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Distribution of antifouling biocides in a coastal area of Tanabe Bay, Japan

Published online by Cambridge University Press:  15 February 2021

Hiroya Harino Open the ORCID record for Hiroya Harino [Opens in a new window]  and
Shigeyuki Yamato
Hiroya Harino*
Affiliation:
Department of Human Sciences, Kobe College, Okadayama 4-1, Nishinomiya, Hyogo662-8505, Japan
Shigeyuki Yamato
Affiliation:
Seto Marine Biological Laboratory, Kyoto University, Shirahama 459, Nishimuro, Wakayama649-2211, Japan
*
Author for correspondence: Hiroya Harino, E-mail: harino@mail.kobe-c.ac.jp
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Abstract

Tributyltin (TBT) and triphenyltin (TPT) concentrations in water samples from Tanabe Bay were found to range from 4–28 ng l−1 and 3–7 ng l−1, respectively. In fishing ports, the concentrations of TBT in surface water were similar to those in bottom water. However, in aquafarming areas with poor flushing, the concentrations of TBT in bottom water were higher than those in surface water. This suggested that the TBT in water samples is re-eluted from sediment. No difference in the concentration of TPT was observed between the surface and bottom waters. The concentrations of TBT and TPT in sediment samples ranged from 3–23 μg kg−1 dry weight and 2–37 μg kg−1 dry weight. TBT and TPT concentrations ranged from 3.1–100 μg kg−1 and 3.1–7.2 μg kg−1 in oysters and gastropods, and from 1.1–4.9 μg kg−1 and ＜0.2–3.9 μg kg−1 in fish, respectively. Organotin concentrations in biota were lower than the tolerable average residue levels (TARLs). Alternative biocides – i.e. diuron, chlorothalonil, dichlofluanid, irgarol 1051 and Sea-Nine 211 – were also detected in surface water, and chlorothalonil and irgarol 1051 were detected in sediment. The concentrations of these compounds in surface water and sediment were lower than those reported previously. Dichlofluanid, chlorotharonil and irgarol 1051 were also found at low levels in oysters and gastropods, and at ranges of 325–339 μg kg−1, 268–291 μg kg−1 and 43–49 μg kg−1, respectively, in fish; the concentrations in fish were close to the TARL levels.

Keywords

Alternative biocidesbiological samplesorganotin compoundssediment sampleswater samples
Type
Research Article
Information
Journal of the Marine Biological Association of the United Kingdom , Volume 101 , Issue 1 , February 2021 , pp. 49 - 59
Copyright
Copyright © The Author(s), 2021. Published by Cambridge University Press on behalf of Marine Biological Association of the United Kingdom†

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Footnotes

†

The online version of this article has been updated since original publication. A notice detailing the changes has also been published.

