinall Unit on runoff by comparing <br />the change in streamflow from the middle-development period to the post-Aspinall <br />period. Mean-monthly streamflow declined about 1.4% in April, 25.1% in May, and <br />' 32.2% in June. Streamflow during the remainder of the year increased, <br />particularly during the winter when average flows were more than 100% greater <br />than the pre-Aspinall flows. Gunnison River mean-monthly flows have declined an <br />average of 1,864 cfs in May and 2,346 cfs in June. Therefore, the loss of peak <br />flows during runoff (Figure 3) has reduced the area and frequency of flooding in <br />lowland areas (Appendix 1: Photos 4 and 5). <br />Cooper and Severn (1994c) compared the mean number of days that flows <br />exceeded 10,000, 15,000, and 20,000 cfs for two periods of water development <br />(1897-1965: pre-Aspinall and 1966-1993: post-Aspinall). They estimated flows <br />' during post-Aspinall development exceeded 10,000 cfs on the average of only 6 <br />days annually as compared to 22 days for the pre-Aspinall development period. <br />The pre-Aspinall period also had, on average, a period of approximately 7 days <br />with flows greater than 15,000 cfs, while the post-Aspinall period had only one <br />' day per year with these flows. The frequency of days with flows greater than <br />20,000 cfs is about 10 times greater (2 days vs. 0.2 days) in the pre- vs. post- <br />Aspinall period of record. <br /> <br /> <br />6 <br />