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San Juan Region <br />The San Juan region consists of the San Juan River <br />drainage basin and the large and area downstream from the <br />confluence of the Green and Colorado Rivers. Most of the <br />flow of the San Juan River originates on the western slope <br />of the Rocky Mountains in Colorado. Streamflow contributed <br />to the Colorado River in this region originates almost en- <br />tirely in the San Juan River basin. The San Juan region <br />contains 35 percent of the total drainage area of the Upper <br />Colorado River Basin and contributes 16 percent of the <br />streamflow and 14 percent of the dissolved-solids load. Lake <br />Powell extends upstream to within about 20 mi of the con- <br />fluence of the Green River, and it has inundated many <br />features in the region, including the mouth of the San Juan <br />River and the former town of Hite, Utah. Except for minor <br />inputs from the Paria River, the flow of the Colorado River <br />leaving the Upper Colorado River Basin is completely con- <br />trolled by Glen Canyon Dam and Lake Powell. During <br />1966-80, the mean annual streamflow of the Colorado River <br />at Lees Ferry, Ariz. (site 69) (table 3, pl. 1), was about 8.8 <br />million acre-ft, mean annual flow-weighted dissolved-solids <br />concentration was 564 mg/L, and the dissolved-solids load <br />was about 6.7 million tons (table 9). <br />Data from 13 sites were evaluated for the San Juan <br />region (pl. 1). Mean annual streamflows, dissolved-solids <br />concentrations and loads, and major-constituent loads were <br />determined at each of these sites (table 9). Chemical com- <br />position of streamflow for selected sites is shown in figure <br />21. Selected monotonic trend-analysis results are listed in <br />table 10. The San Juan region was divided into two sub- <br />regions: the San Juan and the main stem (pl. 1). <br />San Juan Subregion <br />The San Juan subregion consists of the entire San Juan <br />River basin. Large tracts of land are irrigated along the San <br />Juan and Animas Rivers in the vicinity of the towns of <br />Farmington, Bloomfield, and Fruitland, N. Mex. Navajo <br />Dam and Reservoir is the largest water-storage project in <br />the San Juan region. Completed in 1963 and having a capacity <br />of about 1.7 million acre-ft (table 2), Navajo Reservoir is <br />the third largest reservoir in the Upper Colorado River Basin. <br />The Navajo Indian Irrigation Project diverts water from the <br />reservoir to supply Navajo Indian lands east of the Chaco <br />River. Delivery of water to the Navajo Indian Irrigation <br />Project began in 1976. Delivery during 1984 totaled 120,000 <br />acre-ft, about one-half of the estimated depletion at full <br />development. <br />Several diversions export water from the San Juan <br />River basin to the Rio Grande basin. The largest is Azotea <br />Tunnel, which has exported about 107,000 acre-ft/yr from <br />the Navajo River and Rio Blanco drainages since 1971 (table <br />1), as part of the San Juan-Chama Project. Vallecito Reser- <br />voir, Lemon Reservoir, and Electra Lake provide water <br />storage in the Los Pinos and Animas River drainages. Large <br />volumes of irrigation water are imported to the McElmo <br />Creek drainage from the Dolores River through the <br />Montezuma Tunnel. <br />Vallecito Creek near Bayfield, Colo. (site 60) <br />Streamflow in the headwaters of the San Juan drainage <br />generally has low dissolved-solids concentrations. Site 60 <br />(table 3, pl. 1) has very large mean annual runoff, averag- <br />ing 26.8 in., and very low mean annual flow-weighted <br />dissolved-solids concentration, averaging 34 mg/L (table 9). <br />The site is upstream from Vallecito Reservoir, and seasonal <br />streamflow consists of a broad snowmelt-runoff peak fol- <br />lowed by a gradual recession period and very little stream- <br />flow during the winter months (fig. 22A). Calcium and <br />bicarbonate are the predominant ions throughout the year. <br />Analyses of annual monotonic trends indicated small <br />but significant decreases in median annual dissolved-solids <br />concentration of 0.3 mg/L per year and in median annual <br />flow-adjusted concentration of 0.3 mg/L per year (table 10). <br />These decreases represent a 17-percent change in the median <br />annual concentration and in the median annual flow-adjusted <br />concentration during the 21 years of record. Most of this <br />change results from a decrease in dissolved sulfate. The cause <br />of this decrease is not known. <br />San Juan River near Archuleta, N. Mex. (site 61) <br />Site 61 (table 3, pl. 1) is 7 mi downstream from Navajo <br />Dam. About one-half of the total flow of the San Juan River <br />enters the river upstream from this site. Streamflow has been <br />completely regulated since June 1962. Although the initial <br />filling period of the reservoir ended in June 1964, storage <br />did not exceed 1 million acre-ft of its 1.7 million acre-ft <br />capacity until 1968. The effect of reservoir storage and <br />releases on streamflow is shown in figure 22B. Prior to 1962, <br />streamflow was dominated by snowmelt runoff; after the <br />initial reservoir filling, streamflow was almost constant. <br />Although the seasonal variability in dissolved-solids con- <br />centration has been greatly decreased, the mean annual <br />dissolved-solids concentration has not changed between the <br />two periods. From 1964 to 1983, mean annual flow-weighted <br />dissolved-solids concentration averaged 166 mg/L (table 9). <br />Calcium and bicarbonate are the predominant ions throughout <br />the year. <br />The period of record was divided into a preintervention <br />period (1956-61) and a postintervention period (1964-83) <br />(table 4), based on the initial filling of Navajo Reservoir. <br />No annual step trends were statistically significant. There <br />is no evidence of leaching or mineral precipitation in the <br />reservoir. Monthly step trends in streamflow and dissolved- <br />solids concentration and load indicate the decrease in seasonal <br />variability after the initial filling of the reservoir (fig. 23A). <br />Annual monotonic-trend analyses of the postinter- <br />vention period indicated a marginally significant decrease <br />in median annual dissolved-solids concentration of 1.1 mg/L <br />San Juan Subregion 49