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<br />, <br /> <br />I <br /> <br />I' <br /> <br />,.' <br />'/ <br /> <br />co <br />C\J <br />''1' <br />(\J <br />t..:) <br />C;o <br /> <br />.' <br />~, <br /> <br />:;-~: <br /> <br />Evaluations of the technical risks for use of Lower Virgin River Unit water <br />vs. secondary sewage effluent showed that the plant design and operating un- <br />certainties were about equal In magnitude If water quality for the sources <br />were predictable. <br /> <br />.) <br /> <br />The total levellzed cost comparisons, based on appraisal-level accuracy and <br />economic factors suppl ied by Nevada Power Company, are shown on the following <br />bar graph. The comparisons show that Option I Is approximately equal to the <br />base case Option V, that Option II Is approximately $3.2 mil I Ion higher than <br />the base case, and that Option I I I Is approximately $5.5 mil I Ion higher than <br />the base case. Option IV, which uses brine concentrator product water rather <br />than softened cool ing tower ,blowdown for FGD system makeup, is $450,000 less <br />expensive than the base case Option V. <br /> <br />,~ . <br /> <br />,j.. <br /> <br />(;." <br /> <br />Economic sensitivity analysis, which examined the effects of varying chemical <br />cost, power cost and evaporation pond cost, showed that chemical cost was the <br />most slglnflcant economic variable. Of the five options, Option I and Option <br />IV were the least sensitive to chemical cost. While the sensitivity analyses <br />did not directly evaluate the Impact of variations of Lower Virgin River Unit <br />water quality on total level Ized cost, It Is apparent that total cost Is quite <br />sensitive to the predictability of water quality. <br /> <br />~; <br />.;.~( <br />:.., <br /> <br />, , <br />';>;1 <br />'.. <br /> <br /> <br />The in-plant cost of salt removal from the Colorado River system was deter-' <br />mined from the difference In levelized costs of Options I, II and III compared <br />to the base case, and the rate of Lower Virgin River water use. The levelized <br />cost of salt removal was $9 per ton per year for Option I, $66 dollars per ton <br />per year for Option I I, and $115 per ton per year for Option I I I. These In- <br />plant costs must be added to the levellzed costs of collecting and transport- <br />ing Lower Virgin River water to the Harry Allen site to determine the total <br />level Ized cost of salt removal. Collection and transportation costs have been <br />estimated separately by Reclamation. <br /> <br />, <br />,,', <br /> <br /> <br />;;:.," <br />t:~~ <br /> <br />The overal I results of the Task 4 study show that the Lower Virgin River Unit <br />water source Is a viable water supply for the Harry Allen Station, provided <br />the quality and quantity of the water supply are confirmed by additional wells <br />and monitoring. The evaluation of saline water use technologies and water <br />treatment process options showed that both emerging and commercially proven <br />power plant design approaches are available for using the Lower Virgin River <br />Unit water quality. <br /> <br />.'';''. <br />r.J <br />~ <br />. v': <br /> <br />-.; <br /> <br /> <br />The cost advantages of the Ion exchange/sldestream treatment process can be <br />Incorporated Into the Harry Allen Station design If the 'technical and economic <br />viability of the process can be confirmed through field demonstration. We <br />recommend that such a program be considered by Reclamation and Nevada Power <br />Company using the existing field test unit at Southern California Edison's <br />Etiwanda Generating Station near San Bernardino, California. <br /> <br />." <br /> <br /> <br />'';.'> <br />., <br /> <br />'~:.l <br />::: ,~ <br /> <br />iv <br /> <br />,::'C::.. <br /> <br />~:~~~; <br />~~ <br /> <br />',,1',,: <br />