Skip to main content
Log in

Evidence of a filtered approach to environmental monitoring

  • Published:
European Journal of Law and Economics Aims and scope Submit manuscript

Abstract

This contribution focuses on the formulation of optimal inspection strategies and distinguishes between a targeting approach and a filtered approach to monitoring. Using a case study for the Flemish textile industry, we investigate the costs and benefits associated with specific monitoring and enforcement campaigns. The results show the beneficial role such campaigns can play in an effective and efficient monitoring policy. Thus we provide empirical evidence of the advantages associated with the filtered monitoring approach and show that filtering is an interesting complement to targeting.

This is a preview of subscription content, log in via an institution to check access.

Access this article

Price excludes VAT (USA)
Tax calculation will be finalised during checkout.

Instant access to the full article PDF.

Similar content being viewed by others

Notes

  1. For an overview of empirical studies of the enforcement of environmental policy see Cohen (2000).

  2. Belgium as a federal state consists of three regions: Flanders, Wallonia and Brussels Capital.

  3. The IPPC directive 96/91/EG of 24 September 1996 concerning Integrated Pollution Prevention and Control focuses on an integrated and preventive approach to pollution.

  4. The Seveso II directive 96/82/EG of 9 December 1996 deals with the prevention of serious accidents concerning hazardous substances as well as limiting the consequence of such accidents for public health and the environment. It was extended by directive 2003/105/EC and applies to some thousands of industrial establishments where dangerous substances are present in quantities exceeding the thresholds in the directive.

  5. Appendix 1 ‘An alphabetical list of establishments considered to be a nuisance’ to the Order of the Flemish Government of 6 February 1991 concerning environmental licenses.

  6. Chemical oxygen demand (COD) is defined as the amount of oxygen needed per liter wastewater to completely break down the organic elements through oxidation (MIRA-T 2006).

  7. Yearly report AMI (2003), pp. 50–51.

  8. This was an interdisciplinary research project (2002–2004) financed by Federal Research Center with cooperation between the Center of Economic Studies of the K.U.Leuven (S. Proost, S. Rousseau & C. M. Billiet) and the Center of Environment Law of Ghent University (L. Lavrysen & C. M. Billiet).

  9. The Flemish environmental inspection agency was founded in 1991 and, in its own words, the agency was only fully functional in 1993. One of the effects of this starting-up phase is that many of the inspection reports are missing in the files and this makes the quality of the data concerning inspections before 1994 questionable.

  10. Here we exclude missing data. The percentages are calculated for the inspections for which we know the outcome.

  11. This probability is estimated using data from Rousseau (2007) and is low since in many instances more than one inspection was needed to formally document a violation. Also, many of the inspections in the dataset stated known violations in the inspection reports. Of course, these known violations will not to lead to the start of new sanctioning procedure since one was already started before.

  12. It is noteworthy that in none of the cases in our dataset an administrative sanction was imposed by the Flemish environmental inspection agency.

  13. For a recent overview of these topics see Cohen (1999) and Rousseau and Billiet (2008).

  14. The data collection ended in August 2003. Thus the comparison for 2003 has to be corrected for this since we only observe eight months for that year.

  15. For more details on these costs see Billiet et al. (2002) and Rousseau and Proost (2005).

  16. During the P216 project 38 firms received a warning letter to encourage them to correct the identified shortcomings. These warning letters contained 99 specific warnings (AMI 2003).

  17. See, for instance, Proost and Rousseau (2007) or Callan and Thomas (2000).

  18. See AMI (2003), p. 53. In Flanders, each notice of violation is send to the public prosecutor’s office and then the prosecutor decides about the next step in the sanctioning process such as dismissal, settlement or a criminal court trial. We assume that 48% of 22 notices of violation are followed by a monetary sanction: that is 23% of the cases can expect a settlement, 22% a criminal fine in first instance and 3% a fine in appeal (Billiet and Rousseau 2005). These percentages are estimated by looking at the outcome for 69 notices of violations for violations by textile firms in Flanders.

