Alternative Antifouling Biocides

In response to increasing scientific evidence on the toxicity and occurrence of organotin residues from antifouling paints in the aquatic environment, the use of triorganotin antifouling products was banned on boats of less than 25 m length in many countries during 1987. The use of tributyltin (TBT) products on small boats was superseded by products based on copper, containing organic booster biocides to improve the efficacy of the formulation. Available information and evidence on the occurrence, fate and toxicity of these biocides is reviewed. It is concluded that increased copper concentrations in the aquatic environment, due to the increased use of copper-based antifoulants, do not have significant effects on marine ecosystems. However, lack of validated analytical methods, limited monitoring data, and very little information about the fate and toxicity of the booster biocides in the aquatic environment, make accurate risk assessments in relation to these compounds difficult. Copyright © 1999 John Wiley & Sons, Ltd.

[1]  C. Alzieu,et al.  Copper contamination as a result of antifouling paint regulations , 1993 .

[2]  G. Bachelet,et al.  Three decades of tributyltin in the coastal environment with emphasis on Arcachon Bay, France. , 1996, Environmental pollution.

[3]  L. Lawrence,et al.  Fate of an Antifoulant in an Aquatic Environment , 1993 .

[4]  D. J. Call,et al.  Bromacil and diuron herbicides: Toxicity, uptake, and elimination in freshwater fish , 1987, Archives of environmental contamination and toxicology.

[5]  T. Albanis Runoff losses of EPTC, molinate, simazine, diuron, propanil and metolachlor in Thermaikos Gulf, N. Greece , 1991 .

[6]  W. Seinen,et al.  Aquatic toxicological aspects of dithiocarbamates and related compounds. IV. Teratogenicity and histopathology in rainbow trout (Salmo gairdneri) , 1986 .

[7]  C. J. Leeuwen,et al.  Aquatic toxicological aspects of dithiocarbamates and related compounds. III. Embryolarval studies with rainbow trout (Salmo gairdneri) , 1986 .

[8]  Toxicité aiguë d'un fongicide dithiocarbamate, le thirame, vis à vis de plusieurs espèces animales d'eau douce , 1983 .

[9]  M. Borel,et al.  Tin contamination in Arcachon Bay: Effects on oyster shell anomalies , 1986 .

[10]  P. Vasseur,et al.  In vitro effects of Thiram on liver antioxidant enzyme activities of rainbow trout (Oncorhynchus mykiss) , 1992 .

[11]  John N. Lester,et al.  Temporal distribution of organotins in the Aquatic environment: five years after the 1987 UK retail ban on TBT based antifouling paints , 1993 .

[12]  D. Belluck Pesticides in the Aquatic Environment , 1981 .

[13]  S. Sinha,et al.  Copper-induced toxicity in aquatic macrophyte, Hydrilla verticillata: effect of pH , 1996, Ecotoxicology.

[14]  Kenneth W. Bruland,et al.  Speciation of dissolved copper and nickel in South San Francisco Bay: a multi-method approach , 1994 .

[15]  G. L. Willingham,et al.  Degradation of antifouling biocides. , 1996, Biofouling.

[16]  J. Stauber,et al.  Mechanism of toxicity of ionic copper and copper complexes to algae , 1987 .

[17]  Fan Yang,et al.  Occurrence of Organotin Compounds in the Canadian Aquatic Environment Five Years after the Regulation of Antifouling Uses of Tributyltin , 1997 .

[18]  M. Sjöström,et al.  Combined effects of tri-n-butyl tin (TBT) and diuron on marine periphyton communities detected as pollution-induced community tolerance , 1992 .

[19]  John N. Lester,et al.  Organotin distribution in sediments and waters of selected east coast estuaries in the UK , 1992 .

[20]  D. Dive,et al.  Studies on synergistic toxic effects of copper and dithiocarbamate pesticides with the ciliate protozoan Colpidium campylum (Stokes). , 1990, Ecotoxicology and environmental safety.

[21]  C. J. Leeuwen,et al.  Sublethal effects of tetramethylthiuram disulfide (thiram) in rainbow trout (Salmo gairdneri) , 1986 .

[22]  P. Vasseur,et al.  Thiram toxicity to non-target organisms: a comparative study with protozoan and mammalian cells , 1984 .

[23]  L. Hall,et al.  Monitoring dissolved copper concentrations in Chesapeake Bay, U.S.A. , 1988, Environmental monitoring and assessment.

[24]  W. Ernst,et al.  The toxicity of chlorothalonil to aquatic fauna and the impact of its operational use on a pond ecosystem , 1991, Archives of environmental contamination and toxicology.

[25]  Y M Nor,et al.  Ecotoxicity of copper to aquatic biota: a review. , 1987, Environmental research.

[26]  C. V. Van Leeuwen,et al.  Effects of chemical stress on the population dynamics of Daphnia magna: a comparison of two test procedures. , 1987, Ecotoxicology and environmental safety.

[27]  C. Watts,et al.  Comparative Predictions of Irgarol 1051 and Atrazine Fate and Toxicity , 1996 .

[28]  M. Ahsanullah,et al.  Toxicity of copper to the marine amphipod Allorchestes compressa in the presence of water-and lipid-soluble ligands , 1984 .

[29]  J. Lester,et al.  Degradation of Tributyltin in Freshwater and Estuarine Marina Sediments , 1993 .

[30]  Milena Horvat,et al.  Contamination of Mediterranean (Cote d'Azur) coastal waters by organotins and Irgarol 1051 used in antifouling paints , 1996 .

[31]  H. Okamura,et al.  Transformation of the new antifouling compound Irgarol 1051 by Phanerochaete chrysosporium , 1997 .

[32]  H. Blanck,et al.  Toxic effects of the antifouling agent irgarol 1051 on periphyton communities in coastal water microcosms , 1996 .

[33]  J. Stephen,et al.  Tributyltin : case study of an environmental contaminant , 1996 .

[34]  P. Donkin,et al.  Occurrence of the marine antifouling agent Irgarol 1051 within the Plymouth Sound locality: implications for the green macroalga Enteromorpha intestinalis , 1997 .

[35]  L. D. de Alencastro,et al.  Irgarol 1051, an Antifouling Compound in Freshwater, Sediment, and Biota of Lake Geneva , 1996, Bulletin of environmental contamination and toxicology.

[36]  M. Gough,et al.  A survey of southern England coastal waters for the s-triazine antifouling compound irgarol 1051 , 1994 .

[37]  J. Lester,et al.  The fate of tributyltin in the aquatic environment , 1988 .

[38]  E. Gallagher,et al.  The acute toxicity and sublethal effects of chlorothalonil in channel catfish (Ictalurus punctatus) , 1992 .

[39]  J. Lester,et al.  Spatial distribution of organotins in sediments of lowland river catchments. , 1992, Environmental pollution.

[40]  P. Quevauviller,et al.  Butyltin distribution in a sediment core from Arcachon harbour (France). , 1994, Environmental pollution.

[41]  Toxicité aiguë d'un fongicide, le thirame (dithiocarbamate), chez le crustacé amphipode d'eau douce Gammarus pulex , 1982 .

[42]  T. Sibley,et al.  Accumulation and transfer of copper by Oocystis pusilla , 1993, Bulletin of environmental contamination and toxicology.

[43]  K. Bruland,et al.  Trace metal exchange in solution by the fungicides Ziram and Maneb (dithiocarbamates) and subsequent uptake of lipophilic organic zinc, copper and lead complexes into phytoplankton cells , 1997 .

[44]  Effets d'une intoxication par le thirame présent dans le milieu ou la nourriture chez le crustacé Gammarus pulex , 1983 .