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contain large quantities of soluble material; streamflow con- <br />tains relatively high concentrations of dissolved magnesium <br />and bicarbonate but low concentrations of dissolved sulfate. <br />During the snowmelt season, calcium and bicarbonate are <br />the predominant ions. Sodium, calcium, magnesium, and <br />bicarbonate predominate during the low-flow season. No <br />statistically significant annual monotonic trends were detected <br />during 1969-79. <br />Gunnison Subregion <br />The drainage area of the Gunnison subregion (pl. 1) <br />is about 8,000 mil. The Gunnison River is the largest <br />tributary to the Colorado River in Colorado and originates <br />in high mountainous terrain. Irrigation in the Gunnison <br />subregion began about 1890, and more than 200,000 acres <br />was irrigated during 1986, of which about 90,000 acres is <br />along the Uncompahgre River, about 20,000 acres is along <br />Tomichi Creek in the upper Gunnison area, and most of the <br />remainder is near the town of Delta, Colo., in the lower <br />reaches of the Gunnison basin. The large Uncompahgre and <br />lower Gunnison areas are underlain by Mancos Shale. Irri- <br />gation water applied to land underlain by Mancos Shale <br />causes weathering and dissolution of mineral salts from the <br />soils and underlying shale. As a result, the water returns to <br />the river with a larger dissolved-solids load than it had before <br />it was diverted (Iorns and others, 1965). Annual agricultural <br />dissolved-solids loading has been estimated at 360,000 tons <br />from the Uncompahgre Valley and 480,000 tons from the <br />lower Gunnison area (U.S. Department of the Interior, <br />1985), which makes the Gunnison subregion the largest <br />agricultural source of dissolved solids in the Upper Colorado <br />River Basin. <br />Three small transbasin diversions, the Larkspur, Tabor, <br />and Tarbell ditches export water from the Gunnison River <br />subregion to the Arkansas River and Rio Grande basins. <br />Large volumes of water are diverted within the subregion <br />through the Gunnison Tunnel, which transports water from <br />the Gunnison River to the Uncompahgre Valley. Diversions <br />through the tunnel began in 1910, totaled 117,000 acre-ft <br />during 1915, 250,000 acre-ft during 1930, and 352,000 acre- <br />ft during 1950. Taylor Park Dam was built in 1935 for <br />storage as part of the Uncompahgre Project. <br />Three large dams were built for power generation and <br />water storage on the main stem of the Gunnison River as <br />part of the Colorado River Storage Project. Together the <br />reservoirs constitute the Wayne N. Aspinall Unit, formerly <br />known as the Curecanti Unit. The largest and farthest <br />upstream is Blue Mesa Reservoir; the others are Morrow <br />Point Reservoir and Crystal Reservoir. <br />Uncompahgre River at Delta, Colo. (site 12) <br />Streamflow at site 12 (table 3, pl. 1) is affected by im- <br />ports from the Gunnison Tunnel from April through October <br />and by substantial evapotranspiration from irrigated <br />croplands. The streamflow hydrograph for site 12 is char- <br />acterized by a modest snowmelt-runoff peak during May and <br />June and a prominent irrigation-return flow period lasting <br />from September through mid-November (fig. 10A). Calcium <br />and sulfate are the predominant ions during the entire year. <br />Dissolved sulfate makes up about 60 percent of the dissolved- <br />solids load. The river also transports large loads of dissolved <br />sodium, magnesium, and bicarbonate, but only a small load <br />of dissolved chloride. Annual flow-weighted dissolved-solids <br />concentration averages about 1,260 mg/L (table 5). <br />Annual flow of the Uncompahgre River at site 12 did <br />not change significantly during 1959-80, but dissolved-solids <br />concentration and load have decreased since the late 1960's. <br />Annual monotonic-trend analyses indicated highly signifi- <br />cant decreases in median annual values of dissolved-solids <br />concentration of 20.4 mg/L per year and flow-adjusted con- <br />centration of 19.3 mg/L per year, and a significant decrease <br />in median annual dissolved-solids load of 3,810 tons/yr (table <br />6). During the 22-year period, these trends represent a <br />30-percent decrease in median annual concentration, a <br />28-percent decrease in median annual flow-adjusted concen- <br />tration, and a 22-percent decrease in median annual load. <br />All major constituents, except dissolved bicarbonate, de- <br />creased significantly in concentration and flow-adjusted <br />concentration. Flow-adjusted concentration decreased dur- <br />ing all months. The reason for this decline is unknown, but <br />it may be related to regulation and storage by Blue Mesa <br />Reservoir, which is downstream from the irrigated areas in <br />the upper reaches of the Gunnison River and upstream from <br />the diversion point of the Gunnison Tunnel. <br />Gunnison River near Grand )unction, Colo. (site 13) <br />Streamflow hydrographs for site 13 (table 3, pl. 1) are <br />shown in figure 10B. During 1897-1906, a flattening of the <br />snowmelt-runoff peak from diversions for agriculture <br />occurred; the peak further decreased after 1906 because of <br />irrigation diversions through the Gunnison Tunnel. Regula- <br />tion by reservoirs in the Wayne N. Aspinall Unit after 1965 <br />has not decreased the annual flow of the Gunnison River but <br />has approximately halved the flow during the snowmelt <br />season and doubled the flow during the base-flow period. <br />Streamflow and dissolved-solids concentration are less <br />variable throughout the year, and from year to year. As at <br />site 12, the dissolved-solids composition is predominantly <br />calcium and sulfate, with small quantities of sodium, <br />magnesium, and bicarbonate. Although the chemical com- <br />position of streamflow is similar to that of the Uncompahgre <br />River, the dissolved-solids concentration is lower because <br />of dilution from the main stem of the Gunnison River. <br />The period of record at site 13 was divided into a <br />preintervention period (1934-65) and a postintervention <br />period (1966-83), based on the completion of Blue Mesa <br />Dam. The annual step trends in streamflow and dissolved- <br />solids concentration were not significant, but a marginally <br />significant decrease of 119,000 tons in dissolved-solids load <br />Gunnison Subregion 27