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<br />INTRODUCTION <br /> <br />o <br />~ Increasing salinity is threatening to become a major economic problem for users of Colorado <br />W River Water [Kleinman and Brown, 1980]. This basinwide problem affects more than 18 million <br />municipal, agricultural, and industrial users in the lower Colorado River basin as well as the <br />Republic of Mexico. <br /> <br />In 1988 it was estimated that the total annual salinity damages from the use of Colorado River <br />water in the lower Colorado River basin had reached about $300 million; damages are expected <br />to reach $900 million per year by the year 2010 [Lohman, et aI. 1988]. <br /> <br />Damages to agricultural users are in the form of reduced crop yields, added labor costs for <br />irrigation management, and added drainage requirements, Urban users incur additional costs due <br />to more frequent replacement of plumbing and water-using appliances, use of water softeners, <br />and the purchase of bottled water. Industrial users and water treatment and waste water utilities <br />incur reductions in the useful life of system facilities and equipment from increased levels of <br />salinity [Colorado River Basin Salinity Forum, 1990]. <br /> <br />The Colorado River Basin Salinity Control Act of 1984, as amended (Public Law 98-569); the <br />Clean Water Act of 1987 (p.L. 100-4); the Water Resources Planning Act of 1983, as amended <br />(p,L. 97-449); and Executive Order 12088 ("Federal Compliance With Pollution Control <br />Standards") as amended by Executive Order 12580, all provide direction for reducing nonpoint <br />source pollution (salinity) to the Colorado River System from public lands. <br /> <br />The Grand Resource Area Resource Management Plan identifies control of salinity and <br />sedimentation of the Colorado River from public lands as the Critical Watershed issue in the <br />Grand Resource Area, Moab District, Bureau of Land Management (ELM). Salinity control, <br />as reflected in the management actions of the RMP, involves two options: (1) the use of <br />mechanical treatments to stimulate restoration of degraded areas and control runoff and sediment <br />production and (2) management of resource activities that disturb the soil surface, <br /> <br />In 1985 the Greater Sagers Wash Watershed was identified as one of the major salt producing <br />watersheds in the Moab District. The Greater Sagers Wash Watershed is an area of <br />approximately 153,200 acres located 5 miles east of Thompson, Utah, within the Grand <br />Resource Area, Moab District, BLM. (See Figure 1.0). The watershed has its headwaters in <br />the Book Cliffs at an elevation of about 9,000 feet and empties into the Colorado River <br />approximately 32 miles to the southeast at McGraw Bottom, at an elevation of about 4,100 feet. <br />Approximately 60 percent of the watershed is characterized by Mancos Shale-derived saline- <br />alkali soils which are naturally high salt producers. The majority of the watershed is <br />characterized by sparse vegetation cover, high rates of erosion, and high peak flows. <br /> <br />Erosion, sedimentation, and salt yield in the Greater Sagers Wash Watershed are primarily the <br />result of two processes; natural geologic erosion, and accelerated erosion. Natural geologic <br />erosion originates from naturally occurring Badlands and rock outcrop formations. (See Table <br /> <br />1 <br />