Marine Environmental Risk Assessment Method for Active Substances Used in Antifouling Systems on Ships in China

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A Chinese risk assessment procedure was developed to address active substances used in biologically active (biocidal) antifouling paints. The priority was to promote the use of environmentally friendly, technically and economically viable alternatives to DDT/TBT (dichlorodiphenyltrichloroethane/tributyltin) in the control of marine fouling organisms. The procedure was based upon European Union Biocide Product Directive (EU-BPD) and International Standard Organization (ISO) method for the Environmental risk assessment of antifouling systems. In order to focus on Chinese national conditions, international templates were adapted to address regional differences. In the Chinese method, persistence, bioaccumulation and toxicity information is assessed on a step by step basis, allowing an antifouling substance to be defined as either Risk of high concern or Relatively low risk at the end of the decision making process. 4,5-Dichloro-2-n-Octyl-3-Isothiazolinone (DCOIT, Sea-nine), triphenylborane pyridine (TPBP), 8-methyl-N-vanillyl-6-nonenamide (Capsaicin) and Zinc ethylene (bis) dithiocarbamate (Zineb), popularly used in China as active substance of antifouling paints, were reviewed according to the developed procedure. The preliminary results indicate that Sea-nine use in antifouling products can be considered low risk, whereas TPBP, Capsaicin and Zineb failed the screening procedure on the basis of bioaccumulation potential, persistence and an unacceptable risk ratio, respectively. Data availability was determined to be a critical factor in the assessments due to the application of Safety Factors for data-poor substances.

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Advanced Materials Research (Volumes 864-867)

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962-972

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December 2013

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© 2014 Trans Tech Publications Ltd. All Rights Reserved

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[1] K.V. Thomas and S. Brooks: Biofouling, Vol. 26 (2010), pp.73-88.

Google Scholar

[2] M.Y. Diego, S. Kiil and K.D. Johansen: Progress in organic coating, Vol. 50 (2004), pp.75-104.

Google Scholar

[3] UNDP:Stockholm convention on persistent organic pollutants (POPs) (2001).

Google Scholar

[4] M.A. Champ: Sci. Total Environ. Vol. 258 (2000), pp.21-71.

Google Scholar

[5] E. Yoshikawa, K. Namekawa, N. Nagai, K. Shibata, and T. Senda. Research for the risk assessment of anti-fouling system. Shipbuild. Technol. ISST 2007, pp.107-116.

Google Scholar

[6] European Commission. Technical Guidance Document on Risk Assessment in support of Commission Directive 93/67/EEC on Risk Assessment for new notified substances, Commission Regulation (EC) No 1488/94 on Risk Assessment for existing substances and Directive 98/8/EC of the European Parliament and of the Council concerning the placing of biocidal products on the market. 2003, Part IV.

DOI: 10.1002/352760197x.app1

Google Scholar

[7] ISO/TC 8/SC 2. Marine environment protection – Risk assessment on anti-fouling systems on ships – Part 1: Marine environmental risk assessment method on active substances used for anti-fouling systems on ships.

DOI: 10.3403/30213206

Google Scholar

[8] United nations: Globally Harmonised System for the Classification and Labelling of Chemicals (GHS). Guidance on Hazards to the Aquatic Environment–Degradation, 2009, Annex 9, Section A9. 4.

DOI: 10.18356/f259c5bc-en

Google Scholar

[9] State Environmental Protection Administration of China: The guidelines for the testing chemicals-301: Ready biodegradability (Chinese Environmental Science Publishing House, Beijing 2004).

Google Scholar

[10] OECD: OECD Guideline for the Testing of Chemicals, 301 Ready Biodegradability, Paris, (1992).

Google Scholar

[11] State General Administration of the People's Republic of China for Quality Supervision and Inspection and Quarantine (2008), National Standard of the People's Republic of China, GB/T 21815. 1-(2008).

Google Scholar

[12] OECD: Biodegradability in Seawater. Organisation for Economic Cooperation and Development (OECD), OECD Guideline for the Testing of Chemicals No. 306, Paris, (1992).

