DODINE JMPR 1976 Dodine was evaluated at the 1974 Joint Meeting. Temporary maximum residue limits were recommended for apples, pears, grapes, peaches, strawberries, and cherries. Further work was required on metabolism in plants and animals and the Meeting noted that it would be desirable to have information on teratogenicity, the fate in dairy cows fed with treated apple and grape pomace, supervised residue trials in countries other than U.S.A., and further details on residues in supervised trials on peaches and grapes, and during wine processing. Data which have become available since the 1976 meeting are evaluated in this monograph addendum. EVALUATION FOR ACCEPTABLE DAILY INTAKE BIOCHEMICAL ASPECTS Absorption, distribution and excretion Twelve male rats received 5.15 mg/kg bw 14C-dodine, marked at the quanidine moiety, in a single dose by gavage. Urine and faeces were collected daily. Three rats were killed after 24, 48, 96 and 196 hours, and samples from liver, kidney, muscle, fat and carcass were analysed. In urine 41.6% and 43.8% of the administered dose were excreted through 24- and 192-hour intervals, respectively while in the faeces 43.6% and 49.9% of the dose were eliminated in the same intervals. Total recovery from all sources (urine, faeces, g.i. tract and cage rinse) was 96%. Two rats were administered radio-labelled 14C-dodine at a dose of 34 mg/kg bw. The expired air, urine and faeces were monitored daily for 10 days. In expired air of two rats only 0.24% of the administered dose of 34 mg/kg was attributed to 14C carbon dioxide through the 240-hour experimental interval. Therefore oxidation of dodine to CO2 is not suggested as primary route of metabolism in the rat. The excretion of 14C-material by urine and faeces occurred rapidly. After 48 hours about 52% and 38% of the total dose were eliminated in the urine and faeces. After 240 hours, the total elimination by these routes was only slightly increased. Retention of radioactivity (expressed as ppm equivalents of 14C-dodine) in rat tissues (blood, liver, kidney, muscle) ranged between 0.01 and 0.21 mg/kg at the 24-hour interval and less than 0.01 mg/kg at the 192-hour interval in all tissues studied. Residues in fat were 9.5 mg/kg at 24 hours, 2.6 mg/kg at 48 hours and less than 0.01 mg/kg at 192-hours. The half-life of radioactive residues was less than 25 hours in all tissues examined. The nature of the radioactivity in urine, faeces and fat was studied with the help of thin-layer chromatography and isotope dilution analysis (co-crystallization). Among 20 radio-spots in urine four accounted for between 60 and 70% of radioactivity and more than 90% was due to dodine, suggesting that the urinary radioactivity arose from conjugates or other derivatives of dodine. Parent dodine represented 99% of the radioactivity in fat and 70% in faeces. Three minor faecal metabolites, whose migration values were similar to the major urinary metabolites, accounted for 20 to 30% of the extractable radioactivity (Cox and Eisner, 1976). COMMENTS Further studies on absorption, excretion and metabolism have been reported. In rats, elimination of an oral dose was rapid, predominantly in urine and faeces. Dodine, the major chemical residue in fat, decreased to negligible levels within 8 days. Concern was expressed on the relevance of the metabolic studies in rats only with respect to known differences in accumulation by mammalian species. For example, dodine accumulates in guinea pigs and mice in contrast to its rapid elimination from rats. The experiments performed on rats cannot be regarded as wholly sufficient. However, the results of new studies on metabolism in rats, augmenting the information previously considered showing dietary no-effect levels in rat (200 ppm) and dog (50 ppm) allowed an ADI to be recommended. TOXICOLOGICAL EVALUATION Level causing no toxicological effect rat: 200 ppm in the diet equivalent to 10 mg/kg bw dog: 50 ppm in the diet equivalent to 1.25 mg/kg bw ESTIMATE OF ACCEPTABLE DAILY INTAKE FOR MAN 0 - 0.01 mg/kg bw RESIDUES IN FOOD AND THEIR EVALUATION Country statements were received from the