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<br />. <br /> <br />. <br /> <br />w <br />m <br />H:lo. <br />w <br /> <br />However, other strategies for salt load reduction may increase <br />consumptive uses, reducing the amount of water available for downstream <br />use. The most relevant example is consumptive industrial reuse wherein <br />heavy salt concentrations are not returned to the river while the waters <br />containing the salt are lost rather than being returned to the stream. <br />The extent of the net water loss will, naturally, depend on the extent <br />to which the heavily saline waters being reused substitute for evapora- <br />tive losses of higher quality water. <br /> <br />As long as the reused waters have a salinity concentration higher <br />than the river at the point of their return flow, consumptive reuse will <br />reduce the concentrations there and at some downstream points. Farther <br />downstream, if the river's salinity concentration increases to a level <br />greater than that of the water consumptively reused, the reuse will <br />cause an increase in downstream concentration of river salinity. <br />Whether or not the immediate beneficial effects of reuse on salinity <br />will offset the downstream losses from reduced water availability de- <br />pends on both the existing salinity levels (i.e., where we are on the <br />salinity-loss function) and on the marginal value (shadow price) of <br />water quantity. <br /> <br />Since both reduced concentration and water quantity loss (or <br />gain) are relevant, we will present estimates of the values related to <br />each. Regarding the benefits from concentration reduction, irrigation, <br />domestic, and industrial uses are all affected (although much more is <br />known about the effects on irrigated agriculture than about the other <br />activities). For each of these activities, the valuation of a reduction <br />in concentration is approached in a reverse fashion: by estimating the <br />damages from increases in the concentration. <br /> <br />The applicable measure of losses depends on how the affected <br />parties will respond to the increase. Each party has a variety of <br />possible responses, including doing nothing and accepting the consequent <br />losses; changing irrigation (or other water application) practices in <br />ways that reduce damages more than increasing costs; changing cropping <br />patterns; changing sources of water; treating the water, etc. The value \ <br />of damages associated_J1i--E.!L..!.~_.mo.!i..L?:,g'!{,,!!,t;ageous response is the value <br />tObe used_Cis thedi.rect benefit from a sa1.liiTtyconc:entrat1on ,reductio:':,. <br /> <br />We now review the important studies in the literature of salin- <br />ity damage and water value, leading up to the presentation of our best <br />current estimates of net benefits from salinity reduction. <br /> <br />Irrigation. Major concern over water quality in the Lower Colo- <br />rado River was first shown in the "Conference in the Matter of Pollution <br />of the Interstate Water of the Colorado River and Its Tributaries" held <br />in January, 1960 under the joint sponsorship of the riparian states and <br />the Federal Water Pollution Control Administration. The Colorado River <br /> <br />III-2 <br />