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 AZOCYCLOTIN/CYHEXATINExplanation Cyhexatin was evaluated in 1970, 1973, 1974, 1978 and 1981 (FAO/WHO 1971, 1974, 1975, 1979 and 1982)1/. A temporary ADI was recommended in 1978 and converted to an ADI in 1981. Azocyclotin was evaluated in 1979 and 1981 (FAO/WHO 1980, 1982). An ADI was recommended in 1981. The 1979 evaluation of azocyclotin resulted in some recommended temporary MRL's, which were at variance (lower) with those already proposed for cyhexatin for the same commodities. The 1979 Meeting noted that residues from these two compounds cannot be distinguished shortly after application, and therefore required additional information on use patterns and residue data to resolve this problem and harmonize residue limits. Information was received on analytical methodology and on the results of a joint residue study by the manufacturers. RESIDUES IN FOOD AND THEIR EVALUATION RESIDUES RESULTING FROM SUPERVISED TRIALS Parallel trials were carried out by Dow in England (Dow 1982) and by Bayer in the Federal Republic of Germany (Bayer 1982) in which apples (James Grieve in England and Golden Delicious in FRG) were treated with Plictran 25W and Peropal WP, each at the rate of 375 g a.i./ha in a spray volume of 1 500 litres of water. Similar mist blower applications were used in both countries. Samples from each trial were collected at 0, 7, 14, 28 and 35 days after the last application and divided into two sets. One set was exchanged between labs in the respective countries. One set from each country was analysed for total organotin residues, using the colorimetric method by Dow in England, and the other two sets were analysed by Bayer, using their gas chromatographic method, which determines azocyclotin, cyhexatin and dicyclohexyl tin oxide. The results of the Dow analyses are summarized in Table 1 and the results of the Bayer analyses are summarized in Table 2. 1/ See Annex 2 for FAO and WHO documentation. Table 1. Residues in Apples Determined by Colorimetric Analysis Residues (mg/kg) at interval post-treatment (days)1/ Location 0 7 14 28 35 of Product mean mean me an mean mean treatment used (range) (range) (range) (range) (range) UK 1 Plictran 25W 0.46 0.90 0.31 0.12 0.08 (0.33-0.63) (0.71-1.03) (0.21-0.44) (0.11-0.13) (0.05-0.12) Peropal WP 0.49 0.73 0.28 0.11 0.04 (0.42-0.58) (0.54-1.10) (0.19-0.37) (0.09-0.16) (0.02-0.05) UK 2 Plictran 25W 1.04 0.46 0.39 0.14 0.08 (0.69-1.18) (0.27-0.54) (0.31-0.48) (0.10-0.16) (0.07-0.09) Peropal WP 0.90 0.39 0-29 0.14 0.14 (0.66-0.99) (0.28-0.53) (0.18-0.42) (0.09-0.23) (0.09-0.19) FRG 1 Plictran 25W 0.39 0.15 0.14 0.07 0.13 (0.37-0.41) (0.13-0.18) (1.10-0.19) (0.06-0.08) (0.07-0.19) Peropal WP 0.54 0.37 0.31 0.09 0.14 (0.53-0.54) (0.26-0.48) (0.31-0.32) (0.05-0.12) (0.12-0.16) FRG 2 Plictran 25W 0.50 0.59 0.53 0.28 0.29 (0.49-0.52) (0.58-0.60) (0.51-0.56) (0.25-0.31) (0.29-0.30) Peropal WP 0.32 0.49 0.31 0.19 0.14 (0.24-0.40) (0.45-0.52) (0.28-0.34) (0.11-0.26) (0.10-0.18) 1/ Residues not corrected for recovery or control, but corrected for reagent blanks. Average recovery = 93.7%. Table 2. Residues in Apples Determined by Gas Chromatographic Analysis Location Residues (mg/kg) at interval of Product post-treatment (days)1/ treatment used 0 7 14 28 35 UK 1 Plictran 25W 0.35 0.72 0.25 0.18 0.10 Peropal WP 0.44 0.54 0.31 0.16 0.06 UK 2 Plictran 25W 1.20 0.51 0.51 0.21 0.21 Peropal WP 1.06 0.33 0.58 0.24 0.23 FRG 1 Plictran 25W 0.97 1.06 0.68 0.37 0.40 Peropal WP 0.42 0.60 0.53 0.37 0.34 FRG 2 Plictran 0.50 0.23 0.30 0.11 0.15 Peropal WP 0.50 0.25 0.23 0.13 0.14 1/ Plictran values reported as the sum of cyhexatin and dicyclohexyltin oxide. Peropal values reported as the sum of azocyclotin + cyhexatin and dicyclohexyltin oxide. It is evident from a comparison of the values both within the tables and between the tables, that there is no significant difference in residues on apples from the use of either azocyclotin or cyhexatin. Therefore, the discrepancies noted by the 1979 Joint Meeting are mainly due to the use of different application methods and not to any differences in the analytical methods or in the degradation chemistry. METHODS OF RESIDUE ANALYSIS Definition of residue In order to better conform to current analytical practice, the Meeting proposes that the definitions of the residues of azocyclotin and cyhexatin be changed to read as follows: azocyclotin - sum of azocyclotin, cyhexatin and dicyclohexyltin oxide, expressed as cyhexatin. cyhexatin - the sum of cyhexatin and dicyclohexyltin oxide, expressed as cyhexatin. These redefinitions have no effect on recommended maximum residue limits for either product. APPRAISAL The 1979 evaluation of azocyclotin resulted in a discrepancy in certain recommended maximum residue limits for commodities for which limits had already been recommended, based on data from the use of cyhexatin, which is also a degradation product of azocyclotin. In response to this problem, the manufacturers conducted a joint project on apples in England and the Federal Republic of Germany. The results of these tests clearly indicate that the discrepancy was due to different application technologies and that no significant differences in residues would result under identical treatment, climate and analytical conditions. Inasmuch as these new data support the existing recommendations for apples and pears associated with cyhexatin, no changes in any of the cyhexatin maximum residue levels are needed. Residues resulting from the use of either of these products cannot be distinguished analytically because they are principally surface residues and the degradation products are determined by environmental rather than metabolic processes. In addition, the analytical method converts both azocyclotin and cyhexatin to tricyclohexylmethyl tin. Therefore, it is necessary to revise the recommended limit for azocyclotin on apples, beans and strawberries to the same limits recommended for cyhexatin on those commodities. In the case of grapes and eggplant for which supervised trial data are available only for azocyclotin, the recommended limits for azocyclotin remain unchanged. New definitions of the residues are proposed for both products to conform more with current analytical practice. RECOMMENDATIONS Cyhexatin: Recommended maximum residue limits, all commodities - no change. Residues to which the limits apply are the sum of cyhexatin and dicyclohexyltin oxide expressed as cyhexatin. Azocyclotin: The previously recommended maximum residue limits are increased to the values listed below. The limits for azocyclotin represent the sum of azocyclotin, cyhexatin and dicyclohexyltin oxide, expressed as cyhexatin. Commodity Limit (mg/kg) Apples 2 (increased from 0.1) Beans 0.5 (increased from 0.2) Strawberries 2 (increased from 0.1) REFERENCES Bayer AG Residue trials on apples with Peropal and Plictran. 1982 RA-643181B (Plus covering letter). (Unpublished) Dow Ltd. Organotin residues in apples following treatments with 1982 Plictran 25W and Peropal WP acaricides in England and the Federal Republic of Germany - 1981. (Plus covering letter) (Unpublished)
See Also: Toxicological Abbreviations