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<br /> 9. <br />. .. <br /> .~ <br /> eo 10. <br /> = <br /> 11. <br /> <br />Programs in the Uintah Basin, Price-San Rafael rivers, Muddy Creek, and <br />Me Elmo Creek will basically consist of on-farm and lateral linings with <br />very little canal lining. <br /> <br />The use of canals for winter livestock water causes substantial salt <br />loading from several areas in the basin and contributes numerous local <br />waterlogging and soil salinaeion problems. <br /> <br />The barrier well network and Sublette Flat evaporation area as proposed <br />by the USDA, Soil Conservation Service, and minimal on-farm improvements <br />is the most cost-effective salinity program for the Big Sandy area in <br />Wyoming. The "buy-out" alternative as proposed by some local lando,",."ers <br />was evaluated and not found cost-effective. <br /> <br />Ii;. <br /> <br />12. Collection and reverse' osmosfsd'esal.inat'ion oJ a-gricultural return flows <br />should. be included as a viable salinity control alternative in dl irr1-" <br />gated areas. However. 'at cut't'ent estimil-ees .'O'f downstream" danlil'ges, .. '-.,. <br />desalination would not be implemented. <br /> <br />13. The by-pass alternative for the Paradox Valley was evaluated and found to <br />be more cost-effective than the proposed Radium evaporation pond alter- <br />native. This was primarily due to the greatly increased costs of evapor- <br />ation ponds. <br /> <br />14. The proposed desalination of the Glenwood-Dotsero Springs in Colorado was <br />evaluated in detail a. part of this study. It WaS concluded that the <br />most eoonomical alternative was .a primary reverse osmosispl"ntfcllowed. <br />by a much smaller secondary multi-stage flash distillation unit. How- <br />ever, at current average damage estimates, this project is marginally <br />feasible. <br /> <br />t';: <br />~\<:, <br /> <br />15. The use of average costs per .mg/l of treatment .is misleading and should <br />not be used in the delineation or phasing of salinity oontro~ projects. <br /> <br />16. At current average damage estimates, it is cost-effective t'o treat only <br />about 48 to 50 percent of the total attainable salt load reduction from <br />the projects designatad in PL 93-320. <br /> <br />17. All of this analysis points to the faot that the arbitra:rytarget of <br />maintaining 1972 salinity levels at Imperial Dam cannot be cost- <br />effeotivelyattained. In fact, these. results indicate that the target <br />level shoul<l be increased to about 1,030 or 1,040 mg/l or more. <br /> <br />18. Present trends indicate that all of the cost-effective salinity oontrol <br />programs should be on-line no later than 1995. The damage costs due to <br />delayed construction of these projects can be substantial. <br /> <br />19. Sensitivity analysis of the <lata and the optimization procedure indicate <br />that substantial error in costs and the respective salt load contribu- <br />tions of the individual alternatives ,",~uld have to ocour to change the <br />optimal order of implementation of a basin-wide salinity control program. <br /> <br />& <br /> <br />. <br /> <br />9 <br /> <br />~, lb. <br /> <br />... <br />.. <br /> <br />'. <br />