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The interest-based explanation of international environmental policy

Published online by Cambridge University Press:  22 May 2009

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Despite growing international environmental interdependence, the international system lacks a central authority to foster environmental protection. As a consequence, countries have adopted different policies to reduce international environmental problems. More specifically, costly regulations are not universally supported. In order to explain the success and failure of international environmental regulation, it is necessary to systematically focus on the factors that shape the environmental foreign policy of sovereign states. Since such an approach is missing from the literature, we develop an interest-based explanation of support for international environmental regulation and postulate what impact it should have on state preferences for international environmental regulation. Specifically we apply our framework to two prominent cases of negotiations on atmospheric pollution control, namely, efforts to protect the stratospheric ozone layer and the regulation of transboundary acidification (“acid rain”) in Europe.

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Copyright © The IO Foundation and Cambridge University Press 1994

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References

We thank Cary Coglianese, Kenneth Hanf, Madeleine Hösli, Rudy Lewanski, Martin List, John Odell, Tom Princen, Arild Underdal, Albert Weale, and two reviewers for International Organization for helpful comments. Val Bowers's editorial assistance is greatly appreciated. In addition, Detlef Sprinz gratefully acknowledges financial support from the Institute for the Study of World Politics in Washington, D.C., the Population-Environment Dynamics Project, School of Public Health, The University of Michigan, Ann Arbor, and the Horace H. Rackham School of Graduate Studies, The University of Michigan, Ann Arbor. We gladly accept the responsibility for all remaining errors and omissions.

1 See Singer, J. David, “The Level-of-Analysis Problem in International Relations,” in Knorr, Klaus and Verba, Sidney, eds., The International System: Theoretical Essays (Princeton, N.J.: Princeton University Press, 1961), pp. 7792.Google Scholar

2 The term “abatement costs,” as used in this article, reflects the resource outlays associated with a governmental position. It does not reflect damage costs. For international comparisons, abatement costs are expressed as a share of gross domestic product (GDP) or gross national product (GNP) so as to reflect a country's “relative effort.”

3 Keohane, Robert O. and Nye, Joseph S., Power and Interdependence (New York: Harper Collins, 1989).Google Scholar

4 Prittwitz, Volker von, Das Katastrophenparadox: Elemente einer Theorie der Umweltpolitik (The catastrophe paradox: Elements of a theory of environmental policy) (Opladen, Germany: Leske and Budrich, 1990), pp. 103–15.Google Scholar

5 The term “epistemic community” refers to a knowledge-based transnational network of specialists whose members share common views about the causes of environmental problems and the policies to control them. See Haas, Peter M., Saving the Mediterranean: The Politics of International Environmental Cooperation (New York: Columbia University Press, 1990).Google Scholar

6 Haas, Peter M., “Banning Chlorofluorocarbons: Epistemic Community Efforts to Protect Stratospheric Ozone,” International Organization 46 (Winter 1992), pp. 189224 and p. 215 in particular.CrossRefGoogle Scholar

7 This possibility is also mentioned by the proponents of the theory of epistemic communities. See p. 30 of Peter Haas, “Introduction: Epistemic Communities and International Policy Coordination,” International Organization 46 (Winter 1992), pp. 135.Google Scholar

8 See Sprinz, Detlef F., “Why Countries Support International Environmental Agreements: The Regulation of Acid Rain in Europe,” Ph.D. diss., Department of Political Science, The University of Michigan, Ann Arbor, (1992).Google Scholar

9 See pp. 152–54 of Glas, Joseph P., “Protecting the Ozone Layer: A Perspective from Industry,” in Ausubel, Jesse H. and Sladovich, Hedy E., eds., Technology and Environment (Washington, D.C.: National Academy Press, 1989), pp. 137–55.Google Scholar

10 See ibid.; Morrisette, Peter M., “The Evolution of Policy Responses to Stratospheric Ozone Depletion,” Natural Resources Journal 29 (Summer 1989), pp. 793820Google Scholar; Benedick, Richard E., “Ozone Diplomacy,” Issues in Science and Technology 6 (Fall 1989), pp. 4350Google Scholar; and Benedick, Richard E., Ozone Diplomacy: New Directions in Safeguarding the Planet (Cambridge, Mass.: Harvard University Press, 1991).Google Scholar

