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Bioconcentration, Bioaccumulation, and Metabolism of Pesticides in Aquatic Organisms

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Reviews of Environmental Contamination and Toxicology

Part of the book series: Reviews of Environmental Contamination and Toxicology ((RECT,volume 204))

Abstract

From the viewpoint of protecting the natural environment, aquatic ecotoxicological assessment of new pesticides and many existing ones has increasingly become more important. To assess the impact of pesticides on aquatic organisms, international authorities (utilizing OECD and USEPA testing guidelines) require completion of many acute and chronic ecotoxicological studies. Among such studies is testing to measure the potential for bioconcentration. In addition, the authorities in these agencies insist that physico-chemical properties and environmental fate be determined for each registered pesticide. The rationale for such testing is based on the concept that, even if used in conformance with good agricultural practices, pesticides may enter surface waters by several routes such as spray drift, surface runoff, and field drainage, and they may be partitioned to bottom sediments (Katagi 2006). The endpoints of such ecotoxicological testing include mortality and effects on hatching, development, and reproduction. Such endpoints are usually expressed as median-lethal or median-effect concentrations (LC50 and EC50) and no-observed-effect-concentrations (NOEC); such values can be compared with predicted environmental concentrations in exposure media for purposes of risk assessment (Miyamoto et al. 2008). Because aquatic organisms interact with each other in the food web, knowledge of their tendency to bioconcentrate residues in water and from dietary exposure is important when evaluating real environmental pesticide effects. In general, bioconcentration is the most popular term for describing the process by which pesticides enter organisms directly from water through the gills or through epithelial tissues. In contrast, bioaccumulation includes the effect of dietary uptake through food consumption or intake of bottom sediments (Miyamoto et al. 1990). When the levels of a pesticide, accumulated by organisms, are concentrated through two or more trophic levels in a food web, the process is referred to as biomagnification (Connell 1988).

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Authors and Affiliations

  1. Environmental Health Science Laboratory, Sumitomo Chemical Co., Ltd., Takarazuka, Hyogo, 665-8555, Japan

    Toshiyuki Katagi

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  1. Toshiyuki Katagi
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    David M. Whitacre

Appendices

Appendix 1: Chemical Structures of Organic Chemicals and PAHs (Polyaromatic Hydrocarbons)

figure 1_a_191382_1_En

Appendix 2: Chemical Structures of Organochlorine Pesticides and Related Compounds

figure 1_b_191382_1_En

Appendix 3: Chemical Structures of Organophosphorus Pesticides

figure 1_c_191382_1_En

Appendix 4: Chemical Structures of Acid, Ester, and Amide Pesticides and Related Compounds

figure 1_d_191382_1_En

Appendix 5: Chemical Structures of Carbamate and Urea Pesticides and Related Compounds

figure 1_e_191382_1_En

Appendix 6: Chemical Structures of Miscellaneous Pesticides

figure 1_h_191382_1_En

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Katagi, T. (2010). Bioconcentration, Bioaccumulation, and Metabolism of Pesticides in Aquatic Organisms. In: Whitacre, D. (eds) Reviews of Environmental Contamination and Toxicology. Reviews of Environmental Contamination and Toxicology, vol 204. Springer, New York, NY. https://doi.org/10.1007/978-1-4419-1440-8_1

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