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<br />.r.::. <br />o <br />0) <br />00 <br /> <br />regulation depend, as stated previously, on the elasticity of de.mand <br /> <br />for water and the output as a given activity. If the elasticity of de- <br /> <br />mand or the input is low, either because water use has a low cost rel- <br /> <br />ative to total production costs or because few substitutes exist, activity <br /> <br />reduction as a result of pollution control may be minimal (until a point <br /> <br />at which the input cost becomes a substantial portion of total cost or <br /> <br />p;roduction results in losses.). If that elasticity is relatively high, <br /> <br />either because water is a substantial portion of input costfil or substi- <br /> <br />tutes for water are readily available, activity and, water use may change <br /> <br />dramatically with the application of small increments of regulation or <br /> <br />economic disincentives. <br /> <br />If the elasticity of demand for the product is low, then more of <br /> <br />the additional costs will be passed on to consumers (that is TWP curve <br /> <br />will not exhibit sharply diminishing slope). Producers would be ex- <br /> <br />pected to ~educe output only slightly. If that elasticity is high, then <br /> <br />much of the additional cost will be borne by the producer andproduc- <br /> <br />tion will be reduced substantially. <br /> <br />]'>ublic Investment in Treatment Facilities <br /> <br />In areas in which public investment in either treatment facilities <br /> <br />or in other pollution removal technology is undertaken, user activity <br /> <br />changes will depend on how the investment and operation costs are <br /> <br />distributed. If the investment and operation cost is financed from user <br /> <br />fees related directly to water use, reduction in activity may be expected, <br /> <br />30 <br /> <br />. <br /> <br />. <br /> <br />. <br /> <br />. <br /> <br />. <br /> <br />. <br /> <br />. <br /> <br />. <br /> <br />. <br /> <br />. <br /> <br />. <br />