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<br /> en 32,000 <br /> z <br /> ~ 28,000 <br /> ;;:; <br /> ci 24.000 <br />N 9 20.000 <br />t'.) en <br />c 18,000 <br />W ~ <br />W;:. 12,000 <br />'" <br /> w <br /> ~ MOO <br /> 0 <br /> en 4,000 <br /> en <br /> i5 <br /> ::; 0 <br /> :I: <br /> iz -4.000 <br /> 0 <br /> ::Ii -MOO <br /> c <br /> w <br /> Iii -12.000 <br /> :J <br /> .., <br /> C .18,000 <br /> "f <br /> ~ -20.000 <br /> ..J <br /> u. <br /> -24,000 <br /> 1978 <br /> <br />STATION 09095500 <br />STATION 09152500 <br />STATION 09163500 <br /> <br /> <br />"/ <br />I <br />/ <br />I <br />II <br />I <br />II <br /> <br /> <br />I/<~~""""""""""'"'''''''''''''''''''''''' <br /> <br />/ .... <br />....... <br /> <br />" <br />, <br />, <br />\ <br />\ <br />\ <br />\ <br />\ <br />\ <br />\ <br />\ <br />, <br />.....................~:-:-:-................................. <br />.......... <br />..... <br />........ <br />............ <br />............ <br /> <br /> <br />1980 <br /> <br />1982 <br /> <br />1984 <br /> <br />1986 <br />WATER YEAR <br /> <br />1988 <br /> <br />1990 <br /> <br />1992 <br /> <br />1994 <br /> <br />Figure 7. LOWESS smooth curves of flow-adjusted monthly dissolved-solids loads at stations 09095500 <br />Colorado River near Cameo, 09152500 Gunnison River near Grand Junction, and 09163500 Colorado River <br />near the Colorado-Utah State line, water years 1980-93. <br /> <br />Trend results on the seasonal loads for August <br />through October and November through February were <br />variable (table 5). None of the trends in unadjusted <br />seasonal loads for August through October were signif- <br />icant (alpha 0.05). Trends in flow-adjusted loads for <br />August through October were highly significant <br />(decreasing loads with time) for station 09095500 <br />for water years 1986-93 and for station 09152500 <br />for 1970--93 (table 5). Although the flow-adjusted <br />loads for August through October for the three test <br />periods indicated decreasing loads with time for <br />station 09163500, the p values of the trends were <br />not significant. <br />Trends in unadjusted dissolved-solids loads for <br />November through February (table 5) were variable, <br />and the most notable result is the highly significant <br />downward trend in loads at station 09095500 for water <br />years 1986-93. The trend in flow-adjusted load also <br />was highly significant and downward for 1986-93 for <br />station 09095500. The salinity-control projects in the <br />Grand Valley primarily are designed to decrease the <br />quantity of subsurface irrigation drainage, which is the <br /> <br />mechanism of transport of irrigation-induced salinity <br />to the Colorado River (Bureau of Reclamation, 1986). <br />During the low-flow period of the year, a decrease <br />in irrigation-drainage load from the Grand Valley <br />might cause a trend in dissolved-solids loads at <br />station 09163500 during November through February. <br />Although the trend for the November through February <br />loads was downward for 1986-93 at station 09163500, <br />the trend was statistically not significant (table 5). As <br />discussed with annual loads, the small sample size <br />(eight values) for the seasonal data for 1986-93 make <br />it more difficult to reject the null hypothesis of no <br />trend. <br /> <br />Grand Valley Dissolved-Solids Load <br /> <br />The Grand Valley dissolved-solids load is <br />the annual dissolved-solids load to the Colorado <br />River from the Grand Valley (fig. 1), and at least <br />95 percent of that load was irrigation induced (Bureau <br />of Reclamation, 1986). The trends in annual Grand <br />Valley dissolved-solids load (table 1) were downward <br /> <br />20 Trend Analysla 01 Selected Water.Quallty Data Associated With Sallnlty-Control Projects In the Grand Valley, <br />In the Lower Gunnison River Basin, and ~t Meeker Dome, Western Colorado <br />