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<br />EFFECTS OF WATER QUALITY ON WATER USERS 13 <br /> <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 salts from efflorescence at the alluvium- <br />bedrock contacts[12]. <br /> <br />The soluble mineral content of saline formations <br />is variable and can be significantly different <br />within one stratigraphic unit. The <br />determination of the soluble mineral content of <br />surficial soils is highly dependent upon the <br />sampling and analytical methods used. The <br />effects of contact time and sediment to water <br />ratios on rate and extent of dissolution are <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[15] recommends a sediment to water <br />ratio of 1 percent. This ratio allows for greater <br />dissolution of salts and a better estimate of <br />salinity contributed from erosion. <br /> <br />EFFECTS OF WATER QUALITY <br />ON WATER USERS <br /> <br />Economic <br /> <br />Estimating Economic Impacts of Salinity of the <br />Colorado River[16] updated the economic <br />impacts of salinity in the Colorado River Basin <br />and developed a method of forecasting economic <br />impacts as salinity levels rise and water use <br />changes in the future. The first objective ofthe <br />study was to update, revise, clarify, and refine <br />the estimates of economic damages from salinity <br />that had been described in earlier studies [17,18] . <br />Figure 4 shows the relative impact of salinity on <br />water users in the Lower Colorado River Basin. <br />The study estimated damages were $311 million <br />per year based on existing water quality levels <br />and water uses in the Lower Basin. <br /> <br />The second objective of the study was to provide <br />a better means of estimating present and future <br />salinity damages through the development of a <br />comprehensive computer program. Present <br />damages were estimated by the study to be <br />$311 million per year, but as salinity levels <br /> <br /> <br />Crop (36%) <br /> <br />Management (11%) <br /> <br />Household (50%) <br /> <br />Figure 4.-Salinity damages and costs. <br /> <br />increase to more normal levels, damages <br />(figure 5) will also increase. Sensitivity <br />analysis[19] using the damage model showed <br />that damages (or the value of salinity control) <br />increases with salinity. At the salinity <br />standards (879 mg/L at Imperial Dam), damages <br />are projected to exceed $1 billion per year. <br />Using a relatively conservative analysis, the <br />benefit of salinity control was estimated to be <br />$257 per ton (1986 dollar value). In comparison, <br />the cost of salinity control generally ranges from <br />$20 to $100 per ton. <br /> <br />$2,000 <br /> <br />$1,500 <br /> <br />Numeric Crheria <br />of the SaHnIty Standard <br /> <br />879 mgll. <br /> <br /> <br />Ul <br />Q) <br />C> <br />OS <br />E <br />OS <br />o <br />~ <br />:~ <br />OJ <br />CIl <br /> <br />'" <br />c: <br />~ <br />:E <br /> <br />$1,000 <br /> <br />$500 <br /> <br />$0 <br /> <br />400 500 600 700 800 900 1000 1100 <br /> <br />Salinity at Imperial Dam (mglL) <br /> <br />Figure 5.-Salinity damage curve. <br />