PESTICIDE RESIDUES IN FOOD - 1984 Sponsored jointly by FAO and WHO EVALUATIONS 1984 The monographs 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, 24 September - 3 October 1984 Food and Agriculture Organization of the United Nations Rome 1985 OMETHOATE Explanation Omethoate was evaluated in 1971 and reviewed in 1975, 1978, 1979 and 1981 1/. The CCPR at its 12th (1980) Session (ALINORM 81/24 para 64) concerned over the higher toxicity of omethoate than dimethoate, requested the meeting to review the two compounds with a view to recommending separate MRLs for each. Dimethoate is reviewed elsewhere in these evaluations. Some additional information concerning omethoate, received from Australia, The Netherlands, New Zealand and the manufacturers of the compound, is reviewed below. IDENTITY Purity The only manufacturer of omethoate confirmed that technical omethoate has the following composition. Omethoate min 94.5% O-desmethyl-omethoate max 2.0% Dimethyl phosphite max 2.0% Solvents max 2.0% This is substantially identical with the purity of omethoate referred to in 1971. RESIDUES IN FOOD AND THEIR EVALUATION USE PATTERN The manufacturer provided an up-to-date list of registered uses in many countries with recognised registration systems which has been summarized in Table 1. This should be compared with the use pattern for dimethoate. Dimethoate, having been introduced world-wide nine years before the introduction of omethoate in 1965, was adopted for many uses for which omethoate is suitable but which have not been promoted by the manufacturer. 1/ See Annex II for FAO and WHO documentation. Table 1. Registered Used, pre-harvest intervals and maximum residue limits (MRLs) for Omethoate Omethoate Country Crop Concentration Application Rate Pre-harvest MRL (g/1001) (kg/ha) Interval (mg/kg) (days) Algeria Olives 60 Pome fruit 21 Argentina Cereals 21 Citrus fruit 21 Cotton 21 Foddercrops 21 Pastures 21 Pome fruit 21 Potatoes 21 Stone fruit 80 1.2 21 Vegetables 21 Australia Bananas 60 0.60 4 - Cereals, grain 7 0.05 Cereals, green 7(grazing) Citrus 60 1.2 7 2.0 Cotton 0.64 7 0.5 Forage crops 0.22 7(grazing) Fruit 60 0.60 7 2.0 Oilseed 0.05 Oilseed crops (as food stuff) 7 Onions 60 0.60 7 2.0 Pastures 7(grazing) Peppers 60 0.60 7 1.0 Tomatoes 60 0.60 7 1.0 Vegetables (excluding tomatoes and peppers 60 0.60 7 2.0 Table 1. (continued) Country Crop Concentration Application Rate Pre-harvest MRL (g/1001) (kg/ha) Interval (mg/kg) (days) Austria Fruit 50 0.75 35 0.4 Potatoes 0.35-0.5 35 0.05 Sugar beets 0.2 35 0.4 Vegetables 0.35-0.5 35 0.4 Belgium Cereals 0.05 Chicory 0.4 Fruit(excl.citrus) 50-75 0.75 21 0.1 Hops 50-75 0.75 21 Sugar beets 21 Vegetables (excl. chicory) 50-75 0.75 0.1 Brazil (1) Coffee 14 0.01 Cottonseed 14 0.1 Soybeans 14 0.1 Wheat 14 0.1 Canada Apples 2.0 Beans 1.0 Beet leaves 2.0 Broccoli 2.0 Cabbage 2.0 Cauliflowers 2.0 Celery 1.0 Cherries 1.0 Citrus fruit 1.5 Kale 2.0 Lettuce 2.0 Pears 2.0 Peas 0.5 Peppers 0.5 Table 1. (continued) Country Crop Concentration Application Rate Pre-harvest MRL (g/1001) (kg/ha) Interval (mg/kg) (days) Spinach 2.0 Strawberries 1.0 Swiss chard 2.0 Tomatoes 0.5 Turnip leaves 2.0 Chile Field crops 0.3-0.7 Fruit 30-83 0.5-2.7 Cyprus Fruit 15-20 Grapes 15-20 Potatoes 15-20 Vegetables 15-20 Czechoslovakia Fodder beets 7 Sugar beets 7 Denmark Berry fruit 0.5 Grapes 0.5 Leafy vegetables 0.5 Pomefruit 0.5 Potatoes 0.05 Stone fruit 0.5 Other vegetables 0.5 European Artichokes 0.4 Community Berry frqit 0.1 Cherries 0.4 Chicory 0.4 Leek 0.1 Onions - 0.1 Table 1. (continued) Country Crop Concentration Application Rate Pre-harvest MRL (g/1001) (kg/ha) Interval (mg/kg) (days) Root vegetables 0.1 Spinach 0.4 Other food crops 0.2 FAO/WHO 1) Apples 2 Apricots 2 Citrus fruit 2 Cherries 2 Currants (black) 2 Grapes 2 Hops (dried) 3 Olives 2 Peaches 2 Pears 2 Peppers 1 Plums 2 Potatoes 0.05 Strawberries 1 Sugar beet leaves 1 Sugar beets 0.05 Tomatoes 1 Vegetables (not otherwise listed) 2 France Artichokes 62.5 15 0.4 Fruit 62.5-87.5 0.75-1.3 15 1.0 Grapes 62.5 0.75-0.93 7 1.0 Olives 21 0.2 Vegetables (excl.artichokes) 15 1.0 Table 1. (continued) Country Crop Concentration Application Rate Pre-harvest MRL (g/1001) (kg/ha) Interval (mg/kg) (days) German Hops 28 Democratic Crops treated by drift: Republic Food crops 21 Fodder crops 10 Germany, Artichokes 0.4 Federal Beets 35-42 3) 0.05 Republic Berry fruit 0.1 Cherries 0.4 Chicory 0.4 Hops 21 Leek 0.1 Onions 0.1 Potatoes 35 0.05 Root vegetables 0.1 Spinach 0.4 Other fruit 0.2 Other vegetables 0.2 Other food crops 0.05 Greece Citrus fruit 21 Cotton 21 Pome fruit 21 Vegetables 21 Great Britain Cereals 21 Grass crops 42 Hops 21 Pastures 7 Plums 35 Table 1. (continued) Country Crop Concentration Application Rate Pre-harvest MRL (g/1001) (kg/ha) Interval (mg/kg) (days) Israel Alfalfa 7 Citrus fruit 30 0.4 Common vetch 30 Grapes 15 Italy Cereals 0.375-0.75 30 0.05 Fruit 25-50 0.375-2.0 30 0.4 Grapes 25-50 0.375-1.0 30 Olives 25-50 0.375-0.75 30 0.4 Potatoes 25-50 0.5-1.0 30 Sugar beets 30 0.4 Vegetables 30 0.4 Kenya Apples 21 2.0 Beans 21 2.0 Broccoli 21 2.0 Cabbage 21 2.0 Cauliflower 21 2.0 Endive 21 2.0 Kale 21 2.0 Lemons 21 2.0 Lettuce 21 2.0 Melons 21 1.0 Oranges 21 2.0 Pears 21 2.0 Peas 21 2.0 Pecans 21 0.1 Peppers 21 2.0 Potatoes 21 0.2 Rutabagas 21 2.0 Table 1. (continued) Country Crop Concentration Application Rate