PESTICIDE RESIDUES IN FOOD - 1982 Sponsored jointly by FAO and WHO EVALUATIONS 1982 Data and recommendations of the joint meeting of the FAO Panel of Experts on Pesticide Residues in Food and the Environment and the WHO Expert Group on Pesticide Residues Rome, 23 November - 2 December 1982 Food and Agriculture Organization of the United Nations Rome 1983 ETRIMFOSExplanation Etrimfos was evaluated by the 1980 JMPR (FAO 1981).1 A temporary ADI for man was recommended, based on no-effect levels observed in 2-year studies in the rat and dog. The 1980 JMPR Report required disposition and kinetic data on the whole molecule of etrimfos and its triester metabolites in animals and considered observations in man as being desirable. Daily sheet reports on field applicators and comments on the required information have been provided and are summarized in this monograph addendum. EVALUATION FOR ACCEPTABLE DAILY INTAKE BIOCHEMICAL ASPECTS Metabolism Metabolism studies in the rat have shown that the P-O-pyrimidine ester bond in etrimfos is rapidly cleaved. This is the major detoxification process. Studies with rat and mouse liver homogenates (Ioannou and Dauterman 1978) have shown that the P-O-CH3 and the P-O-pyrimidine ester bonds are rapidly cleaved. These studies clearly show that the triester molecule has only a transient existence in the animal system and that the phosphoric acid moiety exists either as the mono-methyl ester, or possibly as free phosphoric acid. Re-esterification of the phosphoric acid moiety in the animal system, if it occurs, would not be something specific to etrimfos, but would be common to organophosphorus insecticides in general (Karapally 1982). 1 See Annex 2 for WHO and FAO documentation. TOXICOLOGICAL STUDIES Observations in Humans During the developing phase of etrimfos, 167 daily sheet reports on field trials personnel were completed. The reports cover more than 220 hours of work in the field with different etrimfos-containing formulations. Applicators worked in different locations under varying weather conditions for periods of 0.5 to 3 hours/day, wearing in most cases only boots and protective overcoats. No noteworthy symptoms or complaints during or at the end of the working period were recorded. No clinical investigations were carried out (Sandoz 1976). COMMENTS Etrimfos was evaluated for an acceptable daily intake for man by the 1980 JMPR. The Meeting examined the submitted comments regarding the metabolism of etrimfos and reports on people engaged in field applications of etrimfos formulations that were made available. Studies of the metabolism and distribution of etrimfos in rats undertaken with 14C in the pyrimidine moiety have provided useful information and, following clarification by the manufacturers, further disposition and kinetic data were not considered necessary. Although the Meeting agreed that the submitted observations in humans were of little value, primarily because no clinical investigations were carried out, an ADI was allocated. TOXICOLOGICAL EVALUATION Level Causing no Toxicological Effect Rat : 6 ppm in the diet, equivalent to 0.3 mg/kg bw. Dog : 10 ppm in the diet, equivalent to 0.25 mg/kg bw. Estimate of Acceptable Daily Intake for Man 0 - 0.003 mg/kg bw FURTHER WORK OR INFORMATION Desirable Further observations in humans. REFERENCES Ioannou, Y.M. Dauterman, W.C. In vitro metabolism of etrimfos by rat 1978 and mouse liver. Pest.Biochem. Physiol. 9:190-195. Karapally, J.C. Personal communication to WHO. Sandroz, Switzerland 1982 Sandoz, Daily sheet reports of field applicators. Agrochemical 1976 Division, Basle, Switzerland. Report from Sandoz submitted to the WHO by Sandoz. (Unpublished)
See Also: Toxicological Abbreviations Etrimfos (Pesticide residues in food: 1980 evaluations)