Chanel

Publications

How to correctly assess mortality benefits in public policiesJournal articleOlivier Chanel, Pascale Scapecchi and Jean-Christophe Vergnaud, Journal of Environmental Planning and Management, Volume 49, Issue 5, pp. 759-776, 2006

This paper concerns the difficulty of taking long-term effects on health into account in an economic valuation. Indeed, public decision makers should incorporate the cessation lag between implementation of an abatement policy and achievement of all of the expected mortality-related benefits for any projects involving health impacts. This paper shows how this time lag problem can be handled by proposing two approaches—either in terms of deaths avoided or of life years saved—within a dynamic perspective. The main findings are that long-term health benefits calculated by standard methods and widely applied to adverse health effects should be corrected downwards when incorporated into an economic analysis. The magnitude of correction depends on the discount rate, on technical choices dealing with epidemiology and on the method chosen to assess mortality benefits.

Does public opinion influence willingness-to-pay? Evidence from the fieldJournal articleOlivier Chanel, Susan Cleary and Stéphane Luchini, Applied Economics Letters, Volume 13, Issue 13, pp. 821-824, 2006

Contingent valuation (CV) surveys have been criticized for assuming that respondents have well-defined preferences. Using an innovative field experiment dealing with a privatized public good, it is shown that respondents are not influenced by public opinion but are positively responsive to scientific information.

Valorisation économique des effets de la pollution atmosphériqueJournal articleOlivier Chanel, Stéphane Luchini, Elsa Faugère, Ghislain Geniaux, Robert Kast and Pascale Scapecchi, Revue Économique, Volume 55, Issue 1, pp. 65-92, 2004

This article introduces the main results of a contextual contingent valuation survey (i.e. specific to the underlying risk) dealing with a change in air pollution exposition. Individual willingness-to-pay for both health (morbidity and mortality) and non-health effects are elicited. The use of an original hypothetical scenario that involves 1 273 inhabitants of the Bouches-du-Rhône and a convenient econometric model (Box-Cox model with censoring) lead to an overall predicted monthly value of 68,6 euros per household for an half decrease of the number of polluted days. A model of expected life-time resource allocation allows us to evaluate, for the first time, a value of a prevented fatality specific to the air pollution risk : 0,8 million Euros.Classification JEL : C1, I1, Q25, D12

Les consentements à payer pour des programmes de prévention sanitaire incluent-ils de l'altruisme ?. Enseignements d'une enquête sur la fièvre QJournal articleOlivier Chanel, Stéphane Luchini, Alain Paraponaris, Christel Protière and Jean-Christophe Vergnaud, Revue Économique, Volume 55, Issue 5, pp. 923-945, 2004

Increasingly, the assessment of health prevention policies is evaluated through willingness to pay (wtp) surveys. When the evaluation deals with policies with a public dimension, the individual? stated wtp can reflect an altruistic component, which may alter the results of the economic valuation. By applying an expected utility framework in a contingent valuation survey on Q fever, we can determine the individuals who integrate an altruistic component in their stated wtp (or not) that we further explain by explanatory variables. The main result is that 66 percent of respondents express an altruistic component when they state their wtp for the collective program. The part devoted to an altruistic motive is on average equal to 3,6 euro, nearly 25 percent of the considered wtp.Classification JEL : C25, D64, D841, I1

Combien valent les décès évités par la prévention ?Journal articleOlivier Chanel and Jean-Christophe Vergnaud, Revue Économique, Volume 55, Issue 5, pp. 989-1008, 2004

This paper concerns the difficulty of taking into account long term health effects of prevention policies in an economic valuation. The proposed methodology estimates the delay between the implementation of a policy and the achievement of all of the expected mortality-related health benefits. Benefits are assessed both in terms of life years gained and premature deaths avoided for two prevention policies: an air pollution abatement policy and a road safety policy. The main findings are that the relative comparison of the policies?benefits is very sensitive to technical choices dealing with the method chosen to assess mortality benefits and the discount rate.Classification JEL : H43, I12, Q25

Computing price trends in sequential auctionsJournal articleOlivier Chanel and Stéphanie Vincent, Recherches économiques de Louvain, Volume 70, Issue 4, pp. 443-460, 2004

This paper compares various methods used for measuring price trends in sequential auctions and draws on index number theory. Data from wine auctions are used to show that different methods applied to the same data may lead to significantly différent conclusions. Moreover the same method can even lead to opposite results depending on the way pairs are selected within the set of similar objects sold sequentially. Finally, the number of identical objects being sold also influences the price trend.