Netherlands, New Zealand, and Sweden. The statements only confirm information on use patterns and national residue limits available to the 1974 Meeting. The U.S. manufacturer submitted the results of metabolism studies in rats (discussed above) and on foliage of apple trees. The results of residue trials on apples at three locations in Germany were also made available. The other information designated as "desirable" was not available. RESIDUES RESULTING FROM SUPERVISED TRIALS In 1975, field experiments were conducted on dodine residues in apples at three locations in Germany (American Cyanamid, 1976a). The results are summarized in Table 1. TABLE 1. Residues of dodine in apples treated in Germany Location Variety Application Interval Residue weeks (mg/kg) Hove Jonathan 1.125 kg/ha, 2 16 & 17 <2.0 applications of a 65% Jork Marsh W formulation 16 & 17 <2.0 Moorende Gloster 17 & 22 <2.0 Analyses were by a colorimetric method. Controls had apparent dodine (crop blanks) equivalent to 0.5 mg/kg. Samples were frozen between sampling and analysis. Recoveries from fortified samples ranged from 89 to 109%. FATE OF RESIDUES In plants The 1974 Meeting (FAO/WHO, 1975) noted a study by Curry (1962) on the metabolism of dodine in apple trees using 14C labelled dodine. The study was in the nature of a tracer experiment, showing only the movement and distribution of total activity in the leaves and fruit. No attempt was made to identify any metabolic products, except for some speculation that the activity in fruit may have been due to protein bound residues of amino acid and guanidine moieties. The 1974 Meeting required additional metabolism data, presumably with identification of any alteration products. A report of a 1976 metabolism study on seedling apple trees was made available to the Joint Meeting (American Cyanamid Co., 1976b). The plants (greenhouse) were sprayed with 14C-dodine at a rate calculated to be equivalent to 2 kg a.i./ha. Total activity and the distribution of activity between surface rinses, extractable and unextractable deposits were followed for 8 weeks. Separation of 8 radioactive metabolites of dodine was obtained by two dimensional thin layer chromatography, but the metabolites were not identified. The study was of value in that it confirmed the earlier conclusions of Curry that (a) there is only minor translocation to new growth (1 mg/kg in new leaves) and (b) that the major portion of the residue is unchanged dodine. Although the metabolites were not identified, the work provides some additional basis for assessment of their toxicological significance in that it shows their proportion to dodine in the total residue. Table 2 shows the total unextractable residue in leaves and Table 3 shows the relative proportions of metabolites and parent in extracts of leaves for the 8 week period. TABLE 2. Total unextractable activity, expressed as mg/kg dodine, in apple leaves Residue radioactivity Time (Weeks) expressed as dodine, mg/kg 0 60.3 1 60.9 2 60.3 4 51.2 8 43.3 8 (Translocation to new growth) 1.0 TABLE 3. Distribution of dodine-derived metabolites found in extracts of Apple leaves Metabolite Coordinates Radioactivity (dodine equivalents, Number of spot mg/kg) after interval (weeks) 0 1 2 4 8 1 (dodine) 55-50 7.3 7.9 9.6 6.9 5.8 2a 50-37 0.8 0.7 - - 2 50-35 1.0 1.7 2.7 2.1 3 41-25 0.5 - 0.9 0.7 4 38-25 0.5 <0.1 1.2 0.9 TABLE 3. (Continued) Metabolite Coordinates Radioactivity (dodine equivalents, Number of spot mg/kg) after interval (weeks) 0 1 2 4 8 5 47-18 <0.1 1.0 0.6 - 6 38-14 0.4 - 1.1 0.7 7 35-16 1.1 1.9 1.2 2.4 Total 14C- extractable residues 7.3 11.8 15.7 14.6 14.0 In processing and cooking Studies on the reduction of dodine residues in cooking and/or processing spinach were conducted by General Foods Corporation and Del Monte Corporation (EPA, 1975). Field treated spinach bearing residues in the range 5.4-18.3 mg/kg was washed before canning and freezing. Residues in washed spinach were 26% of those in unwashed. Residues in blanched frozen and canned spinach were 16% and 7% respectively of residues in the unwashed spinach. Residues in the blanched frozen