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<br />~. <br />..; <br />~.;, <br /> <br />f"l <br />.... <br />> , <br /> <br />..f4 <br />:< ~"1 <br />,] <br /> <br />;.1 <br />;:,',"J <br /> <br />t':~ <br />.;.:.., <br />" <br />:2;':; <br /> <br />r;~ <br />;.;'i <br /> <br />r/' <br /> <br />F;:-~ <br /> <br />~.:}; <br /> <br />.>-,' <br />':"'-; <br /> <br />t:. ~< <br />~,~;i <br /> <br />i~'," <br /> <br />f'''-~ <br />~_:<' <br />Ll <br /> <br />,%~~ <br />"1 <br />'i,:..", <br /> <br />CHAPTER I <br /> <br />INTRODUCTIGl <br /> <br />Problems and Needs <br /> <br />In the study area, an estimated total of about 422,000 tons of salt are <br />picked up annually and conveyed to the Colorado River system. Most salt <br />pickup is attributable to conveyance system seepage and deep percolation as <br />water passes through the weathered and fractured shales of the <br />Mancos Formation. Consumptive use of water and salt pickup by ground-water <br />return flows leave higher salt concentrations in water returning to the river. <br />1\dditional salt sources in the study area include saline water flowing from <br />abandoned oil and gas wells and salt from soils derived from Dakota Sandstone. <br />The frontispiece map depicts the location of salt sources in the unit area. <br /> <br />Information based on 9 years of record shows that the inflow water <br />quality varies from 50 milligrams per liter (mg/L) total dissolved solids <br />(TDS) in the mountain streams to 84 mg/L TDS in the North Fork of the <br />Gunnison River at Somerset gauge and 176 mg/L TOS in the Gunnison River above <br />the confluence with the North Fork. Outflow water quality of the <br />Gunnison River as it leaves the unit area averages 398 mg/L TOS, while <br />tributaries in the saline areas are as high as 7,000 mg/L TOS for individual <br />samples. <br /> <br />Ground-water quality varies from l,OOO to 12,000 mg/L TOS below irrigated <br />areas. Records confirm that TOS concentration in an old unplugged gas well <br />near Austin has reached 30,416 mg/L TOS, the highest recorded concentration in <br />the study area. <br /> <br />Salt reduction estimates for this preliminary findings memorandum were <br />obtained from available Bureau of Reclamation (Reclamation) and U.S. <br />Geological Survey (USGS) gauging station data in the study area. This <br />information was correlated with data from the Grand Valley unit, <br />Colorado River Basin Salinity Control project, and Lower Gunnison Basin unit, <br />Colorado River Water Quality Improvement Program. In or near the unit area, <br />the USGS has 11 gauging stations that monitor daily flows of the <br />Gunnison River and many of the major tributaries. At the North Fork of the <br />Gunnison River near Somerset, USGS also collects water quality data. In' <br />addition to the USGS gauging network, Reclamation maintains a variety of <br />gauging stations ranging from monthly grab sample sites to daily flow <br />stations. <br /> <br />Salt loading from the Cottonwood Creek, Unnamed Gulch, Alum Gulch, and <br />North Delta Canal watersheds was estimated with summer and winter grab sample <br />runs for wetted perimeters and water quality on the canals and laterals. <br />Seepage rates were assumed to be similar to those found in the Grand Valley <br />unit. Ground-water quality was assumed to be similar to that found in the <br />Lower Gunnison Basin unit for similar geologic formations. The salinity <br />estimates for the remaining watersheds were based on a proration of remaining <br />salt contributions from the off-farm sources. <br /> <br />Many identified ground-water seeps, springs, and abandoned oil and gas <br />wells are believed to be adding to the salt loading of the area. Salt loading <br />estimates of the abandoned oil and gas wells were determined from grab samples <br />obtained in the summer of 1985. Of six abandoned test wells located on the <br />south bank of the Gunnison River, one near Austin intermittently spews saline <br /> <br />2 <br /> <br />OIJ()928 <br />