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<br />through time or during the process of project deter- <br />mination. It is true, however, that in order to predict <br />the results at the end of the evaluation process, some <br />way of predicting values al that point must be used; <br />this is ideally done by Ihe use of dynamic equalions <br />for Ihe variables2 or by the assumption Ihat the values <br />of relevant variables will remain the same or change <br />in a predetermined way.3 <br /> <br />The blocks on the right of Figure 5.1 identify <br />specific equations which are used in the model. These <br />equations are developed later in this chapler. As in- <br />dicated by the equalion numbers within Ihe blocks, <br />the same equation may be used in two steps in some <br />inslances (see blocks 4 and 6 and 7 and 8). This means <br />lhat values for an agency in one of these steps were <br />also used later. In the evenl that a social occurrence <br />(such as Ihe ecology movemenl) alters basic public <br />values, Ihe equations would need 10 be recalibrated. <br />Allwo points in the flow chart (blocks 5 and 12) the <br />user of Ihe model must provide values for the para- <br />melers Ip depicllocal conditions. <br /> <br />The decision agency decides that a plan is need- <br />ed and asks the planning agency for a plan or for al- <br />lemate plans.4 Plans are then formulated by the plan- <br />ning agency and a decision made as to whether it is <br />feasible. If so, Ihe planning agency would forward it <br />on to the decision agency. <br /> <br />Equation I (5.4) and Equation 11 (5.6) and IF <br />statement A (5.7) are the only mathematical formu- <br />las used in Ihe model that are nol applications of the <br />basic conceptual equation of the decision process of <br />a group regarding a flood control proposal. <br /> <br />Detailed Development of the <br />Mathematical Model <br /> <br />Concepts in Formulalions of the <br />Mathematical Model <br /> <br />The mathemalical model of Ihe institutional <br />response to flood problems was formulated in terms <br /> <br />2A basic need expressed in Chapter VIII is to develop <br />equations for the perceived characteristics of proposals. <br /> <br />3 An analysis of the measured variables may indicate <br />which variables would have to change in value in order to <br />alter the results of a decision process or if change is even possi. <br />ble. <br /> <br />4Almost any plan could be submitted by the planning <br />agency for evaluation in the model. The computer program <br />could be modified so that the highest positively rated plan <br />would be submitted Illst. If this plan were rejected subse- <br />quently, the second highest rated plan could be submitted, <br />and so on. Also, the system could be established so that plans <br />are submitted in order of priority so long as a constraint is <br />not exceeded. An example would be a financial limitation, <br />in which case alternate plans would be submitted so long as <br />the total costs does not exceed a specified amount. <br /> <br />of representing Ihe interaction of four principal types <br />of components. They are: <br />I. Social characlerislics of the general public <br />and other populations (including organized <br />interesl groups) in the area concerned. <br />2. Agency characleristics of both aclion and <br />planning agencies.5 <br />3. Physical characteristics of the proposed flood <br />conlrol melhods. <br />4. Hydrologic system characteristics. <br /> <br />The first two sels of characteristics are essentially <br />social, and Ihe second two are essentially physical. In. <br />leractions within and between subsets need to be de- <br />fmed and represenled in order 10 model the sociologic <br />response to hydrologic problems. <br /> <br />A linear form of relationships within the model <br />is generally easier to work with, therefore, it is desir- <br />able to use a linear model. However, appropriate <br />limits of applicability need to be set (Narayana et aI., <br />1970). <br /> <br />Equations representing a subsystem can be cali- <br />braled using measurements of the perlinent variables. <br />Five major variables selected from previous tests to <br />be significant in the initial selection of a proposed pro- <br />ject plan are: <br />I. Flood control abiiity. <br />2. Cost per capita. <br />3. Oul.door aeslhelics provided or destroyed. <br />4. Recreation provided or deslroyed. <br />5. Ecological impact (disturbance or improve- <br />menl of natural conditions). <br /> <br />Values for these five variables are used by the com- <br />puter model to determine the acceptability of a possi- <br />ble plan. The variables in the equations (i.e., the sets <br />of characteristics) need to be operalionally deflned <br />for alternative flood conlrol proposals to be compared <br />on the same basis. A melhod was developed for assign- <br />ing numerical values to the perceived significant char~ <br />acteristics of flood control proposals and of pertinenl <br />social groups to form scales thai may be treated as <br />interval or ratio data, a necessary level of measure- <br />ment for modeling purposes.6 <br /> <br />As consistent measures are established, they can <br />be used in regression analysis to predict effects from <br />causes. Coefficients for the equations can be deter- <br /> <br />SThe planning and action agencies may be the same. <br />The categories of characteristics for the various types of agen- <br />cies involved will be largely the same, but appropriate values <br />of these characteristics need to be determined. <br />60rdinal data with a reasonably large number of res- <br />ponse categories over the range of the variable may be treated <br />as interval data with approximately correct results (Labovitz, <br />1970, Baker et al., 1971). <br /> <br />S9 <br />