11 See Benedick, , “Ozone Diplomacy”; and Benedick, Ozone Diplomacy: New Directions in Safeguarding the Planet.Google Scholar

12 Haas, , “Banning Chlorofluorocarbons.”Google Scholar

13 Parson, Edward A., “Protecting the Ozone Layer,” in Haas, Peter M., Keohane, Robert O., and Levy, Marc A., eds., Institutions for the Earth: Sources of Effective Environmental Protection (Cambridge, Mass.: MIT Press, 1993), pp. 2773.Google Scholar

14 Haas, “Banning Chlorofluorocarbons.”

15 The LRTAP Convention serves as an umbrella convention for the international regime on the regulation of transboundary acidification (acid rain) in the member states of the United Nations Economic Commission for Europe (UNECE). Canada and the United States are members of the UNECE as are all European countries.

16 For examples of the literature on the LRTAP, see Jackson, C. Ian, “A Tenth Anniversary Review of the ECE Convention on Long-range Transboundary Air Pollution,” International Environmental Affairs 2 (Summer 1990), pp. 217–26Google Scholar; Rosencranz, Armin, “The ECE Convention of 1979 on Long-range Transboundary Air Pollution,” in Zeitschrift für Umweltpolitik 4 (December 1981), pp. 511–20Google Scholar; Prittwitz, Volker, Umweltaussenpolitik: Grenzüberschreitende Luftverschmutzung in Europa (Foreign environmental policy: Transboundary air pollution in Europe) (Frankfurt a.M.: Campus, 1984)Google Scholar; and Wetstone, Gregory and Rosencranz, Armin, Acid Rain in Europe and North America National Responses to an International Problem (Arlington, Va.: Environmental Law Bookcrafter, 1983).Google Scholar

17 See Rhode, Barbara, ed., Air Pollution in Europe, vol. 1, Western Europe, and vol. 2, Socialist Countries, (Vienna: European Coordination Centre for Research and Documentation in the Social Sciences, Vienna Centre, 1988)Google Scholar; Weidner, Helmut, Air Pollution Control: Strategies and Policies in the Federal Republic of Germany (Berlin: Edition Sigma, 1986)Google Scholar; Weidner, Helmut, Clean Air Policy in Great Britain: Problem Shifting as Best Practicable Means (Berlin: Edition Sigma, 1987)Google Scholar; Boehmer-Christiansen, Sonja and Skea, Jim, Acid Politics: Environmental and Energy Policies in Britain and Germany (London: Belhaven Press, 1991); and Wetstone and Rosencranz, Acid Rain in Europe and North America.Google Scholar

18 The study by Boehmer-Christiansen and Skea, Acid Politics, shows an explicit comparative research design, but the number of explanatory factors exceeds by far the number of cases. Therefore, the conclusions are unlikely to be robust unless different research methods are employed.

19 Sand, Peter, “Air Pollution in Europe: International Policy Responses,” Environment 29 (December 1987), pp. 1620 and 2829.Google Scholar

20 Rosencranz, Armin, “The Acid Rain Controversy in Europe and North America: A Political Analysis,” in Carroll, John E., ed., International Environmental Diplomacy: The Management and Resolution of Transfrontier Environmental Problems (Cambridge, England: Cambridge University Press, 1988), pp. 173–87.Google Scholar

21 Levy, Marc A., “European Acid Rain: The Power of Toteboard Diplomacy,” in Haas, , Keohane, , and Levy, , Institutions for the Earth, pp. 75132.Google Scholar

22 Stoel, Thomas B. Jr., “Fluorocarbons: Mobilizing Concern and Action,” in Kay, David A. and Jacobson, Harold K., eds., Environmental Protection: The International Dimension (Totowa, N.J.: Allenheld, Osmun, 1983), pp. 4574Google Scholar. The quotations are drawn from p. 57.Google Scholar

23 UNEP, “Assessment of Risks to the Ozone Layer,” 1st Meeting of Steering Committee to Plan Workshops on Chlorofluorocarbons, 1718 September 1985, mimeograph, p. 6.Google Scholar

24 We refer to the knowledge available to decision makers in the early 1980s rather than since the late 1980s. Only after the conclusion of the Montreal Protocol did it become evident that the thinning of the stratospheric ozone layer disproportionally affects the polar regions.