  19. Almost all (39 of 41) of the textile firms in our dataset are situated in this basin.

References

  • AMI. (2002). Milieuhandhavingsrapport. LNE Department Environment, Nature and Energy.

  • AMI. (2003). Milieuhandhavingsrapport. LNE Department Environment, Nature and Energy.

  • AMI. (2006). Milieuhandhavingsrapport. LNE Department Environment, Nature and Energy.

  • Ayres, I., & Braithwaite, J. (1995). Responsive regulation: Transcending the deregulation debate. Oxford, UK: Oxford University Press.

    Google Scholar 

  • Billiet, C. M., & Rousseau, S. (2005). Zachte rechtshandhaving in het bestuurlijke handhavingsspoor: De inspectiebeslissing en het voortraject van bestuurlijke sancties. Een rechtseconomische analyse. Tijdschrift voor Milieurecht, 1, 2–33.

    Google Scholar 

  • Billiet, C. M., Rousseau, S., & Proost, S. (2002). Law & economics and the choice of environmental policy instruments. Final Report.

  • Brouwer, R., Beckers, A., Courtecuisse, A., Vanden Driessche, L., & Dutrieux, S. (2007). Economic valuation of the non-market benefits of the European Water Framework Directive: An international river basin application of the contingent valuation method. From www.lne.be. Accessed 27 July 2009.

  • Callan, S. J., & Thomas, J. M. (2000). Environmental economics and management. Theory, policy and applications. Fort Worth, US: Harcourt College Publishers.

    Google Scholar 

  • Cohen, M. A. (1987). Optimal enforcement strategy to prevent oil spills: An application of a principal-agent model with moral hazard. The Journal of Law & Economics, 30, 23–51. doi:10.1086/467128.

    Article  Google Scholar 

  • Cohen, M. A. (1999). Monitoring and enforcement of environmental policy. In T. Tietenberg & H. Folmer (Eds.), International yearbook of environmental and resource economics (Vol. III, pp. 44–106). Cheltenham, UK: Edward Elgar Publishers.

    Google Scholar 

  • Cohen, M. A. (2000). Empirical research on the deterrent effect of environmental monitoring and enforcement. The Environmental Law Reporter, 30, 10245–10252.

    Google Scholar 

  • Eckert, H. (2004). Inspections, warnings, and compliance: The case of petroleum storage regulation. Journal of Environmental Economics and Management, 47, 232–259. doi:10.1016/S0095-0696(03)00079-2.

    Article  Google Scholar 

  • Faure, M. G., & Visser, M. (2004). Law and economics of environmental crime. In H. Sjögren & G. Skogh (Eds.), New perspectives on economic crime (pp. 57–75). Cheltenham, UK: Edward Elgar Publishing.

    Google Scholar 

  • Garoupa, N. (2001). Optimal magnitude and probability of fines. European Economic Review, 45, 1765–1771. doi:10.1016/S0014-2921(00)00084-2.

    Article  Google Scholar 

  • Gray, W., & Deily, M. (1996). Compliance and enforcement: Air pollution regulation in the American steel industry. Journal of Environmental Economics and Management, 31, 96–111. doi:10.1006/jeem.1996.0034.

    Article  Google Scholar 

  • Harrington, W. (1988). Enforcement leverage when penalties are restricted. Journal of Public Economics, 37, 29–53. doi:10.1016/0047-2727(88)90003-5.

    Article  Google Scholar 

  • Heyes, A. (2002). A theory of filtered enforcement. Journal of Environmental Economics and Management, 43, 34–46. doi:10.1006/jeem.2000.1172.

    Article  Google Scholar 

  • Lando, H., & Shavell, S. (2004). The advantage of focusing law enforcement effort. International Review of Law and Economics, 24, 209–218. doi:10.1016/j.irle.2004.08.005.

    Article  Google Scholar 

  • Laplante, B., & Rilstone, P. (1996). Environmental inspections and emissions of the pulp and paper industry in Quebec. Journal of Environmental Economics and Management, 31, 19–36. doi:10.1006/jeem.1996.0029.

