Abstract
Preventing pollution is the best way to protect the marine environment. Because pollution will never be totally eliminated, compensation for pollution damage is an important form of protection. Compensation is necessary for environmental restoration, but it also functions as a deterrent, and thus, has a preventive effect. The polluter-pays-principle, a main concept in environmental law,1 embodies the concept of compensation.
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References
This principle is reflected in Article 3 paragraph 4 Helsinki Convention (Convention on the Protection of the Marine Environment of the Baltic Sea Area, 1992, text published in BGBl. 1994 II p. 1397), Article 2 paragraph 2 (b) OSPAR Convention (Convention for the Protection of the Marine Environment of the North-East Atlantic, text published in BGBl. 1994 II p. 1360); its objective is to channel the costs of prevention and reparation of environmental damage to the person who is in the best position to prevent such damage and to internalize the costs of pollution damage, see Liability & compensation regimes related to environmental damage: Review by UNEP-Secretariat, p. 27 et seq., 103, available from <www.unep.org/depi/liability and compensation.asp>.
Concerning domestic German law see Erbguth, Entwicklungen der Umwelthaftung: Ansätze eines Haftungsregimes für die Verschmutzung der Meere im deutschen Recht, in: 1. Rostocker Gespräch zum Seerecht — Aktuelle Probleme der Haftung für Schäden aus der Meeresverschmutzung, Schriften des Deutschen Vereins für internationales Seerecht, Reihe A, Heft 84; cf. also Bussek, Schutz der Meere vor Verschmutzung, p. 82 et seq.
Article 1(4) UNCLOS (United Nations Convention on the Law of the Sea, BGBl. 1994 II p. 1798).
For a detailed description of pollution sources and their impacts on the marine environment see OSPAR Commission, Quality Status Report for the North-East Atlantic, 2000; Helsinki Commission, The Baltic Marine Environment 1999–2002, Baltic Sea Environment Proceedings No. 87; cf. Ehlers, The Baltic Sea — Threats and Future Priorities, in: Maritime Safety — Current Problems of Use of the Baltic Sea, European Association of Legislation, ed. by Karpen, Vol. 11 (2005) 13 et seq.
This distinction is made by de La Fayette, Compensation for Environmental Damage in Maritime Liability Regimes, in: International Maritime Environmental Law, ed. by Kirchner (2003) 262; European Commission, White Paper on environmental liability, COM (2000) 66 final, p.16 et seq.
White paper (Note 5 supra).
UNEP (Note 1 supra) 27, defines environmental damage as a change that has a measurable adverse impact on the quality of a particular environment or any of its components, including its use and non-use values, and its ability to support and sustain an acceptable quality of life and a viable ecological balance.
See Directive 2004/35/EC, Preamble, paragraph 15, OJ 2004 L 143, p. 56; cf. White Paper (Note 5 supra) 28.
Cf. Balkin, Some Future Developments in Liability and Compensation for Environmental Damage at Sea, in: The Stockholm Declaration and Law of the Marine Environment, ed. by Nordquist/Moore/Mahmoudi (2003) 437.
BGBl. 1993 II p. 1741.
Cartagena Protocol on Biosafety, BGBl. 2003 II p. 1506.
Convention on the Control of Transboundary Movements of Hazardous Wastes and their Disposal, BGBl. 1994 II p. 2703; 2002 II p. 89; 2003 II p. 1626.
Convention on the Prevention of Marine Pollution by Dumping of Wastes and other Matter, 1972, BGBl. 1977 II p. 180.
Article X; de La Fayette, (Note 5 supra) 232, points out that the Contracting Parties have decided that no liability regime is necessary as all dumping of hazardous substances has theoretically been phased out.
For details see UNEP (Note 1 supra) 94 et seq.
CLC; BGBl. 1996 II p. 670; 2002 II p. 943.
Fund Convention, BGBl. 1996 II p. 685; 2002 II p. 943.
HNS Convention, OJ 2002 L 337, p. 55.
Bunkers Convention, OJ L 2002 256, p. 7.
For more details see UNEP (Note 1 supra) 34 et seq., 38, 41; de La Fayette (Note 5 supra) 236 et seq.; Balkin (Note 9 supra) 438 et seq.
See Gehring/Jachtenfuchs, Haftung und Umwelt — Interessenkonflikte im internationalen Weltraum-, Atom-und Seerecht (1988) 195; Gündling, Ölunfälle bei der Ausbeutung des Festlandsockels — Zur Verschmutzung der Meere und ihrer völkerrechtlichen Kontrolle: ZaöRV 1977, 563; UNEP (Note 1 supra) 43.
