Skip to main content

Advertisement

Log in

The Political Game of European Fisheries Management

  • Published:
Environmental and Resource Economics Aims and scope Submit manuscript

Abstract

European fisheries activities are subject to a hierarchy of regulatory authorities. This raises questions regarding the implications of strategic interaction between different authority levels concerning the regulation of these activities. We apply a bio-economic objective function where fishers and regulators have environmental, economic and social preferences, and where fishers are subject to the aggregate of the regulations set by the various authorities. We analyse one situation where EU authorities set their regulation first, followed by national authorities’ regulation, and one situation where the two regulators set their regulations simultaneously. Using data from a survey on preferences among fisheries stakeholders combined with data from the UK nephrops fisheries, this study shows that a hierarchy of regulators with similar preferences will yield higher unit regulations, i.e. higher taxes or higher subsidies than a situation with one regulating authority. When regulators have unequal preferences we may get a situation where one regulator induces a tax on effort, whereas the other offers a subsidy. In this situation the aggregate unit regulation becomes uncertain.

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.

Institutional subscriptions

Similar content being viewed by others

Notes

  1. Clearly, in an uncertain world better protection could be obtained at higher stock levels than MSY. Whereas this technically can be implemented in our model, it makes the model analytically less tractable without adding much to the results. It would increase the optimal unit regulation (when a tax) somewhat and thus reduce the optimal effort compared to the model we use in this paper. In another paper, Aanesen and Armstrong (2014a), we apply an objective function where utility does not decrease in the stock size beyond the MSY stock level.

  2. The expressions for optimal effort for each of the actors are given in the “Appendix 6.1”.

  3. The explicit expressions for the optimal regulations with two regulators setting their regulation simultaneously are given in the “Appendix 6.2”.

  4. This was done in the EU-funded FP7 project “Making the European Fisheries Ecosystem Plan Operationable”.

  5. The three pillars were expanded upon with regards to descriptors and indicators, but this is not necessary for the current analysis.

  6. This is the case with the following preference structure for the fishers; \(\beta _1^F=0.3,\beta _2^F=0.1,\beta _3^F =0.6\).

  7. With two regulators, one set of fishers’ preferences which give this preferred effort level is \(\beta _1^F=0.36,\beta _2^F=0.21,\beta _3^F=0.43\).

  8. Note that this exceeds the MSY level and thus does not represent a steady state solution.

  9. This is the case with the following preference structure for the EU authorities; \(\beta _1^{EU}=0.29,\beta _2^{EU}=0.04,\beta _3^{EU}=0.67\).

References

  • Aanesen M, Armstrong CW (2014a) The implications of environmental NGO involvement in fisheries management. Land Econ 90:560–573

    Article  Google Scholar 

  • Aanesen M, Armstrong CW, Bloomfield HJ, Rockmann C (2014b) What does stakeholder involvement mean for ecosystem based fisheries management? Ecol Soc 19(4):35. doi:10.5751/ES-06947-190435

  • Aanesen M, Armstrong CW (2013) Stakeholder influence and optimal regulations: a common agency analysis of fisheries regulations. J Inst Theor Econ 169:320–338

    Article  Google Scholar 

  • Bailey MC, Polunin NV, Hawkins AD (2012) A sustainable fishing plan for the Farne Deeps nephrops fisheries. Report to the Marine Management Organisation May 2012, Newcastle University

  • Blom-Hansen J (2005) Principals, agents, and the implementation of EU cohesion policy. J Eur Public Policy 12:624–648

  • Bulow JI, Geanakoplos JD, Klemperer PD (1985) Multimarket oligopoly: strategic substitutes and complements. J Polit Econ 93:488–511

    Article  Google Scholar 

  • Campoy JC, Negrete JC (2008) Optimal central bankers contracts and common agency: a comment. Public Choice 137:197–206

    Article  Google Scholar 

  • Campoy JC, Negrete JC (2010) Structural reforms and budget deficit in a monetary union: a strategic approach. BE J Econ Anal Policy 10. doi:10.2202/1935-1682.2125

  • Commission of European Communities (COM) (2008) Preparation of annual economic report (SGECA 08–02), Copenhagen, 21–25 April 2008, Evaluated by STECF 7–11 July 2008

  • Commission of European Communities (COM) (2009) Green paper on the revision of the Common Fisheries Policy, 163

  • Council Regulation (EC) No 2371/2002 on the conservation and sustainable exploitation of fisheries resources under the Common Fisheries Policy

  • Curtiz H, Brodie C, Longoni E (2010) 2008 economic survey of the UK fishing fleet. Seafish, Edinburgh

