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<br />N <br />I- <br />tC <br />fv <br /> <br />channel are similar to those found in the <br />surrounding watershed soils. <br /> <br />Sediment and the resulting salt yield is highly <br />dependent upon landfonn type. Three mtijor <br />landform types-badlands, pediments, and <br />alluvialval1eya--sre associated with the Mancos <br />Shale terrain. <br /> <br />Badlands Bre the most erosionally unstable, <br />with sediment yields as high as 15 tons per acre <br />[21]. Rilling accounts for approximately 80 <br />percent of the erosion [20]. Because sslt <br />production is closely related to sediment yield <br />and the badland soils have not been leached of <br />their S<lluble minerals, they produce the greatest <br />amount of salt of the landform types. <br /> <br />Pediments are gently inclined planate erosion <br />surface carved in bedrock and generally <br />veneered with fluvial gravels. The surface <br />slopes of pediments Bre gentle, making them <br />relatively stable. Pediments have deeper soils <br />and higher infiltration rates than badlands, thus <br />they support a greater vegetation cover and are <br />less erosive. <br /> <br />Alluvial valleys are formed by a change in <br />gradient and the deposition of sediment. They <br />are stable except along the channel where <br />headcutting and gullying occur. Most of the <br />salts have been leached from the alluvial <br />deposits, thus erosion of their landform type <br />yields less salts per unit volume of sediment <br />than the other two landform types. However, <br />channels incised into alluvium incorporate both <br />sediment and salt from sloughed channel backs <br />and salta from efflorescence at the <br />alluvium-bedrock contacts (19J. <br /> <br />The soluble mineral content of saline formations <br />is variable and can be significantly different <br />within one stratigraphic unit. The variability is <br />a result of the parent material, topography, <br />microclimate, and leaching. A3 a result, the <br />salts contributed from any stratigraphic unit are <br />very site specific. <br /> <br />The determination of the soluble mineral contact <br />of surficial soils is highly dependent upon the <br />sampling and anal)tical methods used. The <br />effects of contact time and sediment to water <br />ratios on rate and extent of dissolution are <br /> <br />FACTORS IN SAUNfTY TRENDS 2S <br /> <br />extremely important Since much of the salt is <br />dependent upon sediment load, contact time and <br />sediment to water ratio must be considered. <br />Laronne {22] recommends a sediment to water <br />ratio of 1 to 99. This ratio allows for greater <br />dissolution of salts and a better estimate of <br />salinity being contributed from erosion. <br /> <br />Geochemistry <br /> <br />Dissolution of effiorescence on the surface or <br />minerals in subsurface formations is a major <br />source of salinity. Runofffrom snowmelt and <br />thunderstorms, which causes alluvial, bank, and <br />gully erosion, suspends solids from barren <br />marine shales. The increased concentrations of <br />calcium, magnesium, and sulfate in these waters <br />are due to dissolution of gypsum {calcium <br />sulfate) and dolomite (calcium or magnesium <br />carbonate). Much of the sodium is contributed <br />by exchange of calcium for sodium on clays <br />found in saline marine shales. <br /> <br />Point SOurces of salinity contribute chemical <br />constituents that reflect the mineralogy and the <br />chemical reactions which occur in the rock <br />formations through which the ground waters <br />flow. Natural springs are composed of waters <br />whose subsurface flow paths are ofWn deep, and <br />movement of the water is relatively slow. <br />Therefore, salinity can be very high, often <br />exceeding 10,000 mgIL. Such spring waters vary <br />in composition in the basin. The waters of <br />highest salinity are of sodium chloride character <br />due to highly soluble halite. Other springs are <br />high in concentrations of calcium and sulfate <br />due to contact with gypsum (hydrated calcium <br />sulfate). <br /> <br />The water quality of many seeps throughout the <br />Colorado River Basin ofWn reflects relatively <br />shallow geology and mineralogy. Sodium, <br />calcium, and sulfate concentrations can be fairly <br />high (4,000 to 10,000 mg/L). The chemical <br />makeup is due to a variety of reactions, <br />including dissolution of gypsum, partial <br />precipitation of carbonate minerals, and <br />adsorption of calcium onto clays that have high <br />amounts of exchangeable sodium and <br />magnesium. <br />