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33° <br />OZ <br />JO <br />W <br />Q N <br />W <br />?CL <br />H <br />C/) I_ <br />}w <br />J W <br />LL <br />a <br />°m <br />aU <br />w <br />Z <br />2 <br />-A - <br />1939-83 <br />I I I I I I I I I I I <br />800 <br />600 <br />400 <br />200 <br />=B <br />1897-1906 <br />---- 1920-65 <br />------ 1966-83 ?? - <br />-------------- -------- - <br />15,000 <br />10,000 <br />5000 <br />OCT NOV DEC JAN FEB MAR APR MAY JUNE JULY AUG SEPT <br />Figure 10. Mean daily streamflow at selected sites in Gunnison subregion of Grand region. A, Site 12, <br />Uncompahgre River at Delta, Colo. B, Site 13, Gunnison River near Grand Junction, Colo. <br />was identified (table 4). This decrease is 8 percent of the <br />preintervention median. It corresponds in magnitude with <br />the decrease in the load at site 12 on the Uncompahgre River, <br />which is tributary to the Gunnison River upstream from site <br />13. Monthly step-trend decreases in dissolved-solids concen- <br />tration of about 600 mg/L occurred during the low-flow <br />season of August through March; corresponding increases <br />in streamflow also occurred (fig. 11). Streamflow and <br />dissolved-solids load decreased during the snowmelt period <br />of May and June, and dissolved-solids concentration in- <br />creased slightly during May. <br />Annual monotonic-trend analysis for the preinterven- <br />tion period indicated a significant decrease in median annual <br />flow-adjusted concentration of 2.8 mg/L per year, a <br />13-percent decrease in the median during the 32-year period. <br />During the postintervention period, annual monotonic-trend <br />analyses indicated a significant decrease in median annual <br />dissolved-solids concentration of 16.1 mg/L per year and a <br />highly significant decrease in median annual flow-adjusted <br />concentration of 9.9 mg/L per year. These trends represent <br />a 39-percent decrease in median annual concentration and <br />a 26-percent decrease in median annual flow-adjusted <br />concentration during the 18-year period. The postinterven- <br />tion trends may be related to the completion of Morrow Point <br />and Crystal Reservoirs downstream from Blue Mesa <br />Reservoir. <br />Lower Colorado Subregion <br />The lower Colorado subregion includes the drainage <br />areas of the Dolores River and its tributaries and the Colo- <br />rado River between Grand Junction, Colo., and the con- <br />fluence with the Green River. About 70,000 acres is irrigated <br />along the Colorado River in the Grand Valley near Grand <br />Junction. Irrigation water for about 32,000 acres is supplied <br />by the Grand Valley Canal (constructed before 1900) and <br />Redlands Power Canal. The remaining area is supplied by <br />the Government Highline Canal built by the Federal Grand <br />Valley Project in 1917. This canal takes water diverted from <br />a dam across the Colorado River upstream from Grand Junc- <br />tion and transports it to cropland parallel to the river for 55 <br />mi. Total irrigation diversions averaged 400,000 acre-ft/yr <br />by the early 1930's. Consumptive use by irrigation has been <br />estimated at 247,000 acre-ft/yr (U.S. Bureau of Reclama- <br />tion, 1985a). Most of the irrigated land in the Grand Valley <br />is underlain by Cretaceous Mancos Shale, which is a source <br />of mineral salts dissolved in irrigation-return flow. The U.S. <br />Bureau of Reclamation (1985a) estimated that 580,000 tons <br />of dissolved solids per year is added to the Colorado River <br />in the Grand Junction area. As part of the Colorado River <br />Basin Salinity Control Program, the lining of canals and <br />laterals has been started. The completed project will decrease <br />the dissolved-solids input by an estimated 140,000 tons/yr. <br />Stage I of the project, affecting about 10 percent of the <br />irrigated area, was completed in April 1983. <br />Approximately 28,000 acres is irrigated within the San <br />Miguel River basin and about 7,000 acres in the remainder <br />of the Dolores River basin. About 116,000 acre-ft of water <br />is exported annually from the Dolores River to Montezuma <br />Valley in the San Juan River basin for irrigation of 37,000 <br />acres (U.S. Forest Service and others, 1976). The Dolores <br />Project, under construction since 1977, will export an addi- <br />tional 81,000 acre-ft/yr of water to the San Juan River basin. <br />The Dolores River channel crosses Paradox Valley, one <br />of a series of collapsed salt anticlines in the Paradox Basin. <br />The river flows directly across the soluble Paradox Member <br />of the Hermosa Formation, which is composed of about <br />14,000 ft of halite and halite-rich shale. As specified in Title <br />H of the Colorado River Basin Salinity Control Act, con- <br />struction of salinity-control facilities in the Paradox Valley <br />28 Characteristics and Trends of Streamflow and Dissolved Solids in the Colorado River Basin