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A Strategic Analysis of Eutrophication Abatement in the Baltic Sea

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Abstract

Cooperation between the littoral countries of the Baltic Sea to mitigate eutrophication has proven difficult in the past. In this study, we explore the countries’ incentives to free-ride on agreements, find stable coalitions where free-riding is deterred, and propose alternative ways of designing stable agreements that would reduce eutrophication in the sea. We conclude that strong free-riding incentives for some countries preclude the socially optimal solution in the absence of an enforcing authority. A stable agreement can, however, be formed with some loss in efficiency. The research shows that a treaty with modest abatement targets between all the littoral countries would be more efficient than a coalition between fewer countries but with more ambitious targets. We compare the two international institutions involved in the protection of the Baltic Sea—the intergovernmental Helsinki Commission and the partly supranational European Union—and show that the European Union would not benefit from enforcing an agreement among its member states on the Baltic without Russia being involved in the conservation efforts. Our results suggest that efficient abatement and full participation could be achieved by using the power the European Union has to enforce such an agreement among its members and, simultaneously, negotiating with Russia within the Helsinki Commission.

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Notes

  1. An extensive review of analyses based on game theory can be found in Finus (2001) and Barrett (2003).

  2. The term “focal treaty” was first introduced by Barrett (2002) as the opposite of “consensus treaty”, but the concept (focal treaty) had already been used in earlier research (e.g. by Barrett 1994).

  3. Game-theoretic analyses of IEAs have used both emission and abatement models. The two forms of models are equivalent as long as abatement does not exceed the flow of emissions (Diamantoudi and Sartzetakis 2006).

  4. The following seven basins of the Baltic Sea are distinguished: (1) Bothnian Bay, (2) Bothnian Sea, (3) Baltic Proper, (4) Gulf of Finland, (5) Gulf of Riga, (6) Danish Straits, (7) Kattegat.

  5. Note that the matrices illustrated in Tables 1 and 2 do not sum. The amount of nutrients which does not end up in any sea basin in the next year is decayed by denitrification (for nitrogen) or permanent burial (for both nitrogen and phosphorus).

  6. These are described in detail in e.g. Gren et al. (1995, 1997a).

  7. The cost and benefit parameters for each country and sea basin are listed in Appendix A (Tables 5, 6, 7, 8, 9, 10, 11, 12, 13, 14).

  8. In fact, Poland has already been sued before the European Court of Justice for its failure to introduce a strategy for Baltic Sea protection in time (European Commission 2011).

  9. A notorious example is the Rhine chlorides dispute, which lasted for over 70 years and could not be solved before the victim (the Netherlands) agreed to make side payments to the polluter (France) (Dieperink 2011).

  10. The estimated funding required by waste water treatment sector from the Structural Funds and Cohesion Fund in 2007–2013 is 32 million euros annually for Estonia, 155 million euros for Latvia, 86 million euros for Lithuania and 859 million euros for Poland. These numbers were still subject to negotiation when the report was published (Medhurst 2006).

  11. The St Petersburg waste water treatment plant, opened in 2005, was both internationally and locally funded. For example, The Finnish Ministry of the Environment contributed 10 million euros, and the Swedish International Development Cooperation Agency 11 million euros towards the total budget of 197 million euros (Environment.fi 2005).

Abbreviations

IEA:

International environmental agreement

HELCOM:

Helsinki Commission

BSAP:

The Baltic Sea Action Plan

EU:

European Union

MSFD:

Marine Strategy Framework Directive

SCF:

Structural and Cohesion Funds

ENPI:

European Neighbourhood and Partnership Instrument

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Correspondence to Lassi Ahlvik.

Appendices

Appendix A: Cost and Benefit Function Parameters

See Tables 5, 6, 7, 8, 9, 10, 11, 12, 13 and 14.

Table 5 Parameters \(e_{ij}^l \) for \(l=N\)
Table 6 Parameters \(f_{ij}^l \) for \(l=N\)
Table 7 Parameters \(g_{ij}^l \) for \(l=N\)
Table 8 Parameters \(e_{ij}^l \) for \(l= P\)
Table 9 Parameters \(f_{ij}^l \) for \(l= P\)
Table 10 Parameters \(g_{ij}^l \) for \(l=P\)
Table 11 Parameters \(a_{ij}^l \) for \(l=N\)
Table 12 Parameters \(b_{ij}^l \) for \(l=N\)
Table 13 Parameters \(a_{ij}^l \) for \(l=P\)
Table 14 Parameters \(b_{ij}^l \) for \(l=P\)

Appendix B: Stable Focal Treaties

See Tables 15 and 16.

Table 15 Internally and externally stable focal treaties without side payments
Table 16 Potentially internally and externally stable focal treaties when side payments are allowed

Appendix C: Payoffs for the Nash–Cournot Game

See Tables 17 and 18.

Table 17 Annualized payoffs after size payments and sizes of side payments (in brackets) for all environmental agreements to mitigate eutrophication in the Baltic Sea (in \(10^{6}\) Euros) for the Nash–Cournot game
Table 18 Total emission of nitrogen (N) and phosphorus (P) to the Baltic Sea in all environmental agreements to mitigate eutrophication in the Baltic Sea (in 1,000 kg per year) for the Nash–Cournot game

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Ahlvik, L., Pavlova, Y. A Strategic Analysis of Eutrophication Abatement in the Baltic Sea. Environ Resource Econ 56, 353–378 (2013). https://doi.org/10.1007/s10640-013-9651-1

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