    Google Scholar 

  • Gezelius SS, Hegland TJ, Pavlevsky H, Raakjaer J (2008) The politics of implementation in resource conservation: comparing the EU/Denmark and Norway. In: Gezelius SS, Raakjaer J (eds) Making fisheries management work: implementation of policies for sustainable fishing. Springer, New York

    Chapter  Google Scholar 

  • Hansen LG, Jensen F, Brandt US, Vestergaard N (2006) Illegal landings: an aggregate catch self-reporting mechanism. Am J Agric Econ 88:974–985

    Article  Google Scholar 

  • ICES (International Council for the Exploration of the Sea) (2008) Report of the ICES Advisory Committee 2008. ICES Advice, Book 5, pp 267

  • Jensen F, Vestergaard N (2002a) Management of fisheries in the EU: a principal-agent analysis. Mar Resour Econ 16:277–291

    Article  Google Scholar 

  • Jensen F, Vestergaard N (2002b) A principal-agent analysis of fisheries. J Inst Theor Econ 158:276–285

    Article  Google Scholar 

  • Jensen F, Vestergaard N (2002c) Moral hazard problems in fisheries regulation: the case of illegal landings and discard. Resour Energy Econ 24:281–299

    Article  Google Scholar 

  • Jensen F, Vestergaard N (2007) Asymmetric information and uncertainty: the usefulness of logbooks as a regulation measure. Ecol Econ 63:815–827

    Article  Google Scholar 

  • Walsh CE (1995) Optimal contracts for central bankers. Am Econ Rev 85:150–167

    Google Scholar 

  • World Bank (2009) The sunken Billions. The economic justification for fisheries reform. IBRD/WB, Washington DC, and FAO, Rome

Download references

Acknowledgments

The research on which this paper is based was conducted as part of the EC-FP7 funded project Making the European Fisheries Ecosystem Plan Operational (MEFEPO) (Project # 212881). We wish to thank all MEFEPO partner participants, and specifically Jesper Raakjaer, Innovative Fisheries Management, Aalborg University, Denmark, for constructive discussions and input. We also wish to thank two anonymous reviewers for insightful comments which have contributed to make the paper more relevant. All viewpoints and eventual errors are the responsibility of the authors.

Author information

Authors and Affiliations

Authors

Corresponding author

Correspondence to Margrethe Aanesen.

Appendix

Appendix

1.1 Regulators Moving Sequentially

Taking the derivative of \(\hbox {U}^{EU}\) in (10) w.r.t. E yields the optimal effort for the EU authorities, which is

$$\begin{aligned} E_{EU}^{S*} =\frac{r\left[ {qK\left( {\varGamma ^{EU}+\lambda \varGamma ^{F}} \right) -Q^{EU}-\lambda Q^{F}-\lambda w_1^*+\frac{\varGamma ^{N}+(1-\lambda )\varGamma ^{F}}{\varGamma ^{N}+\varGamma ^{F}}v_1^S } \right] }{2q^{2}K\left( {\varGamma ^{EU}+\lambda \varGamma ^{F}} \right) } \end{aligned}$$
(22)

The optimal effort level for the national authorities is found by maximising \(U^{N}\) w.r.t. E, and given (11), and is given by

$$\begin{aligned} E_N^{S*} =\frac{r\left[ {qK\left( {\varGamma ^{N}+\lambda \varGamma ^{F}} \right) -Q^{N}-\lambda Q^{F}\mp \left( {1-\lambda } \right) t_1^S -\lambda v_1^S } \right] }{2q^{2}K\left( {\varGamma ^{N}+\lambda \varGamma ^{F}} \right) } \end{aligned}$$
(23)

And the optimal effort for the fishers, given two regulators is

$$\begin{aligned} E_F^{**} =\frac{r\left[ {qK\varGamma ^{F}-Q^{F}-v_1^S -t_1^S } \right] }{2q^{2}K\varGamma ^{F}} \end{aligned}$$
(24)

Equalising (22) and (24) yields (13) and equalising (23) and (24) yields (14).