Google Scholar

[13] OECD: Aerobic Mineralisation in surface water – simulation biodegradation test. Organisation for Economic Cooperation and Development (OECD), OECD Guideline for the Testing of Chemicals No. 309, Paris, September (2001).

DOI: 10.1787/9789264070547-en

Google Scholar

[14] European Chemicals Agency. Guidance on information requirements and chemical safety assessment Chapter R. 11: PBT Assessment. (2008).

Google Scholar

[15] ISO/DIS 10890. 2 Paints and varnishes-modelling of biocide release rate from antifouling paints by mass-balance calculation, (2009).

DOI: 10.3403/30174914u

Google Scholar

[16] U.S. Environmental Protection Agency, in: Overall Summary of Triphenylboron Category. 2003, 201-14976A.

Google Scholar

[17] X.J. Zhou; H. Okamura and S. Nagata. Abiotic degradation of triphenylborane pyridine (TPBP) antifouling agent in water. Chemosphere Vol. 67 (2007), p.1904-(1910).

DOI: 10.1016/j.chemosphere.2006.12.007

Google Scholar

[18] C.J. Van Leeuwen, J.L. Maas-Diepeveen, G. Niebeek et al. Aquatic toxicological aspects of dithiocarbamates and related compounds. I. Short-term toxicity tests; Aquat. Toxicol. Vol. 7 (1985), pp.145-164.

DOI: 10.1016/s0166-445x(85)80002-3

Google Scholar

[19] Ma et al. Differential Sensitivity of Two Green Algae, Scenedesmus obliqnus and Chlorella pyrenoidosa, to 12 Pesticides. Ecotoxicol. Environ. Safety Vol. 52 ( 2002), pp.57-61.

DOI: 10.1006/eesa.2002.2146

Google Scholar

[20] A. Arrhenius, T. Backhaus, F. Gronvall, M. Junghans, M. Scholze, and H. Blanck. Effects of Three Antifouling Agents on Algal Communities and Algal Reproduction: Mixture Toxicity Studies with TBT, Irgarol, and Sea-Nine. Arch. Environ. Contam. Toxicol. Vol. 50 (2006).

DOI: 10.1007/s00244-005-1057-9

Google Scholar

[21] U.S. EPA. Office of Pesticide Programs. Environmental Fate and Effects Division: Washington, D.C., (2000).

Google Scholar

[22] C.J. Van Leeuwen, F. Moberts, and G. Niebeek. Aquatic toxicological aspects of dithiocarbamates and related compounds. II. Effects on survival, reproduction and growth of Daphnia magna; Aquat Toxicol. Vol. 7 (1985), pp.165-175.

DOI: 10.1016/s0166-445x(85)80003-5

Google Scholar

[23] J. Bellas. Toxicity of the booster biocide Sea-Nine to the early developmental stages of the sea urchin Paracentrotus lividus; Aquat. Toxicol. Vol. 83 (2007), pp.52-61.

DOI: 10.1016/j.aquatox.2007.03.011

Google Scholar

[24] M.E. Callow and G.L. Willingham. Degradation of antifouling biocides. Biofouling. Vol. 10 (1996), pp.239-249.

DOI: 10.1080/08927019609386283

Google Scholar

[25] A.H. Jacobson and G.L. Willingham. Sea-nine antifoulant: an environmentally acceptable alternative to organotin antifoulants. Sci. Total Environ. Vol. 258 (2000), pp.103-110.

DOI: 10.1016/s0048-9697(00)00511-8

Google Scholar

[26] K.V. Thomas, M. McHugh and M. Waldock. Antifouling paint booster biocides in UK coastal waters: inputs, occurrence and environmental fate. Sci. Total. Environ. Vol. 293 (2002), pp.117-127.

DOI: 10.1016/s0048-9697(01)01153-6

Google Scholar

[27] K.V. Thomas, M. McHugh, M. Hilton and M. Waldock. Increased persistence of antifouling paint biocides associated with paint particles. Environ. Pollut. Vol. 123 (2003), pp.153-161.

DOI: 10.1016/s0269-7491(02)00343-3

Google Scholar

[28] I.K. Konstantinou and T.A. Albanis Worldwide occurrence and effects of antifouling paint booster biocides in the aquatic environment. Environ. International. Vol. 30 (2004), pp.235-248.

