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cc <br />w <br />ac <br />0 <br />a <br />00 <br />0 <br />0Z <br />U N <br />C0 <br />d0 <br />wZ_ <br />H <br />z <br />oa <br />Zm <br />0 <br />g <br />D <br />IL <br />O <br />n <br />400 <br />350 <br />300 <br />250 <br />200 <br />150 <br />100 <br />50 <br />EXPLANATION <br />¦ Arizona <br />® Colorado <br />New Mexico <br />® Utah <br />F]Wyoming R <br />1930 1940 1950 1960 1970 1980 <br />Figure 4. Changes in population between 1930 and 1980 in <br />Upper Colorado River Basin (data from the U.S. Bureau of Cen- <br />sus, 1982). <br />systems of canals and ditches. Consumptive use by crops <br />averaged 1.8 million acre-ft/yr during the 1973-82 water <br />years, about 13 percent of the annual virgin streamflow of <br />the Colorado River at Lees Ferry, Ariz., during the same <br />period (U.S. Bureau of Reclamation, written commun., <br />1985). Virgin streamflow is the streamflow that would have <br />occurred in the absence of human intervention upstream. It <br />is an estimate of all water consumptively used or exported <br />from the basin. <br />Irrigated agriculture is the largest source of dissolved <br />solids related to human activities in the Upper Colorado River <br />Basin. Irrigation-return flows generally have a higher <br />dissolved-solids concentration than the applied water, because <br />of the loading effect of salt dissolution in the soil-aquifer <br />system and the concentrating effect of evapotranspiration. <br />Many areas in the basin did not contribute substantially to <br />runoff, and thus to dissolved-solids loading, until the advent <br />of irrigation. Because irrigation practices began before <br />streamflow and water-quality records were initiated, the in- <br />crease in dissolved-solids loading in the basin can only be <br />estimated. <br />Transbasin Exports and Imports <br />Although much of the 'Upper Colorado River Basin is <br />arid, large volumes of water are exported to other basins. <br />Diversions began in 1892 when the Grand River Ditch was <br />constructed in the headwaters of the Colorado River near <br />Grand Lake, Colo. Total exports averaged less than 2,000 <br />acre-ft/yr at the turn of the century. Exports increased to ap- <br />proximately 100,000 acre-ft by 1920, 200,000 acre-ft by <br />1940, and 500,000 acre-ft by 1955 (fig. 6). During the <br />1973-82 water years, annual transbasin exports averaged <br />739,000 acre-ft, about 5 percent of the virgin streamflow? <br />of the Colorado River at Lees Ferry, Ariz. For the same <br />period, 54 percent of the total exports went to the Platte River <br />basin, 17 percent went to the Arkansas River basin, 15 per- <br />cent went to the Rio Grande basin, and 14 percent went to <br />the Great Basin in Utah. Diversions that export water from <br />the Upper Colorado River Basin are listed in table 1. <br />Transbasin exports from the Upper Colorado River <br />Basin tend to increase the downstream concentration of <br />dissolved solids. Exports primarily are from the headwater <br />regions, where dissolved-solids concentrations are low. The <br />removal of this relatively pure water from the headwater <br />regions leaves less water for dilution downstream. <br />Historically, only one transbasin diversion has brought <br />water into the Upper Colorado River Basin. The Tropic and <br />East Fork Canal has diverted water from the Great Basin <br />into the Paria River basin since 1892, averaging 4,800 acre-ft <br />annually during 1974-83 (Upper Colorado River Commis- <br />sion, 1984). <br />Reservoirs <br />The first artificial reservoirs in the Upper Colorado <br />River Basin were constructed during the 1890's, primarily <br />for water storage and irrigation. Strawberry Reservoir, com- <br />pleted in 1912, was the first reservoir that had a capacity <br />greater than 100,000 acre-ft; it stored water for delivery <br />through Strawberry Tunnel to the Great Basin in Utah. Reser- <br />voirs were important for settlement as well as for agriculture <br />because they increased the year-round availability of water <br />in a region characterized by general aridity and seasonal <br />streamflow resulting from snowmelt. Completion of the <br />Colorado River Storage Project during the the 1960's in- <br />creased the combined capacity of reservoirs in the basin to <br />about 38 million acre-ft, more than three times the mean <br />annual flow measured at Lees Ferry, Ariz. Lake Powell, <br />formed by Glen Canyon Dam, is by far the largest reser- <br />voir and has a total capacity of 27 million acre-ft. It is about <br />the size of Lake Mead, which is formed by Hoover Dam <br />in the Lower Colorado River Basin. Eighty-two reservoirs <br />in the Upper Colorado River Basin have a normal capacity <br />greater than 5,000 acre-ft (table 2). <br />The major effects of reservoirs on streamflow are <br />associated with the regulation of streamflow and evapora- <br />tion losses from the water surface. Reservoir regulation tends <br />to decrease the seasonal variability in streamflow; it increases <br />the low-flow volumes during late summer, autumn, and <br />winter and decreases the peak flows occurring during the <br />snowmelt season, April through June. However, discharge <br />patterns downstream from reservoirs become more complex <br />when the timing and magnitude of releases are controlled <br />by power-generation requirements or by diversion projects. <br />Evaporation from Lake Powell during 1973-82 averaged <br />8 Characteristics and Trends of Streamflow and Dissolved Solids in the Upper Colorado River Basin