and canned spinach without prior washing were 61% and 25% respectively of those in unwashed spinach. In a second experiment, washing field treated spinach reduced residues by about 66% but home type cooking resulted in no further reduction of dodine residues. METHODS OF RESIDUE ANALYSIS The only method previously available for regulatory analyses was the colorimetric method of Steller (1960). A new gas-chromatographic method by Newsome (1976) offers considerable improvement. This method involves methanol extraction, partitioning with chloroform, and GC of the hexafluoroacetylacetone derivative with EC detection. A modification of this method was validated on spinach at 10 and 20 mg/kg fortification levels in U.S. government laboratories and is suitable for regulatory analysis. APPRAISAL The temporary maximum residue limits recommended by the 1974 Meeting were contingent upon additional information on metabolism in plants and animals, teratogenicity studies, fate in dairy cows fed with treated apple and grape pomace, supervised trials on various crops from countries other than U.S.A., and further details on supervised trials on peaches and grapes, and residues in wines. The material designated as required by the 1974 Meeting was partly provided. The material designated as desirable has not been made available (except for a limited residue trial on apples from Germany). A significant advance in analytical methodology was made with the development of the electron-capture GC procedure of Newsome which measures a derivative. Useful information was made available on the reduction of residues in processing and cooking. There was a significant reduction of residues in washing, canning and blanching of spinach but no observable reduction in home cooking. RECOMMENDATIONS Since an ADI has now been allocated, the temporary maximum residue limits recommended by the 1974 Joint Meeting are converted to maximum residue limits. No additional limits are recommended. FURTHER WORK OR INFORMATION REQUIRED(before further Maximum Residue Limits can be recommended) 1. A large animal feeding study to determine whether feeding of apple pomace and grape pomace contributes residues to meat and milk. 2. Identification of metabolites occurring in crops if the levels shown in the 1976 study are found to be toxicologically significant by WHO. DESIRABLE 1. Studies of the metabolism of dodine in species other than the rat, preferably in guinea-pigs and/or dogs. 2. Teratological studies in appropriate animal species. 3. Appropriate mutagenicity studies. REFERENCES American Cyanamid. Technical Report no. 566, Cyanamid International. 1976a Cyanamid of Great Britain Ltd. May 13, 1976. (Unpublished) American Cyanamid. Fate of radiolabeled dodine in young apple 1976b plants American Cyanamid Co., Agricultural Division, Princeton, N.J. Project no. 0542, E.J. Orloski, June 17, 1976. (Unpublished) Cox, G.W., and Eisner, S.K. CL 7521: Absorption, excretion 1976a and metabolism of carbon-14 labelled n-dodecylguanidine acetate in rats. PD-M 13-5: 1-78. Unpublished report submitted by American Cyanamid Company. Cox, G.W., and Eisner, S.K. Dodine: Fate of radiolabeled 1976b dodine (n-dodecylguanidine acetate) in young apple plants. PD-M 13-4: 1-36. Unpublished report submitted by American Cyanamid Company. Curry, A.M. Translocation and metabolism of dodecylguanidine 1962 acetate (dodine) fungicide in apple trees, using C14 radiotagged dodine. J. Agr. Food Chem., 10: 13-17. EPA Unpublished data on reduction of dodine 1975 residues by cooking and processing. FAO/WHO 1974 Evaluations of some pesticide residues in 1975 food. FAO/AGP: 1974/M/11; WHO Pesticide Residues Series, No. 4. Newsome, W.H. A gas-liquid chromatographic method for the 1976 determination of dodine residues on foods. J. Agr. Food Chem., 24: 997-999 Steller, W.A., et al. Colorimetric estimation of dodecylguanidine 1960 acetate residues. J. Agr. Food Chem., 8: 460-464.
See Also: Toxicological Abbreviations Dodine (WHO Pesticide Residues Series 4) Dodine (Pesticide residues in food: 1977 evaluations) Dodine (JMPR Evaluations 2000 Part II Toxicological)