DOI: 10.1016/s0160-4120(03)00176-4

Google Scholar

[29] A.S. Wasilions, K.K. Ioannis, A.L. Dimitra and A.A. Triantafyllos. Survey for the Occurrence of Antifouling Paint Booster Biocides in the Aquatic Environment of Greece. Environ. Sci. & Pollut. Res., Vol. 9 (2002), pp.327-332.

DOI: 10.1007/bf02987576

Google Scholar

[30] K.V. Thomas and S. Brooks. The environmental fate and effects of antifouling paints biocides. Biofouling. Vol. 26 (2010), pp.73-88.

DOI: 10.1080/08927010903216564

Google Scholar

[31] K.V. Thomas, T.W. Fileman, J.W. Readman and M.J. Waldock. Antifouling paint booster biocides in the UK coastal environment and potential risks of biological effects. Mar. Pollut. Bull. Vol. 42(2001), pp.677-688.

DOI: 10.1016/s0025-326x(00)00216-2

Google Scholar

[32] R.L. Amey and C. Waldron. Ptriphenylboron-pyridine, a non-metal antifouling biocide, in: Proceedings of the International Symposium on Antifouling Paint and Marine Environment, Tokyo, Japan. Efficacy and Chemistry of BOROCIDETM (2004).

Google Scholar

[33] H. Okamura,S. Kitano,S. Toyota,H. Harino and K.V. Thomas. Ecotoxicity of the degradation products of triphenylborane pyridine (TPBP) antifouling agent. Chemosphere. Vol. 74 (2009), 1275-1278.

DOI: 10.1016/j.chemosphere.2008.11.014

Google Scholar

[34] U.S. EPA. Office of Pesticide Programs Special Review and Re-registration Division. Re-registration eligibility document-capsaicin: Washington, D.C., (1992).

Google Scholar

[35] Hazardous Substances Data Bank (HSDB), Capsaicin; U.S. Department of Health and Human Services, National Institutes of Health, National Library of Medicine: Bethesda, MD, (2006).

Google Scholar

[36] A. Akagi, N. Sano, H. Uehara, T. Minami, H. Otsuka and K. Izumi. Non-carcinogencity of capsaicinoids in B6C3F1 mice. Food Chem. Toxicol. Vol. 36(1998), pp.1065-1071.

DOI: 10.1016/s0278-6915(98)00077-5

Google Scholar

[37] W.G. Cope, M.R. Bartsch and L.L. Marking. Efficacy of Candidate Chemicals for Preventing Attachment of Zebra Mussels (Dreissena polymorpha). Environ. Toxicol. Chem. Vol. 16 (1997), p.1930-(1934).

DOI: 10.1002/etc.5620160923

Google Scholar

[38] K.W. Wessmahr and D.L. Sedlak. Effect of metal complexation on the degradation of dithiocarbamate fugicides. Environ. Toxicol. Chem. Vol. 19 (2000), pp.820-826.

DOI: 10.1002/etc.5620190406

Google Scholar

[39] M.A. Klisenko and M.S. Vekshtein. Kinetics of the hydrolysis of metal derivatives of dialkyldithiocarbamic and ethylenebisdithiocarbamic acids in their dependence on the pH of the medium, and the identification of their transformation products. Zhurnal obshchei Khimmii. Vol. 41 (1971).

Google Scholar

[40] J.E. Hunter and L.V. Evans. The toxicity of the biocides zineb, nabam and their derivatives to the ship-fouling diatom Amphora coffeaeformis. Biofouling. Vol. 2 (1990), pp.267-287.

DOI: 10.1080/08927019009378150

Google Scholar

[41] H. Kidd: The Agrochemicals Handbook, Third Edition. (Royal Society of Chemistry Information Services, Cambridge. UK. 1991).

Google Scholar

[42] N. Voulvoulis, M.D. Scrimshaw and J.N. Lester. Comparative environmental assessment of biocides used in antifouling paints. Chemosphere. Vol. 47 (2002) , pp.789-795.

DOI: 10.1016/s0045-6535(01)00336-8

Google Scholar