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Table 10. Selected annual monotonic-trend-analysis results-San Juan 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 < 0.01); S, significant (0.01 < p < 0.05); MS, marginally significant <br />(0.05 < p < 0.10); - -, not significant (p > 0.10)] <br />Annual trend in dissolved solids <br />Site Period Annual trend Flow-adjusted <br />(table of in streamflow Concentration Load concentration <br />3, record Signif- Trend Per- Signif- Trend Per- Signif- Trend Per- Signif- Trend Per- <br />plate (water n icance (acre- cents icance 1 icance (tons/ 1 icance 1 <br />1) years) level ft/yr) level (mg/L) cent level yr) cent level (mg/L) cent <br />60 1963-83 21 -- -- -- S -0.3 17 -- -- -- S -0.3 17 <br />61 1964-83 20 -- -- -- MS -1.1 12 -- -- -- -- -- -- <br />62 1955-83 29 -- -- -- -- -- -- -- <br />63 1962-82 21 -- - -- -- -- -- -- -- -- -- <br />65 1964-83 20 -- -- -- MS -3.7 20 -- -- -- S -2.7 15 <br />68 1930-61 32 -- -- -- -- -- -- -- -- -- S -1.5 10 <br />68 1964-83 20 -- -- -- MS -7.1 26 -- -- -- S -3.7 14 <br />69 1942-62 21 -- -- -- S 7.3 33 -- -- -- S 3.3 14 <br />69 1966-80 15 -- - -- -- -- -- -- <br />'Percent change during period of record. <br />low-flow season. Excluding the Animas River inflow, about <br />65,000 tons/yr of dissolved solids is added to the San Juan <br />River in the reach between Archuleta and Farmington, N. <br />Mex., mostly as dissolved sulfate. Irrigation-return flows <br />from agricultural lands possibly are the source of this in- <br />crease. Because of the upstream regulation, dissolved-solids <br />concentration does not vary greatly throughout the year. No <br />statistically significant annual monotonic trends were detected <br />for this site. <br />Chaco River near Waterflow, N. Mex. (site 64) <br />The Chaco River drains a large, but arid, region south <br />of the San Juan River and discharges into the San Juan River <br />just upstream from Shiprock, N. Mex. Site 64 (table 3, pl. <br />1) is about 5 mi downstream from the Four Corners Power- <br />plant, a large, coal-fired utility that began operating in 1967. <br />Coal is supplied from a large strip mine upstream, where <br />Upper Cretaceous deposits in the Fruitland Formation are <br />overlain by Kirtland Shale. Water is pumped from the San <br />Juan River to Morgan Lake, beside the powerplant, where <br />it is used for cooling purposes. Wastewater from the plant <br />drains from several holding ponds into the Chaco River, <br />creating a perennial stream downstream from the powerplant. <br />Base flow is maintained at about 15 ft3/s. The remainder <br />of the flow of the Chaco River is almost entirely from occa- <br />sional, intense rainfall (fig. 22D). Mean annual flow- <br />weighted dissolved-solids concentration averages 801 mg/L, <br />and the mean dissolved-solids load is 33,000 tons/yr (table <br />9), 72 percent of which is sodium and sulfate. <br />San Juan River at Shiprock, N. Mex. (site 65) <br />Streamflow at site 65 (table 3, pl. 1) is about the same <br />as at site 63, but dissolved-solids concentration and load are <br />greater. Of the dissolved solids contributed in the reach, 74 <br />percent is dissolved sodium and sulfate. During 1964-83, <br />mean annual flow-weighted dissolved-solids concentration <br />averaged 324 mg/L (table 9). Calcium, bicarbonate, and <br />sulfate are the predominant ions during the high-flow season. <br />Calcium and sulfate are predominant during the low-flow <br />season. The proportion of dissolved sulfate in the dissolved- <br />solids load increases from 32 percent at site 61 to 41 per- <br />cent at site 63 and to 45 percent at site 65. The seasonal <br />variability of streamflow and dissolved solids at site 65 <br />markedly decreased after the closure of Navajo Reservoir. <br />The period of record was divided into a preintervention <br />period (1958-61) and a postintervention period (1964-83) <br />based on the initial filling of Navajo Reservoir. Because of <br />the short preintervention period, step trends were not <br />evaluated nor were monotonic trends evaluated for that <br />period. Annual monotonic-trend analyses for the postinter- <br />vention period indicated marginally significant decreases in <br />median annual dissolved-solids concentration of 3.7 mg/L <br />per year and significant decreases in median annual flow- <br />adjusted concentration of 2.7 mg/L per year (table 10). These <br />decreases represent a 20-percent change in the median an- <br />nual concentration and a 15-percent change in the median <br />annual flow-adjusted concentration during the 20-year period. <br />Mancos River near Cortez, Colo. (site 66) <br />Site 66 (table 3, pl. 1) is downstream from about 12,000 <br />acres of irrigated land underlain by Mancos Shale. Navajo <br />Wash drains additional irrigation area and discharges into <br />the Mancos River downstream from the site. Therefore, the <br />Mancos River contributes substantially more dissolved solids <br />than reported for this site. Snowmelt runoff from the moun- <br />tain headwaters results in a hydrograph peak from April <br />through June. Calcium and sulfate are predominant through- <br />out the year. Magnesium also becomes predominant during <br />52 Characteristics and Trends of Streamflow and Dissolved Solids in the Colorado River Basin