References

Anastasiou, TI, Chatzinikolaou, E, Mandalakis, M and Arvanitidis, C (2016) Imposex and organotin compounds in ports of the Mediterranean and the Atlantic: is the story over? Science of the Total Environment 569–570, 1315–1329.CrossRefGoogle ScholarPubMed
Batista-Andrade, JA, Caldas, SS, Batista, RM, Castro, IB, Fillamann, G and Primel, EG (2018) From TBT to booster biocides: levels and impacts of antifouling along coastal areas of Panama. Environmental Pollution 234, 243–252.CrossRefGoogle ScholarPubMed
Batley, GE, Fuhua, C, Brockbank, CI and Flegg, KJ (1989) Accumulation of tributyltin by the Sydney rock oyster Saccostrea commercialis. Australian Journal Marine Freshwater Research 40, 49–54.CrossRefGoogle Scholar
Cavalheiro, J, Sola, C, Baldanza, J, Tessier, E, Lestremau, F, Botta, F, Preud'homme, H, Monperrus, M and Amouroux, D (2016) Assessment of background concentrations of organometallic compounds (methylmercury, ethyllead and butyl- and phenyltin) in French aquatic environments. Water Research 94, 32–41.CrossRefGoogle ScholarPubMed
de Mora, SJ, King, NG and Miller, MC (1989) Tributyltin and total tin in marine sediment profiles and the apparent rate of TBT degradation. Environmental Technology Letter 10, 901–908.CrossRefGoogle Scholar
de Oliveira, CR, dos Santos, DM, dos Madueira, LAS and de Marchi, MRR (2010) Speciation of butyltin derivatives in surface sediments of three southern Brazilian harbours. Journal of Hazardous Materials 181, 851–856.CrossRefGoogle Scholar
Deng, L, Liu, C-H, Zheang, H-M and Xu, H-L (2015) Levels and assessment of organotin contamination at Futian mangrove wetland in Shenzhen, China. Regional Studies in Marine Science 1, 18–24.CrossRefGoogle Scholar
Dowson, PH, Bubb, JM, Williams, TP and Lester, JN (1993) Degradation of tributyltin in sediment in freshwater and estuarine marina sediments. Water Science Technology 28, 133–137.CrossRefGoogle Scholar
Environmental Agency (2011) Available at https://www.env.go.jp/water/heisa/heisa_net/waters/tanabewan.html/ (Accessed 21 December 2020). (In Japanese.)Google Scholar
Evans, DA and Huggett, RJ (1991) Statistical modeling of intensive TBT monitoring data in two tidal creeks of the Chesapeake Bay. Marine Environmental Research 32, 169–186.CrossRefGoogle Scholar
Fernández-Alba, AR, Hernando, MD, Piedra, L and Chisti, Y (2002) Toxicity evaluation of single and mixed antifouling biocides measured with acute toxicity bioassays. Analytica Chimica Acta 456, 303–312.CrossRefGoogle Scholar
Fisheries Agency (2018) Available at https://www.jfa.maff.go.jp/j/kikaku/wpaper/h29_h/trend/1/t1_2_4_2.html/ (Accessed 21 December 2020). (In Japanese.)Google Scholar
Furdek, M, Vahcic, M, Scancar, J, Milacic, R, Kniewald, G and Mikac, N (2012) Organotin compounds in seawater and Mytilus galloprovincialis mussels along the Croatian Adriatic coast. Marine Pollution Bulletin 64, 189–199.CrossRefGoogle ScholarPubMed
Gao, J-M, Wu, L, Chen, Y-P, Zhou, B, Guo, J-S, Zhang, K and Ouyang, W-J (2017) Spatiotemporal distribution and risk assessment of organotins in the surface water of the Three Gorges Reservoir region, China. Chemosphere 171, 405–414.CrossRefGoogle ScholarPubMed
Gibbs, PE and Bryan, GW (1986) Reproductive failure in populations of the dog-whelk, Nucella lapillus caused by imposex induced by tributyltin from antifouling paints. Journal of the Marine Biological Association of the United Kingdom 66, 767–777.CrossRefGoogle Scholar
Gibbs, PE, Spencer, BE and Pascoe, PL (1991) The American oyster drill, Urosalpinx cunerea (Gastropoda): evidence of decline in an imposex-affected population (R. Blackwater, Essex). Journal of the Marine Biological Association of the United Kingdom 71, 827–838.CrossRefGoogle Scholar
Harino, H (2004) Occurrence and degradation of representative TBT free-antifouling biocides in aquatic environment. Coastal Marine Science 29, 28–39.Google Scholar
Harino, H (2016) Emerging issues on contamination and adverse effects by alternative antifouling paints in the marine environments. In Horiguchi, T (ed.), Biological Effects by Organotin. Tokyo: Springer, pp. 43–70.Google Scholar
Harino, H, Fukushima, M, Yamamoto, Y, Kawai, S and Miyazaki, N (1998) Organotin compounds in water, sediment, and biological samples from the Port of Osaka, Japan. Archives of Environmental Contamination and Toxicology 35, 558–564.CrossRefGoogle ScholarPubMed
Harino, H, Fukushima, M and Kawai, S (2000) Accumulation of butyltin and phenyltin compounds in fish species. Archives of Environmental Contamination and Toxicology 39, 13–19.CrossRefGoogle ScholarPubMed
