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<br />Cameo call was on and Ute Water was full reliant u on re lacement reservoir and Je Creek <br />Y P P n'Y <br />~ releases for its supplies (see Attachment D -1977 and other years). <br />"" Attached are a series of graphs which depict the projected flow reductions at the top of the 15-mile <br />reach due to the District's operations in differing but meaningful ways. Figure 3.7 shows the <br />monthly reductions which would have occurred during the minimum runoff year on the Colorado <br />River during the study period (1977) and the maximum runoff year (1984). In 1977, reductions are <br />near average until the onset of the runoff season in April, when reductions dramatically drop off to <br />about zero by the last 4 months of the year. During this year, availability of the District's direct <br />diversion rights would have been limited, necessitating the release of water from the Jerry Creek <br />Reservoirs. Additionally, when water would have been available from the District's appropriations, <br />the Cameo call would have been on, resulting in replacement reservoir releases. These two factors <br />result in near-zero flow reductions in the Colorado River when compared to historical flows. In the <br />maximum runoff year (1984), water was in great supply and no replacement reservoir water was <br />required, resulting in larger overall flow reductions by the District. Thus, hydrologic effects. are <br />expected to be minor during drought conditions when flows are most critical to endangered fish. <br />Larger flow reductions, which may occur during wet years, should not represent as significant an <br />effect to endangered fish since river flows during such periods are generally plentiful. <br />Figure 3.8 shows what the annual variation would have been in flow reductions over the 19-year <br />simulation period. Reductions average about 26 cfs on an annual basis, but range from 13 cfs in <br />1977 to 30 cfs in 1975. <br />Figure 3.9 shows what flow reductions would have been over a representative low flow /high flow <br />cycle which occurred from 1976-1980. The bars represent the actual flow reductions simulated and <br />the line shows the average monthly reductions over the fu1119-year period. The graph demonstrates <br />that flow reductions will be significantly below average during drought periods when reliance on the <br />Jerry Creek Reservoirs and replacement reservoir releases is high, followed by higher than average <br />reductions when flows on the river recover, the Jerry Creek Reservoirs can be refilled, and no <br />_ replacement water is needed. <br />~' Figure 3.10 is a frequency distribution of the flow reductions that would have been caused by the <br />District's future operations. The graph shows the percent of time that flow reductions are above or <br />below the rates on the horizontal axis. The 50 percent frequency rate is 25.7 cfs; i.e., half the <br />reductions. are above 25.7 cfs and half are below. The relative steepness of the curve near the center <br />of the graph indicates that flow reductions tend to occur more often in the steep portion of the graph <br />(22-39 cfs) with relatively few occurrences outside of this range. <br />Figure 3.11 compares the average monthly adjusted historic flows to what the reduced flows on the <br />Colorado River at the top of the 15-mile reach would have been following District diversions. <br />Similarly, Figures 3.12 and 3.13 compare monthly historic and future flows for the low runoff (1977) <br />and high runoff (1984) years. The charts emphasizes that while flow reductions do occur, the effects <br />on the Colorado River are very small due to the large flows in the river. <br /> <br />CDM Camp Dresser & McKee <br />o:~aoa~-~-o~ooc~ner~vn-s.ooc B-15 <br />