• Aucun résultat trouvé

A ssessment of costs

N/A
N/A
Protected

Academic year: 2022

Partager "A ssessment of costs"

Copied!
2
0
0

Texte intégral

(1)

T

he 172-page document continues theKnowledge for actionseries of books that provides professionals in the water and aquatic-environment sector (scientists, engineers, water managers, instructors, students, etc.) with information on recent research and science-advice work.

The book is available on the Onema site (www.onema.fr), in the Resources section, and at the national portal for

"Water technical documents"

(www.documentation.eaufrance.fr).

Contact: veronique.barre@onema

Translation:Bartsch&Cie Graphicdesign:BéatriceSaurel Printedby:CFI-2013 Photo credits:

M. Bramard - M.Carrouee - C. Forst - V. Marty - C. Roussel - M. Salvetti - F. Weingertner.

O

ver the past 15 years, economic assessment has come to play an increasingly important role in water management. Environmental economic

assessment, which is more social-economic than financial in nature,

consists of analysing all the activities of economic agents (individuals, the State, companies, non-profit organisations, etc.) and their effects on society and the environment in order

to determine the quantitative and qualitative consequences,

both positive and negative.

The use of economic assessments for water management was significantly boosted by the launch of the European

water framework directive (WFD) in December 2000 and by the progressive development of sub-basin management

plans (SBMP) in France.

W

hether the goal is to characterise in social-economic terms how water is used in a given area or to assess the costs and environmental impacts of a programme of measures or a project, economic analysis is now an integral part of the preparatory and formulation processes of public policy.

Whatever the size of the project, cost-recovery analysis, cost-effectiveness analysis and cost-benefit analysis are all assessment techniques that water specialists must use to comply with regulations and implement water-management policy in their area.

The bookEconomic analysis for management of water and aquatic environments presents definitions, information and a discussion on the economic-analysis techniques used to manage water and aquatic environments. The goal is to assist in the operational implementation of economic analysis. This document briefly outlines the contents of the book.

Maria Salvetti

1 Analysis of water uses, impacts and pressures

Identification of potential measures

Justification of potential exemptions

Formulation of programmes of measures Implementation of

programmes of measures and incentive pricing

Assessment of the impacts of programmes

of measures

Economic characterisation of water uses Assessment of cost recovery

Justification of exemptions - disproportionate costs Costing of programmes

of measures Assessment of the

cost-effectiveness of measures

(2)

A ssessment of costs

The first step in assessing the costs of a project or programme is to precisely list all the costs that must be taken into account and quantified. Frequently, it is also necessary to determine the unit costs and the extent of the planned measures in order to calculate the total implementation cost of the project or programme. This type of cost assessment is often used in more elaborate economic analyses such as cost-effectiveness, cost-benefit and cost-recovery analyses. Most standard, economic analyses take into account the production costs and the economic costs of a project or measure.

Social-economic and environmental assessments attempt to determine the total cost.

A ssessment of environmental impacts

Once the costs of project implementation have been calculated, it is often necessary to estimate the environmental impacts of the project. This consists of identifying the environ- mental benefits and damages incurred by the project or measure. The point of the assessment of these impacts is to inform on the economic, social and environmental effects caused by the project or measure.

An economic assessment indicating the value of an environmental good is based primarily on methods linking a value expressed in monetary terms (euros, dollars, etc.) with changes in the environmental status. The process of monetising does not mean that the environ- mental good, in this case the aquatic environment, becomes a marketable item that can be freely purchased or exploited. It provides a quantified assessment that can then be compared to economic values more commonly used in analysis such as costs and available budgets.

A number of different approaches to the economic assessment of environmental goods have been devised. Each sheds light on a particular aspect and is selected depending on the value to be calculated. For example, to determine market or option values, cost-based methods are employed. To calculate non market-related use values, revealed-preference methods are used. Finally, non-use values can be measured by stated-preference methods.

C ost recovery

The concept of cost recovery is explicitly mentioned in the European water framework directive (WFD). Cost-recovery analysis must be carried out in the process of drafting the characterisation report for each river-basin district. A more simplified form of the analysis may also be carried out for an SBMP. The results can serve as true decision-aid tools in that they facilitate debate and inform on the economic issues in the area covered by the SBMP.

Cost-recovery calculations consist of identifying and estimating all the economic flows resulting from the services pertaining to water use. The objective being that water users cover the costs incurred by their use of water as much as possible, primarily through the price paid for water. The analysis must therefore indicate the degree to which each category of water-service users in fact pays for the water it consumes and discharges.

D isproportionate costs

The European water framework directive requires that the Member States reach environ- mental objectives for the status of all water bodies in the major river basins by 2015. The concept of disproportionate cost is used to justify exemptions in terms of deadlines or of the final status. It is therefore an important component in the formulation and planning of programmes of measures.

However, the WFD did not indicate precisely just what the concept of disproportionate costs means and covers. Each Member State has attempted to better understand and more precisely define the concept by tracing its general outline and meaning, and by proposing the necessary economic-analysis methods. The approaches developed in France and the U.K. are presented and contrasted here.

2 3 4

Environmental externalities Economic externalities Opportunity costs

Capital costs Operating and

maintenance costs Totalcost

Economiccosts

Productioncosts

C haracterisation of water uses

Before launching economic studies to assess the consequences of a project or measure, it is first necessary to list the existing water uses in the given area.

Characterisation of water uses is the term commonly employed for this description of water uses lying at the crossroads between economics and the natural environment.

An economic characterisation of water uses consists of estimating the importance of water in the economy and the social-economic development of the studied river basin.

The analysis must identify the significant water uses and study the basin dynamics in order to contribute to the formulation of a base scenario.

It must also attempt to foresee any changes in the main economic and human activities that could impact on pressures and water quality. Study must be devoted to the probable changes in the main social-economic parameters such as the local policies implemented, growth rates of the main economic sectors, investments in the water sector, local population dynamics, etc.

The listing of water uses in the area serves to integrate the local social-economic environment and the local water-management issues in the analysis. All the above elements are important factors in the discussions concerning action programmes and measures.

Market value Option value Non-market value

Cost-based methods

Revealed-preference methods

Stated-preference methods Non-use values

Références

Documents relatifs

The higher-order flow losses can include decline in investments not related to drought mitigation, drop in national income, opportunity costs of drought-related budget

“A Treatise on Horses Entitled Saloter or, a Complete System of Indian Farriery”. 17 Bearing the title Sha li ho tra’i mdo’i gnas las rta’i rigs bzhi, chapter eight

It is the stake of the case of study presented here: we will see how the project evolved in the direction of a better urban integration and especially how the actors of the

This last step does NOT require that all indicator be converted - best if only a small percent need to be reacted to make the change visible.. Note the

True 4- Karim buys milk from the super market... B/ Complete the table:

Yet, it shares one key character with other scyllarids that Cancrinos claviger is lacking: the non-separation of the proximal elements of the petaloid region of the antenna

Complementarity among farms represents a lever to increase protein self-sufficiency at regional level through local exchanges Local exchanges of organic fertilisers and crops

L’archive ouverte pluridisciplinaire HAL, est destinée au dépôt et à la diffusion de documents scientifiques de niveau recherche, publiés ou non, émanant des