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Current status of organophosphorus compounds contamination in Maizuru Bay, Japan

Published online by Cambridge University Press:  15 October 2013

Hiroya Harino*
Affiliation:
Department of Human Sciences, Kobe College, Okadayama 4-1, Nishinomiya, Hyogo 662-0827, Japan
Emi Yatsuzuka
Affiliation:
Department of Human Sciences, Kobe College, Okadayama 4-1, Nishinomiya, Hyogo 662-0827, Japan
Chiaki Yamao
Affiliation:
Department of Human Sciences, Kobe College, Okadayama 4-1, Nishinomiya, Hyogo 662-0827, Japan
Masaaki Ueno
Affiliation:
Maizuru Fisheries Research Station, Kyoto University, Nagahama, Maizuru, Kyoto 625-0086, Japan
Madoka Ohji
Affiliation:
Institute of Symbiotic Science and Technology, Tokyo University of Agriculture and Technology, Fuchu, Tokyo 183-8509, Japan
*
Correspondence should be addressed to: H. Harino, Department of Human Sciences, Kobe College, Okadayama 4-1, Nishinomiya, Hyogo 662-0827, Japan email: harino@mail.kobe-c.ac.jp

Abstract

The concentrations of organophosphoric acid triesters (OPEs) in water samples from Maizuru Bay were in the range of 3.0–62 ng/l. In general, the concentrations of OPEs were found in the order of TBXP > TDCPP > TCEP > TBP > TCP > TPP > TEP. The organophosphorous pesticides (OPPs) diazinon, fenitrothion, iprobenfos and chlorpyrifos were detected in water samples. The concentrations of OPEs in sediment from Maizuru Bay were in the range of <0.5–56 µg kg−1 dry weight (dw). Among OPPs, diazinon in sediment samples were in the range of 1.8–71 µg kg−1 dw. However, the detection frequencies of fenitrothion and chlorpyrifos in sediment were low. The concentrations of OPEs in mussels from Maizuru Bay were in the range of <1–34 µg kg−1 wet weight (ww). The concentrations of OPEs were found in the order of TBP > TDCPP > TCP > TBXP = TPP = TCEP. Pesticides were detected in mussels, but these concentrations were lower than the acceptable daily intake (ADI) values. The partition coefficients between water and sediment (Kws) of diazinon and fenitrothion were 200–1300 and 200–300, respectively and the partition coefficients between water and biological samples (Kwb) of diazinon and fenitrothion were 700–3300 and 450–700, respectively, suggesting that these pesticides accumulate in biological samples at higher rates than in sediment.

Type
Research Article
Copyright
Copyright © Marine Biological Association of the United Kingdom 2013 