Economic Costs of Air Pollution Related Health Impacts - an Impact Assessment Project of Austria, France and SwitzerlandJournal articleR.K. Seethaler, N. Kunzli, H. Sommer, Olivier Chanel, M. Herry, S. Masson, J.C. Vernaud, P. Filliger, F. Horak, R. Kaiser, et al., Clean Air & Environmental Quality, Volume 37, Issue 1, pp. 35-43, 2003

The quantification of environmental-related health effects and their valuation in monetary units play a key role for a sustainability-oriented planning of policy measures. The present paper demonstrates the calculation of air pollution-related health costs using the tri-national study of Austria, France and Switzerland on health costs due to transport-related air pollution, that was conducted on behalf of the Third WHO Ministerial Conference (London, 1999). The epidemiological information on exposure-response functions (effect estimates) and health outcome frequencies (mortality and morbidity; prevalence, incidence, or person-days) combined with the air pollution exposure of the population, provides the number of attributable cases to total air pollution and to traffic-related air pollution. For the assessment of health costs, two different methods are available. The main method consists of the willingness-to-pay approach, that assesses the willingness to pay for a reduction in risk, that is for the prevention of a (statistical) fatality or illness. This approach includes the material costs as well as intangible cost elements, i.e. for pain, suffering and the loss of life quality. A partial method is the human-capital approach that estimates the medical costs and the loss of income, production or consumption arising due to premature mortality or morbidity and which only covers the material cost elements. Across the three countries (74 million inhabitants) the health costs due to traffic-related air pollution for the year 1996 amount to some 27 billion €. This amount translates to approximately 1.7% of GDP and an average of 360€ per capita per year. In all three countries, the premature mortality is predominant, accounting for about 70% of the costs.

Nathalie Moureau, Analyse économique de la valeur des biens d'art: La peinture contemporaineJournal articleOlivier Chanel, Journal of Cultural Economics, Volume 26, Issue 3, pp. 237-239, 2002

No abstract is available for this item.

Pollution atmosphérique et santé : évaluation monétaire et effets de long terme.Journal articleOlivier Chanel, Serge Masson, Pascale Scapecchi and Jean-Christophe Vergnaud, Région et Développement, Volume 12, pp. 33-53, 2000

Les effets sur la santé dits de long terme pose des difficultés particulières dans les évaluations économiques. En effet, puisque ces effets sont dues à une exposition cumulée à des facteurs de risque, il faut s'attendre à des délais entre la date de mise en oeuvre d'une politique de réduction de ces facteurs de risque et le moment où la totalité des bénéfices sanitaires espérés seront obtenus. Nous développons une méthodologie qui permet d'estimer ces délais et l'évolution des bénéfices obtenus. Nous appliquons cette méthodologie au cas d'une politique de réduction de la pollution de l'air. Le résultat principal est que la prise en compte de ces délais conduit à diviser par un facteur 1,6 à 2,5 les bénéfices. Il apparaît aussi que le taux d'actualisation a un effet qui dépend de la méthode de valorisation monétaire des effets sanitaires.

Public-health impact of outdoor and traffic-related air pollution: a European assessmentJournal articleN. Kunzli, R. Kaiser, S. Medina, M. Studnicka, Olivier Chanel, P. Filliger, M. Herry, F. Horak, V. Puybonnieux-Texier, P. Quenel, et al., The Lancet, Volume 356, Issue 9232, pp. 795-801, 2000

Background:
Air pollution contributes to mortality and morbidity. We estimated the impact of outdoor (total) and traffic-related air pollution on public health in Austria, France, and Switzerland. Attributable cases of morbidity and mortality were estimated.

Methods:
Epidemiology-based exposure-response functions for a 10 μg/m3 increase in particulate matter (PM10) were used to quantify the effects of air pollution. Cases attributable to air pollution were estimated for mortality (adults >30 years), respiratory and cardiovascular hospital admissions (all ages), incidence of chronic bronchitis (adults >25 years), bronchitis episodes in children (<15 years), restricted activity days (adults >20 years), and asthma attacks in adults and children. Population exposure (PM10) was modelled for each km2. The traffic-related fraction was estimated based on PM10 emission inventories.

Findings:
Air pollution caused 6% of total mortality or more than 40 000 attributable cases per year. About half of all mortality caused by air pollution was attributed to motorised traffic, accounting also for: more than 25 000 new cases of chronic bronchitis (adults); more than 290 000 episodes of bronchitis (children); more than 0·5 million asthma attacks; and more than 16 million person-days of restricted activities.

Interpretation:
This assessment estimates the public-health impacts of current patterns of air pollution. Although individual health risks of air pollution are relatively small, the public-health consequences are considerable. Traffic-related air pollution remains a key target for public-health action in Europe. Our results, which have also been used for economic valuation, should guide decisions on the assessment of environmental health-policy options.