25 Jones, Robin R., “Consequences for Human Health of Stratospheric Ozone Depletion,” in Jones, R. Russell and Wigley, T., eds., Ozone Depletion: Health and Environmental Consequences (New York: John Wiley & Sons, 1989), pp. 207–27.Google Scholar

26 UNEP, Ad Hoc Working Group of Legal and Technical Experts for the Preparation of a Protocol on Chlorofluorocarbons to the Vienna Convention for the Protection of the Ozone Layer (Vienna Group), “Report of the Ad Hoc Working Group on the Work of Its Second Session,” UNEP/WG 167/2, 4 March 1987, p. 7.Google Scholar

27 Quoted from Whitney, Craig R., “EC Official Says Europeans Soon Can Shield Ozone Layer,” International Herald Tribune, 6 March 1989, p. 5.Google Scholar

28 Skin cancer may also be caused by other factors. However, given the small number of cases, a multiple regression analysis of the various causes of skin cancer appears not to be feasible.

29 Heimsoeth, Harald, “The Protection of the Ozone Layer,” Environmental Policy and Law 10 (April 1983), pp. 3436.CrossRefGoogle Scholar

30 Ibid., p. 35.

31 UNEP, Ad Hoc Working Group of Legal and Technical Experts for the Elaboration of a Global Framework Convention for the Protection of the Ozone Layer (hereafter Working Group for Ozone Layer Protection), “Draft Annex Concerning Measures to Control, Limit, and Reduce the Use and Emissions of Fully Halogenated Chlorofluorocarbons (CFCs) for the Protection of the Ozone Layer, Submitted by Finland, Norway, and Sweden,” UNEP/WG 94/4 Add. 3, 17 October 1983, pp. 12.Google Scholar

32 Australia had also been invited, but it did not participate in the conference.

33 UNEP, Working Group for Ozone Layer Protection, “Article II to the Protocol: Control of Use of CFCs, Proposal by the Expert from the Netherlands,” UNEP/WG 110/CRP.5, 23 October 1984.Google Scholar

34 UNEP, Vienna Group, “Report of the Ad Hoc Working Group on the Work of Its Third Session,” UNEP/WG 172/2, 8 May 1987, p. 5.Google Scholar

35 Ibid, p. 7.

36 UNEP, Working Group for Ozone Layer Protection, “Report of the Working Group,” UNEP/WG 78/13, 17 June 1983, p. 3.Google Scholar

37 UNEP, Working Group for Ozone Layer Protection, “Draft Annex Concerning Measures to Control, Limit, and Reduce the Use and Emissions of Fully Halogenated Chlorofluorocarbons (CFCs) for the Protection of the Ozone Layer, Submitted by Finland, Norway, and Sweden,” UNEP/WG 94/4 Add. 1, 15 September 1983, p. 3.Google Scholar

38 UNEP, Working Group for Ozone Layer Protection, “Recommendation of the Ad Hoc Working Group of Legal and Technical Experts for the Elaboration of a Global Framework Convention for the Protection of the Ozone Layer for a Decision to be Taken by the Governing Council of UNEP,” UNEP/WG 94/CRP 34, 19 January 1984.Google Scholar

39 See UNEP, Conference of Plenipotentiaries on the Protection of the Ozone Layer, “Final Report of the Ad Hoc Working Group of Legal and Technical Experts for the Elaboration of a Global Framework Convention for the Protection of the Ozone Layer,” UNEP/IG 53/4, Annex II, 28 January 1985, p. 4Google Scholar; and UNEP, Vienna Group, “Draft Report of the Ad Hoc Working Group on the Work of Its First Session,” UNEP/WG 151/L.4, 15 January 1987, pp. 67.Google Scholar