    Article  Google Scholar 

  • Liekens, I., & De Nocker, L. (2008). Rekenraamwerk voor de economische baten voor een betere waterkwaliteit. Study executed by order of the Vlaamse Milieumaatschappij, MIRA/2008/07, VITO. Available on www.milieurapport.be.

  • Malik, A. S. (2007). Optimal environmental regulation based on more than just emissions. Journal of Regulatory Economics, 32(1), 1–16. doi:10.1007/s11149-006-9007-7.

    Article  Google Scholar 

  • MIRA-T. (2006). Focusrapport. VMM.

  • MIRA-T. (2007). Indicatorrapport. VMM.

  • Ogus, A., & Abbot, C. (2002). Pollution and penalties. In T. Swanson (Ed.), An introduction to the law and economics of environmental policy: Issues in institutional design (pp. 493–516). Amsterdam: Elsevier.

    Chapter  Google Scholar 

  • Polinsky, A. M., & Shavell, S. (1979). The optimal tradeoff between the probability and magnitude of fines. The American Economic Review, 69(5), 880–891.

    Google Scholar 

  • Polinsky, A. M., & Shavell, S. (1992). Enforcement costs and the optimal magnitude and probability of fines. The Journal of Law & Economics, 35, 133–148. doi:10.1086/467247.

    Article  Google Scholar 

  • Proost, S., & Rousseau, S. (2007). Inleiding tot de milieueconomie. Leuven: Acco.

    Google Scholar 

  • Rasmusen, E. (1995). How optimal penalties change with the amount of harm. International Review of Law and Economics, 15, 101–108. doi:10.1016/0144-8188(94)00008-I.

    Article  Google Scholar 

  • Rousseau, S. (2007). Timing of environmental inspections: Survival of the compliant. Journal of Regulatory Economics, 32(1), 17–36. doi:10.1007/s11149-006-9013-9.

    Article  Google Scholar 

  • Rousseau, S., & Billiet, C. M. (2008). Rechtseconomische analyse van de handhavingsnood in het milieubeleid. Review of Business and Economics, 53(2), 188–212.

    Google Scholar 

  • Rousseau, S., & Proost, S. (2005). Comparing environmental policy instruments in the presence of imperfect compliance–A case study. Environmental & Resource Economics, 32(3), 337–365. doi:10.1007/s10640-005-6646-6.

    Article  Google Scholar 

  • Stafford, S. L. (2002). The effect of punishment on firm compliance with hazardous waste regulations. Journal of Environmental Economics and Management, 44, 290–308. doi:10.1006/jeem.2001.1204.

    Article  Google Scholar 

  • Vander Beken, T., & Balcaen, A. (2007). Strafrechtelijke sanctionering van milieurecht: Stroomschema van PV tot vonnis. Environmental Lawforce Working Paper 2007-02.

Download references

Acknowledgments

This research was financed by the project ‘Economic modelling of environmental law enforcement’ funded by the Fonds voor Wetenschappelijk Onderzoek (FWO) and the SBO-project ‘Environmental Law Enforcement: a Comparison of Practice in the Criminal and the Administrative Tracks’ (www.environmental-lawforce.be) funded by the Instituut voor Wetenschap en Technology (IWT). Moreover I sincerely want to thank two anonymous referees and Carole M. Billiet for their useful suggestions.

Author information

Authors and Affiliations

Authors

Corresponding author

Correspondence to Sandra Rousseau.

Rights and permissions

Reprints and permissions

About this article

Cite this article

Rousseau, S. Evidence of a filtered approach to environmental monitoring. Eur J Law Econ 29, 195–209 (2010). https://doi.org/10.1007/s10657-009-9117-7

Download citation

  • Received:

  • Accepted:

  • Published:

  • Issue Date:

  • DOI: https://doi.org/10.1007/s10657-009-9117-7

Keywords

JEL Classification

Navigation