Quantitative inter-specific chemical activity relationships of pesticides in the aquatic environment.

Inter-species correlations could be a useful tool for predicting toxicity and for establishing sensitivity ratios among species. In this paper, quantitative inter-specific chemical activity relationships (QICAR) for aquatic organisms were developed to verify if such an approach could be utilised for estimating toxicological data when no other information is available. Inter-specific toxicity relationships on fish, Daphnia and algae were performed for pesticides considering a large data set (more than 600 compounds) and grouping the data either on a functional (herbicides, fungicides and insecticides) or chemical class base. Good correlations were found between several fish species and they were improved by excluding, from the data set, highly specific compounds such as organophosphorus insecticides. Relationship between fish (rainbow trout) and Daphnia was significant for the whole data set, but clearly improves if congeneric classes of pesticides are considered. The most significant results were found for azoles (fungicides) and for all data set of pesticides with the exclusion of organophosphorus and carbamate insecticides. As expected, toxicity on algae does not correlate either with fish or with Daphnia on the whole data set, but excluding the classes acting specifically toward one organism (insecticides and several classes of herbicides), good relationships were found. The analysis of the data permits the conclusion that the specificity in the mode action of pesticides is the key parameter for expecting or not inter-specific relationships. By the relative specificity of action of a group of compounds towards two species, the probability of obtaining a QICAR for this group can be derived. In general, compounds acting with the same level of specificity towards two different species, have a higher probability of showing inter-specific relationships and the lower the specificity of the mode of action of the compounds (e.g. narcotics or less inert chemicals), then the stronger are the relationships.

[1]  D. Schaeffer,et al.  Quantitative comparisons of acute toxicity of organic chemicals to rat and fish. , 1984, Ecotoxicology and environmental safety.

[2]  Terry W Schultz,et al.  Comparative toxicity of selected nitrogen-containing aromatic compounds in the Tetrahymena pyriformis and Pimephales promelas test systems , 1989 .

[3]  Marco Vighi,et al.  QSARs for toxicity of organophosphorous pesticides to Daphnia and honeybees , 1991 .

[4]  T W Schultz,et al.  Relationships of quantitative structure-activity to comparative toxicity of selected phenols in the Pimephales promelas and Tetrahymena pyriformis test systems. , 1986, Ecotoxicology and environmental safety.

[5]  W. Slooff,et al.  Comparison of the susceptibility of 22 freshwater species to 15 chemical compounds. I. (Sub)acute toxicity tests , 1983 .

[6]  J. Dearden,et al.  QSAR studies of comparative toxicity in aquatic organisms. , 1991, The Science of the total environment.

[7]  J. Leahey The pyrethroid insecticides. , 1985 .

[8]  C. D. S. Tomlin,et al.  The pesticide manual, Eleventh edition , 1997 .

[9]  D. Adema,et al.  A comparative study of the toxicity of 1,1,2-trichloroethane, dieldrin, pentachlorophenol and 3,4 dichloroaniline for marine and fresh water organisms , 1981 .

[10]  B. Taylor,et al.  Comparisons of acute toxicity of selected chemicals to rainbow trout and rats. , 1998, Ecotoxicology and environmental safety.

[11]  L. Baker,et al.  Structure-activity relationships for Di and Tri alkyl and/or halogen substituted phenols , 1989, Bulletin of environmental contamination and toxicology.

[12]  D. Delistraty Acute toxicity to rats and trout with a focus on inhalation and aquatic exposures. , 2000, Ecotoxicology and environmental safety.

[13]  K. Kaiser,et al.  QSAR in Environmental Toxicology - II , 1984 .

[14]  J. Hermens,et al.  Classifying environmental pollutants , 1992 .