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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
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