THIODICARB EXPLANATION Thiodicarb was evaluated for acceptable daily intake by the 1985 Joint Meeting (Annex 1, FAO/WHO, 1986a), at which time a temporary ADI of 0 - 0.01 mg/kg b.w. was established. A toxicology monograph was published (Annex 1, FAO/WHO, 1986c). Data designed to satisfy the requirements of the 1985 Joint Meeting were submitted for consideration by the present Meeting, and these data are summarized in this monograph addendum. EVALUATION FOR ACCEPTABLE INTAKE BIOLOGICAL DATA Toxicological studies Special study on teratogenicity Rabbits Thiodicarb was administered orally in 0.5% carboxymethylcellulose to 4 groups of 22 artificially-inseminated New Zealand white rabbits once daily on gestation days 6 through 19, inclusive. Dosage levels were 0, 5, 20, and 40 mg/kg b.w./day. Throughout gestation, all females were observed twice daily for toxicity, and body weights and food consumption were recorded at appropriate intervals. On gestation day 29, all surviving females were sacrificed for the scheduled caesarean sections. All fetuses were weighed, sexed, and examined for external, skeletal, and soft-tissue anomalies and developmental variations. Body-weight gain and food consumption were inhibited during the treatment and post-treatment periods in the 40 mg/kg b.w./day dose group, primarily during the initial 6 days of compound administration. No clinical signs of maternal toxicity or embryo-/fetotoxicity were observed at any dose levels. Maternal body-weight gain and food consumption were not adversely affected at dose levels of 5 or 20 mg/kg b.w./day. An evaluation of the types and frequency of fetal anomalies and developmental variations did not indicate a teratogenic response in this study (Rodwell, 1986). Short-term study Dogs Four groups of 6 beagle dogs/sex/dose level were administered thiodicarb in the diet at levels of 0, 164, 487, or 1510 ppm (equal to 4.4 and 4.5, 12.8 and 13.8, and 38.3 and 39.5 mg/kg b.w./day for males and females, respectively) for 1 year. Criteria evaluated for compound effects included mortality, body-weight gain, appearance and behaviour, and food and compound consumption. Clinical laboratory studies, ophthalmologic examinations, gross necropsy findings, organ-weight data, and histopathology were performed. No effects were observed on mortality, clinical signs, body-weight gain, or food or water consumption. Slight decreases in erythrocyte count, haematocrit, and haemoglobin were noted in the high-dose males and females at all 3 observation intervals in the study. Erythrocyte counts and haemoglobin values in males were slightly lower than control values at weeks 13 and 26. Significant plasma, red blood cell, and brain cholinesterase activity inhibition (> 25%) occurred in the high-dose animals during the course of the study. Red blood cell cholinesterase activity inhibition exceeding 25% also occurred in the mid-dose males (27%) and females (28%) at week 13. No other changes were noted that would suggest a compound-related effect on any other measured clinical pathology parameter. Liver and spleen weights of the treated females were increased in a dose-related manner when compared to the controls. These increases were noted also in the organ/body- and organ/brain-weight ratios in females, where statistical significance, compared to controls, was noted at the high dose only. These changes were not seen in the males. No other changes were notes that would suggest a compound-related effect in the other organ weight data, or in the ophthalmology, gross pathology, or histopathology data. Based on these observations, the NOEL of thiodicarb in beagle dogs in this study was 487 ppm, equal to an intake of 12.8 mg/kg b.w./day for males and 13.8 mg/kg b.w./day for females (Hamada, 1986). COMMENTS The 1-year dog study requested by the 1985 Joint Meeting has been received and reviewed. A NOEL of 487 ppm was established. The previous Meeting had also requested information on a possible effect on body-weight gain noted in a rat teratology study. A study in rabbits was submitted to the present Meeting, which failed to confirm the observations in rats. The Meeting therefore concluded that the available data permitted the allocation of a full ADI. LEVEL CAUSING NO TOXICOLOGICAL EFFECT Rat: 60 ppm in the diet, equivalent to 3 mg/kg b.w./day. Dog: 487 ppm in the diet, equal to 12.8 mg/kg b.w./day in males. and 13.8 mg/kg b.w./day in females. ESTIMATE OF ACCEPTABLE DAILY INTAKE FOR MAN 0 - 0.03 mg/kg b.w. STUDIES WHICH WILL PROVIDE INFORMATION VALUABLE FOR THE CONTINUED EVALUATION OF THE COMPOUND Observations in humans. REFERENCES Hamada, N. One-year feeding study in dogs with thiodicarb technical. 1986 Project No. 21100-126. Unpublished report from Hazleton Laboratories, Inc., Falls Church, VA, USA. Submitted to WHO by Union Carbide Agricultural Products Company, Inc., Research Triangle Park, NC, USA. Rodwell, D.E. A teratology study in rabbits with thiodicarb, Project 1986 No. WIL-95002. Unpublished report from WIL Research Laboratories, Inc. Submitted to WHO by Union Carbide Agricultural Products Company, Inc., Research Triangle Park, NC, USA.
See Also: Toxicological Abbreviations Thiodicarb (Pesticide residues in food: 1985 evaluations Part II Toxicology) Thiodicarb (JMPR Evaluations 2000 Part II Toxicological)