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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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LEGISLATIVE FRAMEWORKWater use framework- European Parliament and Council Directive 2000/60/EC establishing a framework for Community action in the field <strong>of</strong>water policyWater and water ambient protection- Consequent <strong>to</strong> the Water Framework Directive- Directive about the bathing water quality (European Parliament and Council Directive 2006/7/EC)- Directive dealing with the protection <strong>of</strong> groundwater against pollution and deterioration (European Parliament and CouncilDirective 2006/118/EC)Other Directives- Council Directive 1976/464/EEC on pollution caused by certain dangerous substances discharged in<strong>to</strong> the aquaticenvironment- Council Directive 1991/676/EEC <strong>of</strong> 12 December 1991 concerning the protection <strong>of</strong> waters against pollution caused bynitrates from agricultural sourcesSpecific water and waste water- Council Directive 1998/83/EC regulating the quality <strong>of</strong> water <strong>to</strong> be used for human consumption,- Council Directive 1991/271/EEC concerning urban waste-water treatmentThe main objective <strong>of</strong> the Water Framework Directive is <strong>to</strong> achieve good water status for all waters by2015. The Directive, therefore, pursues protection <strong>of</strong> all water bodies, including inland surface waters,transitional waters, coastal waters and groundwater.Even if activities <strong>to</strong> implement the Water Framework Directive are now under way in Member States andEuropean countries under a common implementation strategy 22 , the main principles, that are relevant forthe water project analysis, can be clearly outlined:- integrating the management <strong>of</strong> water resources on a river district scale. The ‘river basin district’ is theadministrative and terri<strong>to</strong>rial unit basis for the management <strong>of</strong> water from all points <strong>of</strong> view and isdefined as a set <strong>of</strong> terrestrial and marine areas, which include one or more neighbouring basins;- economics integrated in<strong>to</strong> the management <strong>of</strong> the water services. The Water Framework Directiveclearly integrates economics in<strong>to</strong> water management and water policy decision-making. To achieve itsenvironmental objectives and promote integrated river basin management, the Directive calls for theapplication <strong>of</strong> economic principles (e.g. water pricing). The Directive requires an economic analysis <strong>of</strong>the different uses <strong>of</strong> resources and water services 23 ;- the <strong>to</strong>tal cost recovery: the tariff policies for attaining the goal <strong>of</strong> economically and environmentallysustainable use <strong>of</strong> water resources, must take in<strong>to</strong> account the ‘<strong>to</strong>tal water costs’:♦ financial costs: these are the costs <strong>of</strong> providing and administering water services, namely operatingcosts, and maintenance costs <strong>of</strong> capital for the renewal <strong>of</strong> equipment and new plants (capital andinterests and the possible return on equity);♦ environmental costs: these are related <strong>to</strong> damage <strong>to</strong> the environment, and <strong>to</strong> those who use it,caused by the environmental impact <strong>of</strong> the construction <strong>of</strong> the project infrastructures and by thesubsequent use <strong>of</strong> the water;♦ resource costs: these represent the costs <strong>of</strong> foregone opportunities that other users suffer due <strong>to</strong>the depletion <strong>of</strong> the resource beyond its natural rate <strong>of</strong> recharge or recovery (e.g. costs related <strong>to</strong>groundwater over-abstraction). These users can be either those <strong>of</strong> <strong>to</strong>day, or those <strong>of</strong> <strong>to</strong>morrow,who will also suffer if water resources are depleted in the future. In principle, the goal <strong>of</strong> making22See: European Commission, Common Implementation Strategy for the Water Framework Directive, Guidance Document No 1 ‘Economicsand the Environment – The Implementation Challenge <strong>of</strong> the Water Framework Directive’ produced by Working Group 2.6 – WATECO, 2003.23The main features <strong>of</strong> the economic analysis can be summarised as follows (see also WATECO 2003): <strong>to</strong> carry out an economic analysis <strong>of</strong>water uses in each River Basin District; <strong>to</strong> assess the ‘<strong>to</strong>tal water costs’ and <strong>to</strong> assess current levels <strong>of</strong> cost-recovery; <strong>to</strong> assess trends in watersupply, water demand and <strong>investment</strong>s; <strong>to</strong> identify areas designated for the protection <strong>of</strong> economically significant aquatic species and <strong>to</strong> designateheavily modified water bodies based on the assessment <strong>of</strong> changes <strong>to</strong> such water bodies and <strong>of</strong> the impact (including economic impact); <strong>to</strong>support the selection <strong>of</strong> a programme <strong>of</strong> measures for each river basin district on the basis <strong>of</strong> cost-effectiveness criteria and <strong>to</strong> define theimplications <strong>of</strong> the programmes for cost-recovery; <strong>to</strong> estimate the need for potential (time and objective) derogation from the Directive’sobjectives based on an assessment <strong>of</strong> the costs and benefits and <strong>of</strong> the costs <strong>of</strong> alternatives for providing the same objective.92

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