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Guide to COST-BENEFIT ANALYSIS of investment projects - Ramiri

Guide to COST-BENEFIT ANALYSIS of investment projects - Ramiri

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determine directly the willingness-<strong>to</strong>-pay. Other methods can be adopted, which may be found inliterature.b) Water supply <strong>projects</strong>, with the aim <strong>of</strong> protecting the resources <strong>of</strong> high quality and environmental value.Some <strong>projects</strong> aim at avoiding over-exploitation or some water sources and at identifying alternatives.An example is the replacement <strong>of</strong> water extracted from coastal aquifers, which have become salty due<strong>to</strong> pumping excessive volumes <strong>of</strong> resource, with water produced from other sources, such asdesalination, wastewater reuse, surface water sources, etc. The benefit (or non use value) is given bythe water preserved for other uses, current or future. The possible alternative uses <strong>of</strong> the saved waterhave <strong>to</strong> be accurately identified and, for each <strong>of</strong> them, the related potential demands quantified.When this is done, the benefits can be valued by means <strong>of</strong> water accounting prices as in the previouscase.c) The main benefit <strong>of</strong> the interventions aimed at limiting water leaks is the reduced volume <strong>of</strong> waterused for supplying the networks compared <strong>to</strong> an equal or greater quantity <strong>of</strong> distributed water.Examples are <strong>projects</strong> for network rehabilitation or, more in general, <strong>of</strong> ‘water asset management’. Asin the previous case, the benefit is given by the water preserved for other uses, <strong>to</strong> be quantified assaid above.d) For any intervention, that is intended <strong>to</strong> guarantee the availability <strong>of</strong> drinking resources in areas withsanitary problems, and where water sources are polluted, the benefit may be directly estimated byvaluing the deaths and illnesses that can be avoided by means <strong>of</strong> an efficient water supply service. Tomake an economic valuation, it is necessary <strong>to</strong> refer on one hand (illnesses) <strong>to</strong> the <strong>to</strong>tal cost <strong>of</strong>hospital or out-patient treatments and <strong>to</strong> the income loss due <strong>to</strong> possible absence from work, and onthe other hand (deaths) <strong>to</strong> the statistical life value quantified on the basis <strong>of</strong> the average income andresidual life expectancy or with other methods.e) The social benefits <strong>of</strong> sewer and depura<strong>to</strong>r <strong>projects</strong> may be evaluated on the basis <strong>of</strong> the potentialdemand for sewage, that will be fulfilled by the <strong>investment</strong> and estimated according <strong>to</strong> an adequateaccounting price 34 . Alternatively, if possible, direct valuation may be applied <strong>to</strong> benefits such as:- The value <strong>of</strong> the illnesses and deaths avoided thanks <strong>to</strong> an efficient drains service (see above);- The value derived from preserving or improving the quality <strong>of</strong> the water bodies or the lands inwhich the waste water discharges and the related environment. This value is made up <strong>of</strong> both ‘use’and ‘non-use’ values (see the diagram below).f) For ‘white’ or mixed drains <strong>projects</strong>, the benefit is the damage avoided <strong>to</strong> land, real estate and otherstructures due <strong>to</strong> potential flooding or unregulated rainwater, valorised on the basis <strong>of</strong> the costs forrecovery and maintenance (avoided costs).In any case, if no standard economic appraisal method is applicable for the specific project, it is possible<strong>to</strong> resort <strong>to</strong> comparisons with any similar project, that may have been developed in a context as close aspossible <strong>to</strong> the one in the affected area. Obviously, in the case <strong>of</strong> <strong>projects</strong> that have multiple objectivesand, therefore, derive from a combination <strong>of</strong> two or more <strong>of</strong> the categories above, the benefits are givenby a proper combination <strong>of</strong> those described above.For any project, the positive or negative externalities due <strong>to</strong> the impact <strong>of</strong> the infrastructure’s constructionand the use <strong>of</strong> the water resources, have <strong>to</strong> be carefully taken in<strong>to</strong> account, as far as possible, by means <strong>of</strong>a quantitative approach. Various methods exist for the valuation <strong>of</strong> environmental costs and benefits andthese can be found in the literature (see Annex F) 35 .As mentioned in Chapter 2, taxes and subsidies should usually be treated as transfers within society andshould therefore be excluded from the estimation <strong>of</strong> economic costs. However, in the water service34Basically the same as the demand for water, applying an appropriate reduction fac<strong>to</strong>r <strong>of</strong> the flow rates waste water discharged in the seweragenetwork (as an as an example from literature: 0,8).35See, as example, Pearce D., Atkinson G. and Moura<strong>to</strong> S. ‘Cost-Benefit Analysis and the Environment: Recent Developments’ (2005).100

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