40 UNEP/WG 172/2, pp. 56.Google Scholar

41 UNEP/WG 167/2, p. 6.Google Scholar

42 Lang, Winifried, “Diplomatie zwischen Ökonomie und Ökologie: Das Beispiel des Ozonvertrags von Montreal” (Diplomacy between economics and ecology: The case of the Montreal Protocol), Europa-Archiv 43 (25 February 1988), p. 108.Google Scholar

43 See Benedick, , Ozone Diplomacy: New Directions in Safeguarding the Planet, p. 85Google Scholar: and Haas, , “Banning Chlorofluorocarbons,” p. 209.Google Scholar

44 Unfortunately, no data are available on the rate of skin cancer in the mid-1970s for Austria or for the Netherlands.

45 Stoel, Thomas B. Jr., Miller, Alan S., and Milroy, Breck, Fluorocarbon Regulation: An International Comparison (Lexington, Mass.: D.C. Heath, 1980), p. 221.Google Scholar

46 International Herald Tribune, 19 December 1986, p. 4.Google Scholar

47 See pp. 357–58 of Sebenius, James K., “Challenging Conventional Explanations of International Cooperation: Negotiation Analysis of the Case of Epistemic Communities,” International Organization 46 (Winter 1992), pp. 323–65CrossRefGoogle Scholar; and Benedick, , Ozone Diplomacy: New Directions in Safeguarding the Planet, p. 33Google Scholar; and Morrisette, , “The Evolution of Policy Responses to Stratospheric Ozone Depletion,” pp. 815–16.Google Scholar

48 Glas, , “Protecting the Ozone Layer,” p. 150.Google Scholar

49 DuPont is quoted in International Herald Tribune, 29 March 1988, p. 4.Google Scholar

50 Dickman, Steven, “West Germany Strides Towards CFC Elimination by 2000,” Nature 327 (14 May 1987), p. 93Google Scholar. A similar observation has been made by Benedick. In explaining the differences in 1990 within the EC on the policy toward regulation, Benedick remarks that the FRG announced that it will phase out CFCs in 1995 and other ozone-depleting substances before the end of the century. This took place after the federal government of the FRG had concluded that alternatives to the major harmful chemicals were close to commercial feasibility for nearly all applications. See Benedick, , Ozone Diplomacy: New Directions in Safeguarding the Planet, pp. 164–65.Google Scholar

51 Hammitt, James K. et al. , Product Uses and Market Trends of Potential Ozone-depleting Substances, 1985–2000 (Santa Monica, Calif.: Rand Corporation, 1986), p. 17.Google Scholar

52 MacKenzie, Debora, “Chemical Giants Battle over Ozone Holes,” New Scientist 114 (23 April 1987), p. 22.Google Scholar

53 UNEP/WG.172/2, p. 6.Google Scholar

54 Benedick, , Ozone Diplomacy: New Directions in Safeguarding the Planet, pp. 3031.Google Scholar

55 Miller, Alan, “The Development of Substitutes for Chlorofluorocarbons: Public-Private Cooperation and Environmental Policy,” Ambio 19 (October 1990), pp. 338–40.Google Scholar

56 Organization for Economic Cooperation and Development (OECD), The OECD Programme on Long Range Transport of Air Pollutants: Measurements and Findings, 2d ed. (Paris: OECD, 1979).Google Scholar

57 Geographically small countries or those with extremely small emissions have been excluded from the analysis. Canada, Turkey, and the United States were not included in the analysis since they are not (or are insufficiently) covered by EMEP. In addition, EMEP monitors only the European part of the former Soviet Union.

58 The interviews of experts were undertaken by Detlef Sprinz as part of a larger research effort on the international regulation of transboundary air pollution in Europe. For details, see Sprinz, “Why Countries Support International Environmental Agreements.”