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References

REFERENCES

Agradi, E., Baga, R., Cillo, F., Ceradimi, S. and Heltai, D. (2000) Environmental contaminants and biochemical response in eel exposed to Po river water. Chemosphere 41, 15551562.CrossRefGoogle ScholarPubMed
David, M.D.J. and Seiber, N. (1999) Analysis of organophosphate hydraulic fluids in U.S. Air Force Base soils. Archives of Environmental Contamination Toxicology 36, 235241.CrossRefGoogle ScholarPubMed
Domasgaski, J. (1996) Pesticides and pesticide degradation products in stromwater runoff; Sacramento River Basin, California. Water Resources Bulletin 32, 953964.CrossRefGoogle Scholar
Domasgaski, J. (1997) Results of a prototype surface water network design for pesticides developed for the San Joaquin River Basin California. Journal of Hydrology 192, 3350.CrossRefGoogle Scholar
Eguchi, S., Harino, H. and Yamamoto, Y. (2009a) Assessment of antifouling biocides contaminations in Maizuru Bay, Japan. Archives of Environmental Contamination Toxicology 58, 684693.CrossRefGoogle ScholarPubMed
Eguchi, S., Inaba, N., Shiraishi, T., Ueno, M., Masuda, R., Yamashita, Y. and Yamamoto, Y. (2009b) Marine heavy metal pollution monitoring in Maizuru Bay, Kyoto Prefecture, in Japan—status of lead pollution in Maizuru Bay. Kobe College Studies 55, 117131. [In Japanese.]Google Scholar
Eguchi, S., Usumoto, S., Yamamoto, S., Yoshimura, M., Ueno, M., Masuda, R., Yamashita, Y. and Yamamoto, Y. (2009c) Marine heavy metal pollution monitoring in Maizuru Bay, Kyoto Prefecture, in Japan II—status of lead pollution in local and transplanted stock of bivalves. Kobe College Studies 56, 153164. [In Japanese.]Google Scholar
FAO/WHO (1982) Pesticide residues in food—1982. Available at: http://www.inchem.org/documents/jmpr/jmpmono/v82pr35.htm (accessed 5 September 2013).Google Scholar
Fries, E. and Puttmann, W. (2003) Monitoring of the three organophosphate esters TBP, TCEP and TBEP in river water and ground water (Oder, Germany). Journal of Environmental Monitoring 5, 346352.CrossRefGoogle ScholarPubMed
Fukushima, M. and Kawai, S. (1986) Present status and transition of selected organophosphoric acid triesters in the water area of Osaka city. Ecological Chemistry 8, 1324. [In Japanese.]Google Scholar
Gilman, D.V., David, L.D. and Barbara, V.B. (1979) Measuring and estimating the bioconcentration factor of chemicals in fish. Journal of the Fisheries Research Board of Canada 36, 10401048.Google Scholar
Ishikawa, S., Taketomi, M. and Shinohara, R. (1985) Determination of trialkyl and triaryl phosphates in environmental samples. Water Research 19, 119125.CrossRefGoogle Scholar
Kawagoshi, Y., Fukunaga, I. and Itoh, H. (1999) Distribution of organophosphoric acid triesters between water and sediment at a sea-based solid waste disposal site. Journal of Material Cycles and Waste Management 1, 5361.Google Scholar
Lekkas, T., Kolokythas, G., Nikolaou, A., Kostopoulou, M., Kotrikla, A., Gatidou, G., Thomaidis, N.S., Golfinopoulos, S., Makri, C., Babos, D., Vagi, M., Stasinakis, A., Petsas, A. and Lekkas, D.F. (2004) Evaluation of the pollution of the surface waters of Greece from the priority compounds of List II, 76/464/EEC directive and other toxic compounds. Environment International 30, 9951007.CrossRefGoogle ScholarPubMed
Marklund, A., Andersson, B. and Haglund, P. (2003) Screening of organophosphorus compounds and their distribution in various indoor environments. Chemosphere 53, 11371146.CrossRefGoogle ScholarPubMed
Regnery, J. and Puttmann, W. (2010) Seasonal fluctuations of organophosphate concentrations in precipitation and storm water runoff. Chemosphere 78, 958964.CrossRefGoogle ScholarPubMed
Sato, K. and Kadokami, K. (1995) Determination of organophosphoric acid triesters in aquatic environmental samples by GC/MS. Journal of Environmental Chemistry 5, 821827.CrossRefGoogle Scholar
Sheldon, L.S. and Hites, R.A. (1978) Organic compounds in the Delaware River. Environmental Science and Technology 12, 11881194.CrossRefGoogle Scholar
Tsuda, T. (2007) Insecticides in water and fish from rivers and lakes. Journal of Environmental Chemistry 17, 603627. [In Japanese.]CrossRefGoogle Scholar
Tsuda, T., Aoki, S., Kojima, M. and Fujita, T. (1992) Pesticides in water and fish from rivers flowing into Lake Biwa (II). Chemosphere 24, 15231531.CrossRefGoogle Scholar
Tsuda, T., Aoki, S., Kojima, M. and Fujita, T. (1994) Pesticides in water and fish from rivers flowing into Lake Biwa (III). Toxicology and Environmental Chemistry 41, 8590.CrossRefGoogle Scholar
Yamada, H. (1987) Water pollution by organophosphoric acid triesters and its effects on aquatic organisms—a review. Bulletin of Tokai Fishery Research laboratory 123, 1530. [In Japanese.]Google Scholar
Yamaguchi, Y., Fukushima, M., Fujita, T. and Yamada, A. (1991) Distribution and seasonal variation of pesticides in Yodo River Basin. Journal of Environmental Chemistry 1, 5663. [In Japanese.]CrossRefGoogle Scholar