Harino, H, Yamamoto, Y, Kawai, S and Miyazaki, N (2003) Butyltin and phenyltin residues in water, sediment and biological samples collected from Otsuchi Bay, Japan. Otsuchi Marine Science 28, 84–90.Google Scholar
Harino, H, Mori, Y, Yamaguchi, Y, Shibata, K and Senda, T (2005) Monitoring of antifouling booster biocides in water and sediment from the port of Osaka, Japan. Archives of Environmental Contamination and Toxicology 48, 303–310.CrossRefGoogle ScholarPubMed
Harino, H, Eguchi, S and Yamamoto, Y (2010) Concentrations of antifouling biocide in mussel and oyster from Awaji Island, Japan. Kobe College Study 57, 12–23. (In Japanese.)Google Scholar
Horiguchi, T, Shiraishi, H, Shimizu, M, Yamazaki, S and Morita, M (1995) Imposex in Japanese gastropods (Neogastropoda and Mesogastropoda): effects of tributyltin and triphenyltin from antifouling paints. Marine Pollution Bulletin 31, 402–405.CrossRefGoogle Scholar
Jadhav, S, Bhaosale, D and Bhosle, N (2011) Baseline of organotin pollution in fishes, clams, shrimps, squids and crabs collected from the west coast of India. Marine Pollution Bulletin 62, 2213–2219.CrossRefGoogle ScholarPubMed
Kobayashi, K, Yamato, S, Harino, H and Kitano, M (2008) A bioassay using sea urchin egg development to identify organotin pollution in sea water. Coastal Marine Science 32, 77–81.Google Scholar
Koutsaftis, A and Aoyama, I (2007) Toxicity of four antifouling biocides and their mixutures on the brine shrimp Artemia salina. Science of Total Environment 387, 166–174.CrossRefGoogle ScholarPubMed
Langston, WJ, O'Hara, S, Pope, ND, Davey, M, Shortridge, E, Immamura, M, Harino, H, Kim, A and Vane, CH (2012) Bioaccumulation surveillance in Milford Haven waterway. Environmental Monitoring Assessment 184, 289–311.CrossRefGoogle ScholarPubMed
Law, RJ, Waldock, JJ, Allxhin, CR, Laslett, RE and Bailey, KJ (1994) Contaminants in seawaer around England and Wales: results from monitoring surveys. Marine Pollution Bulletin 28, 668–675.CrossRefGoogle Scholar
Lee, M-R-N, Kim, U-J, Lee, I-S, Choi, M and Oh, J-E (2015) Assessment of organotin and tin-free antifouling paints contamination in the Korean coastal area. Marine Pollution Bulletin 99, 157–165.CrossRefGoogle ScholarPubMed
Liu, D, Pacepavicius, GJ, Maguire, RJ, Lau, YL, Okamura, H and Aoyama, I (1997) Transformation of the new antifouling compound irgarol 1051 by Phanerochaete chrysosporium. Water Research 31, 2363–2369.CrossRefGoogle Scholar
Liu, L-L, Wang, J-T, Chung, K-N, Leu, M-Y and Meng, P-J (2011) Distribution and accumulation of organotin species in seawater, sediments and organisms collected from a Taiwan mariculture area. Marine Pollution Bulletin 63, 535–540.CrossRefGoogle ScholarPubMed
Maguire, RJ and Tkacz, RJ (1985) Degradation of the tri-n-butyltin species in water and sediment from Toronto harbour. Journal of Agriculture and Food Chemistry 33, 947–953.CrossRefGoogle Scholar
Midorikawa, S, Arai, T, Harino, H, Ohji, M, Duc Cu, N and Miyazaki, N (2004) Concentrations of orgnotin compounds in sediment and clams collected from coastal areas in Vietnam. Environmental Pollution 131, 401–408.CrossRefGoogle ScholarPubMed
Okamura, H, Aoyama, I, Liu, D, Maguire, J, Pacepavicius, GJ and Lau, Y (1999) Photodegradation of irgarol 1051 in water. Journal of Environmental Science and Health B34, 225–238.CrossRefGoogle Scholar
Penninks, AH (1993) The evaluation of data-derived safety factors for bis (tri-n-butyl) tin in marine sediments near Auckland, New Zealand. Food Additives and Contaminants 10, 351–361.CrossRefGoogle Scholar
Radke, B, Wasik, A, Jewell, LL, Piketh, SJ, Pączek, U, Gałuszka, A and Namieśnik, J (2012) Seasonal changes in organotin compounds in water and sediment samples from the semi-closed port of Gdynia. Science of the Total Environment 441, 57–66.CrossRefGoogle ScholarPubMed
Shim, WJ, Oh, JR, Kahng, SH, Shim, JH and Lee, SH (1998) Accumulation of tribytyl and triphenyltin compounds in Pacific oyster, Crassostrea gigas, from the Chinhae Bay system, Korea. Archives of Environmental Contamination and Toxicology 35, 41–45.CrossRefGoogle ScholarPubMed
Takahashi, S, Tanabe, S, Takeuchi, I and Miyazaki, N (1999) Distribution and specific bioaccumulation of butyltin compounds in a marine ecosystem. Archives of Environmental Contamination and Toxicology 37, 50–61.CrossRefGoogle Scholar
Virkirs, AO, Davidson, B, Kear, LL and Fransham, RL (1991) Long-term monitoring of tributyltin in San Diego Bay, California. Marine Environmental Research 32, 151–167.Google Scholar