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200 <br />100 <br />0 <br />300 <br />0 200 <br />Z <br />O <br />U 100 <br />w <br />U) 0 <br />ir <br />w <br />0- 30,000 <br />w <br />T 20,000 <br />U <br />10,000 <br />U <br />Z 0 <br />3 1000 <br />O <br />J <br />LL <br />Q 500 <br />Lu <br />x <br />F- <br />t/) 0 <br />} <br />Q 4000 <br />D <br />Z <br />w 2000 <br />2 <br />0 <br />40,000 <br />20,000 <br />0 <br />A 1974-83 <br />B <br />1974-83 <br />C <br />1952-65 <br />---- 1966-83 <br />D <br />1950-83 <br />E <br />1952-83 <br />F <br />1914-34 <br />-- 1935-49 <br />- ---- 1950-65 <br />------ 1%6-83 <br />I oil Rill I <br />OCT NOV DEC JAN FEB MAR APR MAY JUNE JULY AUG SEPT <br />Figure 12. Mean daily streamflow at selected sites in lower Colorado subregion of Grand region. A, Site <br />15, Reed Wash near Loma, Colo. B, Site 17, Salt Creek near Mack, Colo. C, Site 18, Colorado River near <br />Colorado-Utah State line. D, Site 19, San Miguel River at Uravan, Colo. E, Site 20, Dolores River near Cisco, <br />Utah. F, Site 21, Colorado River near Cisco, Utah. <br />month. Sodium also is a predominant cation during the low- <br />flow season. Leaching from the underlying Mancos Shale <br />contributes large quantities of calcium, magnesium, and <br />sulfate. The source water from the Colorado River contains <br />large quantities of sodium and chloride from upstream ther- <br />30 Characteristics and Trends of Streamflow and Dissolved Solid <br />mal springs, and the concentration of these constituents in <br />irrigation-return flow is increased because of evapotranspira- <br />tion. The combined mean annual dissolved-solids load from <br />sites 14, 15, 16, and 17 is about 303,000 tons (table 5). Other <br />sites in the Grand Valley where irrigation-return flow was <br />s in the Colorado River Basin