59 Hettelingh, Jean-Paul, Downing, Robert F., and Smet, Peter A.M. de, Mapping Critical Loads for Europe, Coordination Center for Effects (CCE) technical report no. 1 (Bilthoven: CCE, National Institute of Public Health and Environmental Protection, the Netherlands, 1991).Google Scholar

60 Using 1991 data is only a second-best strategy, since abatement policies during the 1980s have been asymmetric across countries. However, the procedure can be justified on the basis of the failure of previous abatement efforts to lead to a major improvement of the state of the ecosystems. Therefore, the incentive structure for countries to reach additional emission-reduction protocols had not changed. Furthermore, our dichotomous classification is likely to reduce the errors introduced by asymmetric emission policies across nations. In conclusion, the data resemble the basic ecological vulnerability of states in 1985.Google Scholar

61 Amann, Markus and Kornai, Gabor, “Cost Functions for Controlling SO2 Emissions in Europe,” Working Paper Series of the International Institute for Applied Systems Analysis, WP-87–065, Laxenburg, Austria, mimeograph, 1987.Google Scholar

62 Ibid., pp. 2 and 3, respectively.

63 It must be noted that the UK objected to 1980 as the reference year since it would have easily fulfilled the obligations with a base year chosen from the early 1970s; personal communication.

64 Rosencranz, , “The ECE Convention of 1979 on Long-range Transboundary Air Pollution,” p. 517.Google Scholar

65 Swedish Ministry of Agriculture, Proceedings of the 1982 Stockholm Conference on Acidification of the Environment, June 21–30, 1982 (Stockholm: Swedish Ministry of Agriculture, 1982), p. 37.Google Scholar

66 The 30 percent level was chosen for purely political reasons and is not based on (narrow) ecological considerations.

67 See Prittwitz, , Umweltaussenpolitik—Grenzüberschreitende Luftverschmutzung in Europa, p. 143Google Scholar; and Boehmer-Christiansen, and Skea, , Acid Politics, p. 216.Google Scholar

68 Although the British Department of the Environment was willing to sign the Helsinki Protocol, this was overruled by Prime Minister Thatcher. See Boehmer-Christiansen and Skea, Acid Politics—Environmental and Energy Policies in Britain and Germany, p. 216.Google Scholar

69 UNECE, Air Pollution Across Borders, Air Pollution Studies, no. 2 (Geneva: UNECE), pp. 129–33.Google Scholar

70 See Prittwitz, Volker, “Several Approaches to the Analysis of International Environmental Policy,” Working paper series of the Abteilung Normbildung und Umwelt des Forschungsschwerpunkts Technik-Arbeit-Umwelt, FS II 88308Google Scholar, Berlin, Wissenschaftszentrum, mimeograph, 1988, pp. 89Google Scholar; and Prittwitz, , Das Katastrophenparadox, pp. 115–29.Google Scholar

71 They were normally supported by Austria, the Netherlands, and Switzerland.

72 This applies both to the Vienna and the LRTAP Conventions.

73 See Inglehart, Ronald, The Silent Revolution: Changing Values and Political Styles Among Western Publics (Princeton, N.J.: Princeton University Press, 1977);Google Scholar and Inglehart, Ronald, Culture Shift in Advanced Industrial Society (Princeton, N.J.: Princeton University Press, 1990).Google Scholar

74 See Sprinz, Detlef, “Environmental Concern and Environmental Action in Western Europe: Concepts, Measurements and Implications,” presented at the 86th annual meeting of the American Political Science Association, 30 August-2 September 1990, San Francisco.Google Scholar

75 Schwarzer, Gudrun, Weiträumige grenzüberschreitende Luftverschmutzung: Konfliktanalyse eines internationalen Umweltproblems (Transboundary air pollution: Conflict analysis of an international environmental problem)Google Scholar, Arbeitspapiere, Tübinger zur internationalen Politik und Friedensforschung, no. 15 (Tübingen, Germany: Arbeitsgruppe Friedensforschung, Institut für Politikwissenschaft, Universität Tübingen, 1990).Google Scholar

76 See Sprinz, , “Why Countries Support International Environmental Agreements,” chaps. 5–7.Google Scholar