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Table 8. Selected annual monotonic-trend-analysis results-Green region <br />[Stations with less than 10 years of dissolved-solids data are not reported; n, number of years of dissolved-solids data; acre-ft/yr, acre-feet per <br />year; mg/L, milligrams per liter; tons/yr, tons per year; HS, highly significant (p < 0.01); S, significant (0.01 < p< 0.05); MS, marginally significant <br />(0.05 < p < 0.10); - -, not significant (p > 0.10)] <br /> <br />Site Period <br />(table of <br />3, record <br />plate (water <br />1) years) <br /> <br /> <br />n <br />Annual trend <br />in streamflow <br />Signif- Trend Per- <br />icance (acre- 1 <br />level ft/yr) cent Annual <br /> <br />Concentration <br />Signif-Trend Per- <br />icance 1 <br />level (mg/L) cent trend in <br /> <br /> <br />Signif- <br />icance <br />level dissolved solids <br />Flow-adjusted <br />Load concentration <br />Trend Per- Signif- Trend Per- <br />(tons/ icance <br />yr) cent' level (mg/L) cents <br />22 1962-82 220 -- -- -- -- -- -- S -615 15 -- -- -- <br />23 1966-83 18 -- <br />- <br />-- -- <br />-- -- -- -- -- -- -- <br />24 1964-81 18 -- <br />- -- <br />-- - <br />- -- -- -- -- -- <br />25 1968-83 16 -- - -- -- -- -- <br />27 1962-80 218 MS 1,140 79 -- -- -- S 1,740 53 S 13.9 17 <br />30 1952-63 12 -- -- -- -- -- -- MS -15,600 34 -- -- -- <br />30 1964-83 20 -- -- -- -- -- -- -- -- -- -- -- -- <br />31 1963-83 21 -- -- -- -- -- -- -- -- -- -- -- -- <br />32 1955-83 228 -- -- -- -- -- -- -- -- -- S 3.1 16 <br />33 1955-83 228 -- -- -- HS -9.4 41 -- -- -- HS -5.0 20 <br />34 1965-83 19 -- - -- -- -- -- -- -- <br />38 1951-83 33 -- -- -- HS 9 21 S 3,380 65 HS 1.2 29 <br />40 1951-83 33 S 6,440 71 -- -- -- MS 1,310 50 -- -- -- <br />41 1962-83 22 -- <br />-- -- - <br />- -- -- -- -- -- -- <br />43 1957-83 27 -- -- -- -- -- -- <br />44 1974-83 10 -- -- -- -- -- -- -- -- -- HS -3.5 12 <br />45 1971-83 13 -- -- -- -- -- -- <br />46 1971-83 13 -- -- -- HS -44.1 34 -- -- -- MS -24.2 20 <br />50 1951-68 18 -- -- -- -- -- -- -- -- -- -- -- -- <br />50 1969-83 15 -- -- -- -- -- -- -- <br />53 1949-83 231 -- -- -- S -33.2 37 -- -- -- HS -23.1 28 <br />54 1929-62 34 -- - -- -- -- -- -- -- <br />54 1965-83 19 -- -- -- - -- -- -- -- -- -- <br />57 1947-83 37 -- -- -- -- -- -- <br /> 'Percent change during period of record. <br /> 20ne or more years of data are mi ssing within th e period of record. Percenta ge changes are <br />calcu lated on the entire period. <br />from August through March (fig. 15C). The dissolved-solids <br />concentration is less variable than at site 24; calcium and <br />bicarbonate are the predominant ions throughout the year. <br />Flow-weighted dissolved-solids concentration and load are <br />greater than at site 24, and there is a larger sulfate load. No <br />statistically significant trends were detected during 1968-83. <br />Little Sandy Creek above Eden, Wyo. (site 26) <br />Mean daily streamflow at three sites in the Big Sandy <br />River basin are shown in figure 15D. The streamflow hydro- <br />graph for site 26 (table 3, pl. 1), upstream from the irrigated <br />area, indicates snowmelt beginning in April and peaking in <br />June, and very low streamflow from August through Feb- <br />ruary. Dissolved-solids concentration was relatively small, <br />even during the low-flow season, and the flow-weighted con- <br />centration averaged about 146 mg/L during 1976-81 (table <br />7). Calcium, sodium, and sulfate are the predominant ions <br />throughout the year, and bicarbonate also is a predominant <br />anion during the snowmelt-runoff season. The proportion of <br />dissolved sulfate increased during the low-flow season. No <br />trends were analyzed at this site because of the short period <br />of record. <br />Big Sandy River below Eden, Wyo. (site 27) <br />Mean daily streamflow at site 27 (table 3, pl. 1) is much <br />larger than at site 26 because of the larger drainage area; <br />however, the seasonal pattern is remarkably different (fig. <br />15D). Beginning about May, snowmelt runoff is diverted <br />almost totally for irrigation; irrigation-return flows dominate <br />during the remainder of the year. Mean annual flow-weighted <br />dissolved-solids concentration is large; during 1962-80, it <br />averaged 1,510 mg/L (table 7). Annual dissolved-solids load <br />averaged about 82,000 tons. Sodium and sulfate composed <br />76 percent of the dissolved-solids load. <br />Annual monotonic-trend analyses indicated a marginal- <br />ly significant increase in median annual streamflow of 1,140 <br />acre-ft/yr (table 8). Median annual dissolved-solids load <br />increased significantly, as a result of large increases in base <br />36 Characteristics and Trends of Streamflow and Dissolved Solids in the Colorado River Basin