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<br />, <br /> <br />. <br /> <br /> <br />j <br /> <br />. <br /> <br />~ <br /> <br />'. <br /> <br />.. <br />. <br /> <br />-. <br />i; <br /> <br />.'?. <br /> <br />~,~ <> <br /> <br />~ <br />tv <br />...... <br />en <br /> <br />SECTION 6 <br /> <br />METHOD OF ANALYSIS <br /> <br />The research approach c1eveloped for this work consistecl of four phases: <br /> <br />1, Development of a cost-effectiveness anelysis applicable to the <br />salinity control problem in the Upper Coloraclo River Basin; <br /> <br />2. <br /> <br />Evaluation of salinity sources in the basin; <br /> <br />3. Selecting an array of salinity control alternatives; and <br /> <br />4. <br /> <br />Application of the anslytical proceclure to the Upper Basin c.ondi- <br />t ions. <br /> <br />The fourth phase is encompassed in the following section. The seconcl phase <br />was describecl in genersl terms in Section 5 and will be ~~panclecl somewhat in <br />this section. <br /> <br />COST-EFFECTIVENESS A.~LYSIS <br /> <br />The method of salinity control program analysis was originally developecl <br />in a study of water quality improvement alternatives in the Utah Lake drainage <br />area in central Utah (Walker et al., 1973). The approach involved decomposing <br />a basin-wicle prOblem into first hyclrologic subbasin problems and from there <br />into technological subunits. The principal assumption in the c1ecomposition <br />.was that by evaluating net mass emission of salts from each subbasin, the <br />problem consists of mutually exclusive components that coulcl..be aclded .together <br />in arriving at the basin-wide optimal program. This assumption implies physi- <br />cally thst: (1) water utilization at one location is not significantly <br />affectecl by a change in water use practices elsewhere; and (2) salinity is a . <br />completely conservative pollutant. Walker and Skogerboe (1980) c1iscuss the <br />physical assumptions and show mathematically the relationship between the <br />physical system and these assumptions. <br /> <br />A schematic view of the conceptual model is given in Figure 15. G,alker, <br />1978). The basic structure of the model is a function relating the cost of <br />s,a11n:lty control and the effectivenes:3 or the investment in terms of reducing <br />mass emission (Mgm/yr). Associatecl with each cost-effectiveness function are <br />inclicatio s of how much of the cost ancl effectiveness is allocated to each <br />alternative encompassed in the optimi~ation. Examination of Figure 15 in some <br />detail will serve to illustrate the additive construction of the overall <br />optimal strategy. <br /> <br />39 <br /> <br />~ <br />t' <br /> <br />, <br />, <br /> <br />" <br /> <br />.' <br /> <br />-. .. ~ ',' <br /> <br />. .~ . <br /> <br />.,' <br /> <br />J <br />