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<br />fluence evaluation of flood control proposals. The <br />effect of these factors is to bias a group for or againsl <br />flood conlrol proposals and establish a general under- <br />lying lendency to approve or reject them. If the atti- <br />tude were negative a proposal would have to overcome <br />this generalized conditioned response, or attitude, or <br />be rejected. If for example, people with urban back- <br />grounds, or home ownership, or some other character. <br />istic were likely 10 approve a flood control proposal <br />withoul specific knowledge about ii, this lendency or <br />predisposition would be an example of a biasing fac- <br />tor. Such a factor may have a separate effect and also <br />be usefui in an Acceptance Funclion. For instance, <br />two variables used in Ihis study were experience with <br />flooding and proximity of flood experience 10 presenl <br />residence. Either of these may cause a tendency for <br />favoring control measures and may alter the respon- <br />denis' perception of the effectiveness of a particular <br />flood control method. <br /> <br />The relative importance of eilher of Ihese two <br />variables may also depend on the evaluation judge's <br />knowledge of the proposal. For example, a person <br />who lends to be in favor of flood control because he <br />perceived a need may reject a parlicular proposal <br />when he learns that it is less efficient than another <br />method. A "labeling" phenonemon, or conditioned <br />response to a symbol, may occur because of the name <br />"flood control." This type of response may be re- <br />moved with sufficient knowledge. 6 <br /> <br />The evaluation of a flood control proposal is <br />determined by adding the effect of predisposing char- <br />acteristics and the Acceptance Functions discussed in <br />Ihe preceding section 7 as shown in Figure 4.4. This <br />diagram illustrates the conceptualization behind the <br />equation applied to every agency and the public in <br />the model. <br /> <br />For example, suppose a project would actually <br />cost $3,000,000 and add a tax of $150 per taxpayer <br />in the affecled area. The perceived cost by members <br />of the population, however, would not necessarily be <br />this dollar cost; in fact, Ihe perceived cost may nol be <br />in dollars9 The perceived cost would be "high" to <br />"low" depending on a person's circumstances and back- <br />ground. What is considered "low" by one group may <br />be considered "high" by anolher. The perceived char- <br /> <br />6The idea of "labeling" and its dynamics is interesting <br />in itself. A label may have meaning so long as the person <br />judging does not have reason to doubt the validity of the <br />label. <br />7The weightings of each term, factor, or Acceptance <br />Function is done by Uge of regression analysis. <br />8The perceived cost could accurately be expressed in <br />dollars only if the dollar figures used were proportionate to <br />the meanings which the costs have to all respondents. It would <br />be easier to use a scale directly measuring this "perceived cost:" <br />in non-monetary units. <br /> <br />acteristics were measured by scales of "low" to "high" <br />in calibrating the main equation developed in this re- <br />port. <br /> <br />The Distortion Factors in Figure 4.4 reflect the <br />differences between the designed characteristics of a <br />proposal and the perceived characterislics. The agen- <br />cy perceptions are assumed 10 be the same as Ihose <br />of the designer because of information exchange dur- <br />ing the design of a proposal. Distortion Factors <br />should perhaps be used to account for I)-an agency's <br />perception of other agency's proposals, and 2) Ihe <br />public's evaluation of a flood control proposal, but <br />this is not done in the present model. Since the pub- <br />lic's perceplion of flood control proposal characteris- <br />tics was directly measured, any distortion is already <br />included. The assumption that the agency opinion is <br />correctly perceived is justified on Ihe basis of the pub- <br />licily given to flood.control decisions by an agency. <br /> <br />The variables shown in Figure 4.4 are not ex- <br />haustive. Other consigerations such as safety and <br />generality of benefit may be included (see Andrews, <br />and Geertsen, 1974a: 33-35). Also effecls on num- <br />erous "other groups" may be usefully represented in <br />the model. Acceptance Functions for other groups <br />affecled can be as many as there are groups whose <br />opinions are significant. The model can be expanded <br />by repeated applicalion of the basic equation based <br />on this conceptualization of the decision process with <br />groups being connected to each other through Accepl- <br />ance Functions of this last type. The model can be <br />made as complicated as desired by adding more inter- <br />actions as they are observed. <br /> <br />Special Interest Group Functions <br /> <br />In applying the equalions based on the concep- <br />tualization of the decision process shown in Figure <br />4.4, a problem develops in that the results predict the <br />average attitude of the public, and people in unusual <br />situations have a disproportionate influence on the <br />outcome of the total process. Special interest groups <br />act 10 block or promote changes. They are vocal and <br />may be influential. <br /> <br />Expa1l8ion Effect <br /> <br />A concern or value is latent and unimportant <br />until it is threatened, when its imporlance is suddenly <br />expanded. When this vaiue becomes a group concern, <br />whether by an existing group or one newly organized, <br />its public role is expanded greatly. The resulting "ex- <br />pansion effect 11 is psychological, cognitive, and emo- <br />tional and often becomes a "cause" for a specialinter- <br />est group. This latent-expansion phenomena needs to <br />be identified and represented in a social system for <br />decision-making. In an ecological special interest <br />group, for example, potential effects on an ecological <br /> <br />S3 <br />