AMINOCARB JMPR 1978 IDENTITY Chemical name 4-dimethylamino-m-tolyl methylcarbamate Structural formula CH 3 -NH-C00 EVALUATION FOR ACCEPTABLE DAILY INTAKE BIOCHEMICAL ASPECTS Biodegradation A review of the biodegradation of aminocarb has suggested that the data on the in vivo metabolic fate has not been fully investigated (Kuhr and Dorough, 1976). The metabolic fate of aminocarb in animals, plants and insects has been investigated and based on in vitro data from an extensive base and some available in vivo studies, the following sequence of metabolism can be proposed. (This is based on data from Krishna and Casida, 1966; Oonnithan and Casida, 1966; 1968; and Strother, 1970; 1972).TOXICOLOGICAL EVALUATION The data available was insufficient and no acceptable daily intake for man has been established. RESIDUES IN FOOD AND THEIR EVALUATION The limited information which was available is summarized in the following appraisal. APPRAISAL Aminocarb is a non-systemic carbamate insecticide used mainly against many lepidopterous larvae and other biting insects. It also has some acaricidal and molluscicidal activity. Aminocarb is available as 50% and 75% water-soluble powders and is applied as 0.075 - 1.0%, solutions to fruits and vegetables. Use in forestry against the budworm is becoming important and could become the main use for aminocarb in the future. Surface residues of aminocarb are readily changed to less volatile products by photolyt: modification of the 4-dimethylamino group. In the bean plant, the major metabolic product 4-methylamino-m-tolyl methylcarbamate. The other degradation products so far identified are 4-formamido-m-tolyl methylcarbamate, 4-methylformamido-m-tolyl methylcarbamate and 4-amido-m-tolyl methylcarbamate. Glycosides are subsequently formed. Horseradish peroxidase attacked aminocarb quite rapidly but the tyrosinase system did not degrade it to any extent. Aminocarb is not persistent in soil. Two methods of analysis, both apparently suitable for regulatory purposes, are available. A GLC procedure has been described for aminocarb in forest foliage and soil using the nitrogen-specific electrical conductivity detector. The procedure still has to be validated for fruit and vegetables. High-pressure liquid chromatography with UV detection has also been applied to the analysis of cabbage, corn, potatoes and wheat with satisfactory detection limits and reproducibility. EVALUATION The data available were insufficient to establish an ADI or residue limits. FURTHER WORK OR INFORMATION Required (before an ADI or residue limits can be established) 1. Further data on toxicology and the occurrence of residues. Desirable 1. Data from countries on use patterns and on residues from supervised trials on which to base residue limits. 2. Studies on the fate of residues in animals. REFERENCES Kuhr, R.J. and H.W. Dorough Carbamate Insecticides: Chemistry, (1976) Biochemistry and Toxicology. CRC Press, Cleveland, Ohio, pg. 175-177. Krishna, J.G. and J.E. Casida, Fate in Rats of the Radiocarbon from (1966) Ten Variously Labelled Methyl and Dimethycarbamate-14C Insecticide Chemicals and Their Hydrolysis Products. J. Agr. Food Chem. 14:98. Oonnithan, E.S. and J.E. Casida Metabolites of Methyl and (1966) Dimethylcarbamate Insecticide Chemicals as Formed by Rat Liver Microsomes. Bull. Env. Contam. Toxicol. 1:59. Oonnithan, E.S. and J.E. Casida Oxidation of Methyl and (1968) Dimethylcarbamate Insecticide Chemicals by Microsomal Enzymes and Anticholinesterase Activity of the Metabolites. J. Agr. Food Chem. 16:28. Strother, A. Comparative Metabolism of Selected N-Methyl Carbamates (1970) by Human and Rat Liver Fractions. Biochem. Pharmacol. 19:2525. Strother, A. In Vitro Metabolism of Methylcarbamate Insecticides by Human and Rat Liver Fractions. Toxicol. Appl. Pharmacol. 21:112.
See Also: Toxicological Abbreviations Aminocarb (ICSC) Aminocarb (Pesticide residues in food: 1979 evaluations)