The agreement is available at <www.opol.org.uk>; for further details see Swan, Ocean Oil and Gas Drilling and the Law (1979) 181 et seq.; Gehring/Jachtenfuchs (Note 27 supra); Bussek (Note 2 supra) 75 et seq.
See for these examples Swan (Note 24 supra) 344.
Convention on Civil Liability for Damage resulting from Activities Dangerous to the Environment, Council of Europe, European Treaty Series No. 150; cf. White Paper (Note 5 supra) 52.
See UNEP (Note 1 supra) 44 et seq.; White Paper (Note 5 supra) 52.
For details see White Paper (Note 5 supra) 25 et seq.
Directive 2004/35/EC of 21 April 2004, OJ 2004 L 143, p. 56; for details see Becker, Einführung in die Richtlinie über Umwelthaftung zur Vermeidung und Sanierung von Umweltschäden: NVwZ 2005, 371 et seq.
Article 2(2); this definition is in line with the proposal made by an UNEP expert group, cf. UNEP (Note 1 supra) 5.
However, the definition of damage to protected species and natural habitats does not include adverse effects resulting from expressly authorised acts, Article 2(1)(a); cf. Becker Einführung in die Richtlinie über Umwelthaftung zur Vermeidung und Sanierung von Umweltschäden: NVwZ 2005 (Note 52 supra) 373.
Directive 2000/60/EC of the European Parliament and of the Council of 23 October 2000 establishing a framework for Community action in the field of water policy, OJ 2000 L 327, p. 1.
Directive 79/409/EEC of 2 April 1979, OJ 1979 L 103, p. 1.
Directive 92/43/EEC of 21 May 1992, OJ 1992 L 206, p. 7.
Article 8(4); as far as adverse effects to protected species or natural habitats are concerned the damage itself may be negated in case of authorised activities, cf. Einführung in die Richtlinie über Umwelthaftung zur Vermeidung und Sanierung von Umweltschäden: NVwZ 2005 373 supra Note 56.
In this context neither the compensation schemes for nuclear damage nor for damage from seabed mining, based on Part XI of UNCLOS, are taken into consideration; see for information de La Fayette (Note 5 supra) 249 ff., 253 ff.; Bothe, The Protection of the Marine Environment against the Impacts of Seabed Mining: An Assessment of the New Mining Code of the International Seabed Authority, in: Marine Issues — From a Scientific, Political and Legal Perspective, ed by. Ehlers/Mann-Borgese/Wolfrum (2002) 229 et seq.
This situation is also critizised by de La Fayette (Note 5 supra) 232.
As concerns the problems related to compensation regulations on the high seas cf. Bussek (Note 2 supra) 110.
Cf. Notes 60 and 61 supra.
For criteria to be developed cf. UNEP (Note 1 supra) 117.
Cf. UNEP (Note 1 supra) 110 et seq.
Rightly UNEP (Note 1 supra) 103, points out that this represents a major gap in liability agreements.
Cf. Einführung in die Richtlinie über Umwelthaftung zur Vermeidung und Sanierung von Umweltschäden: NVwZ 2005, 373 Note 56 supra.
Paragraph 4 subparagraph 2 no. 2 a and 3 Federal Water Act, BGBl. 2002 I p. 3167; cf. Hoffmeister/Kokott, Öffentlich-rechtlicher Ausgleich für Umweltschäden in Deutschland und in hoheitsfreien Räumen, Berichte 9/02 des Umweltbundesamtes, p. 91.
Cf. Note 2 supra 3.
UNEP (Note 1 supra) 117, supports the idea of a fund, established by either State or industry as a method of collective reparation in case that restoration measures are not technically feasable or reasonable.
At least in principle such a fee system would be comparable to the German Federal Water Fee Act; cf. Hoffmeister/ Kokott (Note 77 supra) 93.
See Bussek (Note 2 supra) 106 et seq., 122, who proposes a “blanket allowance” for the preservation of the seas.
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Ehlers, P. (2007). Origins and Compensation of Marine Pollution — A Survey. In: Basedow, J., Magnus, U. (eds) Pollution of the Sea — Prevention and Compensation. Hamburg Studies on Maritime Affairs, vol 10. Springer, Berlin, Heidelberg. https://doi.org/10.1007/978-3-540-73396-6_9
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