The explicit expressions for the optimal regulations are

$$\begin{aligned} v_1^{S*}&= -\frac{\varGamma ^{EU}\left( {\Gamma ^{N}+\varGamma ^{F}} \right) }{\varGamma ^{F}\left( {\Gamma ^{EU}+\Gamma ^{N}+\varGamma ^{F}}\right) }w_1^*+\frac{\left( {\Gamma ^{N}+\varGamma ^{F}} \right) \left( {Q^{EU}\Gamma ^{F}-\hbox {Q}^{F}\varGamma ^{EU}} \right) }{\varGamma ^{F}\left( {\Gamma ^{EU}+\Gamma ^{N}+\varGamma ^{F}} \right) }\end{aligned}$$
(25)
$$\begin{aligned} t_1^{S*}&= \frac{\left( {\varGamma ^{N}+\varGamma ^{F}} \right) \left( {\varGamma ^{EU}+\varGamma ^{F}} \right) }{\varGamma ^{F}\left( {\Gamma ^{EU}+\Gamma ^{N}+\varGamma ^{F}}\right) }w_1^*-\frac{\Gamma ^{N}\left( {Q^{EU}\Gamma ^{F}-\hbox {Q}^{F}\varGamma ^{EU}-\varGamma ^{EU}w_1^*} \right) }{\varGamma ^{F}\left( {\Gamma ^{EU}+\Gamma ^{N}+\varGamma ^{F}}\right) } \end{aligned}$$
(26)

1.2 Regulators Moving Simultaneously

The national authorities’ optimisation problem in the case of two regulators is now

$$\begin{aligned}&maxU^{N}=\beta _1^N \textit{PqKE}\left( {1-\frac{qE}{r}} \right) +\beta _2^N \left( {\textit{pqKE}\left( {1-\frac{qE}{r}} \right) -aE} \right) \nonumber \\&\quad \,+\,\beta _3^N SE+\rho \left( {t_0^C +t_1^C E} \right) .\end{aligned}$$
(27)
$$\begin{aligned}&\hbox {s.t}.\quad \beta _1^F PqKE\left( {1-\frac{qE}{r}} \right) +\beta _2^F \left( {\textit{pqKE}\left( {1-\frac{qE}{r}} \right) -aE} \right) \nonumber \\&\quad \,+\beta _3^F SE-\left( {t_0^C +t_1^C E} \right) -\left( {v_0^C +v_1^C E} \right) \ge 0\end{aligned}$$
(28)
$$\begin{aligned}&{\dot{X}}\equiv [F(X)-h(E,X)]=0 \end{aligned}$$
(29)

were we have kept the same share of the regulation revenue to national authorities, \(\uprho \), as in the previous examples.

Taking the derivative of \(\hbox {U}^{N}\) w.r.t. E yields the optimal effort for the national authorities, which is

$$\begin{aligned} E_N^{C*} =\frac{r\left[ {qK\left( {\varGamma ^{N}+\lambda \varGamma ^{F}} \right) -Q^{N}-\lambda Q^{F}+(1-\lambda )t_1^C -\lambda v_1^C } \right] }{2q^{2}K\left( {\varGamma ^{N}+\lambda \varGamma ^{F}} \right) } \end{aligned}$$
(30)

The optimal effort level for the EU authorities is given by

$$\begin{aligned} E_{EU}^{C*} =\frac{r\left[ {qK\left( {\varGamma ^{EU}+\lambda \varGamma ^{F}} \right) -Q^{EU}-\lambda Q^{F}+(1-\lambda )v_1^C -\lambda t_1^C } \right] }{2q^{2}K\left( {\varGamma ^{EU}+\lambda \varGamma ^{F}} \right) } \end{aligned}$$
(31)

And the optimal effort for the fishers, given two regulators is

$$\begin{aligned} E_F^{**} =\frac{r\left[ {qK\varGamma ^{F}-Q^{F}-v_1^C -t_1^C } \right] }{2q^{2}K\varGamma ^{F}} \end{aligned}$$
(32)

The explicit expressions for the optimal regulations when there are two regulators are:

$$\begin{aligned} t_1^{C*}&= \frac{Q^{N}\varGamma ^{EU}-Q^{EU}\varGamma ^{N}+Q^{N}\varGamma ^{F}-Q^{F}\varGamma ^{N}}{\left( {\Gamma ^{EU}+\Gamma ^{N}+\varGamma ^{F}} \right) }\end{aligned}$$
(33)
$$\begin{aligned} v_1^{C*}&= \frac{Q^{EU}\varGamma ^{N}-Q^{N}\varGamma ^{EU}+Q^{EU}\varGamma ^{F}-Q^{F}\varGamma ^{EU}}{\left( {\Gamma ^{EU}+\Gamma ^{N}+\varGamma ^{F}} \right) } \end{aligned}$$
(34)

Rights and permissions

Reprints and permissions

About this article

Check for updates. Verify currency and authenticity via CrossMark

Cite this article

Aanesen, M., Armstrong, C.W. The Political Game of European Fisheries Management. Environ Resource Econ 63, 745–763 (2016). https://doi.org/10.1007/s10640-015-9878-0

Download citation

  • Accepted:

  • Published:

  • Issue Date:

  • DOI: https://doi.org/10.1007/s10640-015-9878-0

Keywords

JEL Classification

Navigation