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Table 6. Selected annual monotonic-trend-analysis results-Grand region <br />[Sites having 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 year; <br />mg/L, milligrams per liter; tons/yr, tons per year; HS, highly significant (p 4 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 ' <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/ 1 icance <br />yr) cent level (mg/L) cents <br />2 1947-83 37 -- -- -- S 0.4 22 -- -- -- -- <br />3 1947-83 37 -- -- -- S -1.9 21 HS -1,250 26 HS -2.1 23 <br />4 1959-83 25 -- -- -- S -2.4 24 -- -- -- HS -1.0 11 <br />5 1950-83 34 -- -- -- -- -- -- -- -- -- -- <br />6 1959-83 25 -- -- -- -- -- -- -- -- -- -- -- -- <br />8 1973-82 10 -- -- -- -- -- -- -- -- -- -- -- -- <br />10 1934-49 16 -- -- -- MS -5.8 21 -- -- -- -- -- -- <br />10 1950-83 34 -- <br />11 1969-79 11 -- -- -- -- -- -- -- -- -- -- <br />12 1959-80 22 -- -- -- HS -20.4 30 S -3,810 22 HS -19.3 28 <br />13 1934-65 32 -- -- -- -- -- -- -- -- -- S -2.8 13 <br />13 1966-83 18 -- -- -- S -16.1 39 -- -- -- HS -9.9 26 <br />15 1974-83 10 S 1,620 26 S -38.4 25 MS -2,770 19 MS -37.0 25 <br />17 1974-83 10 S 2,220 40 -- <br />18 1962-83 .22 -- -- -- MS -11.2 34 -- -- -- HS -4.8 16 <br />20 1952-83 32 -- -- -- -- -- -- HS 4,990 46 HS 4.7 24 <br />21 1929-49 21 -- <br />21 1950-65 16 -- -- - -- -- -- -- -- " -- <br />21 1966-83 18 -- -- -- -- -- -- -- -- -- MS -2.9 9 <br /> 'Percent change during period of record. <br />a 22-percent increase in median annual concentration dur- <br />ing the 37-year period. The monotonic trend in median <br />annual streamflow since 1947 was not statistically signifi- <br />cant, perhaps because of the large annual variability and the <br />large streamflow volume during 1983. <br />Eagle River at Gypsum, Colo. (site 3) <br />Although the streamflow at site 3 (table 3, pl. 1) is com- <br />parable to the Colorado River preintervention streamflow at <br />site 2, the dissolved-solids concentration is much higher. The <br />mean annual flow-weighted dissolved-solids concentration <br />is 288 mg/L, and the mean annual streamflow is about <br />410,000 acre-ft (table 5). Sources of dissolved solids include <br />mining operations and surface outcrops of Pennsylvanian <br />sedimentary formations. Outcrops of the Eagle Valley <br />Evaporite contain thick salt beds (Warner and others, 1985). <br />During the snowmelt season (May-July), calcium and bicar- <br />bonate are the predominant ions. Calcium and sulfate <br />predominate during the remainder of the year. The Home- <br />stake Tunnel has only slightly affected the streamflow of the <br />Eagle River (fig. 8B). <br />Although streatnflow has not changed significantly, <br />dissolved solids decreased during 1947-83. Annual <br />monotonic-trend analyses indicated a significant decrease in <br />median annual dissolved-solids concentrations of 1.9 mg/L <br />per year, and highly significant decreases in values of median <br />annual dissolved-solids load of 1,250 tons/yr and flow- <br />adjusted concentration of 2.1 mg/L per year (table 6). Dur- <br />ing the 37-year period, these trends represent a 21-percent <br />decrease in median annual concentration, a 26-percent <br />decrease in median annual load, and a 23-percent decrease <br />in median annual flow-adjusted concentration. Median annual <br />flow-adjusted concentrations of all major constituents also <br />decreased. The cause of the decrease is unknown, but may <br />be related to the change from mining and agricultural land <br />uses to recreational land use. <br />Colorado River near Dotsero, Colo. (site 4) <br />Streamflow at site 4 averages approximately 1.4 million <br />acre-ft/yr, and the mean annual, flow-weighted dissolved- <br />solids concentration is about 213 mg/L (table 5). Calcium <br />and bicarbonate are the predominant ions throughout the <br />year. Sulfate also is a predominant ion during the low-flow <br />season because of the large load contributed by the Eagle <br />River. During 1959-83, annual monotonic-trend analyses <br />indicated a significant decrease in median annual dissolved- <br />solids concentration of 2.4 mg/L per year and a highly signifi- <br />cant decrease in median annual flow-adjusted concentration <br />Upper Colorado Subregion 23