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<br />Salinity studies of the Uncompahgre Project area (U.S. Bureau of <br />Reclamation, 1984) determined that most of the increase in salt load (equi- <br />valent to dissolved-solids load) in the Uncompahgre River through the study <br />area was caused by surface water entering the shallow ground-water system and <br />dissolving salts from the soil and underlying shale. The shallow ground water <br />then flows through weathered and fractured shale or through sand and gravel <br />layers and discharges into canals, into natural drainages, or directly into <br />the Gunnison River or the Uncompahgre River. A large percentage of the <br />recharge to the ground-water system is from deep percolation of applied irri- <br />gation water and distribution-system losses (U.S. Bureau of Reclamation, <br />1984). Although only about 38 percent of the irrigated area served by the <br />Uncompahgre Project is located on the east side of the valley, 64 percent of <br />the salt-load increase came from project lands on the east side (U.S. Bureau <br />of Reclamation, 1984). Virtually all of the salt loading from irrigated areas <br />on the east side of the valley was caused by surface water dissolving salt <br />from adobe (Mancos) soils or from weathered and fractured shale layers in the <br />Mancos Shale. The water in the Mancos Shale had an estimated salinity concen- <br />tration (or dissolved-solids concentration) of 4,500 mg/L (U.S. Bureau of <br />Reclamation, 1984). <br /> <br />PREVIOUS INVESTIGATIONS <br /> <br />Water-quality data were collected in the Uncompahgre Project area pri- <br />marily to study and monitor salinity; much of the long-term data available <br />are major-ion and dissolved-solids data for stream sites. Trace-element data <br />were collected at two sites on the Gunnison River and two sites on the <br />Uncompahgre River. There are no data available for pesticide concentrations <br />in the study area. Ground-water use in the project area is quite limited; <br />consequently, few water-quality analyses are available. Geochemical data for <br />soils were available for irrigated areas near Delta and Grand Junction. The <br />few biological data were collected from Sweitzer Lake, Ridgway Reservoir, and <br />the Uncompahgre River downstream from Ridgway Reservoir. <br /> <br />Water-Quality Data <br /> <br />Streams <br /> <br />The U.S. Geological Survey collected major-ion and dissolved-solids data <br />from 1959-63 at sites on the Gunnison River between the North Fork confluence <br />and Delta. The only trace-element data collected were for boron. Mean dis- <br />solved-solids concentration (80 samples) was 488 mg/L, and boron concentra- <br />tions ranged from 50 to 150 ~g/L (8 samples). The Colorado Department of <br />Health collected trace-element data for the Gunnison and Uncompahgre Rivers <br />at Delta and for the Uncompahgre River at Ridgway; these data are summarized <br />in table 1. The overall collection period for the data listed in table 1 is <br />1968-88. The data were retrieved from the storage and retrieval (STORET) part <br />of the U.S. Environmental Protection Agency's Water Quality Control <br />Information System. The longest term and most comprehensive water-quality <br />data-collection site in the Gunnison River basin is at the gaging station near <br />Grand Junction (station 09152500 in fig. 1). The U.S. Geological Survey has <br /> <br />20 <br />