Pre-harvest MRL (g/1001) (kg/ha) Interval (mg/kg) (days) Swiss chard 21 2.0 Spinach 21 2.0 Tomatoes 21 2.0 Wheat 21 0.04 Meat, fat and meat by- products of cattle, 0.02 goats, hogs, horses and sheep Korea Apples 50-62.5 0.75-0.95 Citrus 50-62.5 2.0 -2.5 Luxemburg Cereals 0.05 Fruit 0.5 Vegetables 0.5 Other food crops 0.05 Mexico Alfalfa 10/28 2) 2.0 Apples 28 2.0 Barley 0.3-0.45 60 3) 0.04 Beans, dried 0.3-0.45 0.2 Beans, green 0.3-0.45 2.0 Broccoli 7 2.0 Brussels sprouts 3 2.0 Cabbage 3 2.0 Cauliflowers 7 2.0 Celery 7 2.0 Chick peas 0.3-0.45 21 2.0 Citrus fruit 1.0-1.25 28 2.0 Cotton 0.25-0.8 14 0.1 Table 1. (continued) Country Crop Concentration Application Rate Pre-harvest MRL (g/1001) (kg/ha) Interval (mg/kg) (days) Grapes 28 1.0 Lettuce 14 2.0 Maize 0.3-0.45 14 0.1 Melons 3 1.0 Oranges 15 2.0 Pears 28 2.0 Pecans 21 0.1 Peppers 2.0 Potatoes 0.2 Safflower 14 0.1 Snap beans 0.3-0.45 2.0 Sorghum 0.3-0.45 28 0.1 Soybeans 21 0.05 Stone fruit 0.85-1.0 Tomatoes 7 2.0 Tobacco 0.45-0.65 21 Wheat 0.3-0.45 60 3) 0.04 Morocco Fruit 0.25-0.75 Vegetables 0.25-0.75 Netherlands Artichokes 0.4 Berry fruit 0.1 Cherries 0.4 Chicory 0.4 Leak 0.1 Onions 0.1 Vegetables 0.1 Spinach 0.4 Strawberries 0.1 Table 1. (continued) Country Crop Concentration Application Rate Pre-harvest MRL (g/1001) (kg/ha) Interval (mg/kg) (days) Other fruit 0.2 Other vegetables 0.2 Other 0 4) New Zealand Cereals 21 Citrus fruit 21 Fodder crops 14 Grapes 42 Lucerne 14 Maize (fodder) 14 Pome fruit 21 General 0.5 Portugal Apples 21 Citrus fruit 28 Cotton 21 Hops 21 Pears 21 Plums 21 South Africa Alfalfa 7 2.0 Apples 28 1.5 Citrus fruit 35 2.0 Clover 7 2.0 Cotton 50 Grapes 28 1.5 Pears 28 1.5 Peas 7 1.0 Table 1. (continued) Country Crop Concentration Application Rate Pre-harvest MRL (g/1001) (kg/ha) Interval (mg/kg) (days) Spain Citrus fruit 25-75 1.0-3.0 30 0.4 Cotton 0.25-1.0 30 Fruit 25-75 0.25-0.75 0.4 Grapes 50-75 0.75-1.5 30 0.4 Hops 25-75 0.25-0.75 30 Pome fruit 25-75 0.25-0.75 30 0.4 Potatoes Stone fruit 25-75 0.25-0.75 30 0.4 Sugar beet Vegetables 25-75 0.375-0.75 0.4 Sweden Fruit 0.1 Potatoes 0.1 Vegetables 0.1 Taiwan Apples 21 Guavas 21 Soybeans 60 Thailand Rice 0.75 Cotton 60 0.9 Tobacco 60 0.9 Citrus 60-80 1.5-2.5 Fruit 60-80 0.9-1.2 Turkey Fruit 50-200 Grapes 50-75 0.5-0.75 Cotton 0.5-0.75 Vegetables 50-75 Sugar beet 50 Citrus 50-75 1.0-1.5 Table 1. (continued) Country Crop Concentration Application Rate Pre-harvest MRL (g/1001) (kg/ha) Interval (mg/kg) (days) USA 5) Alfalfa 2.0 Apples 2.0 Beans (dry, 2.0 lima, snap) Broccoli 2.0 Cabbage 2.0 Cauliflowers 2.0 Celery 2.0 Cherries 2.0 Citrus pulp, dried 5.0 (as feed stuff) Collards 2.0 Cottonseed 0.1 Endive 2.0 Grapefruit 2.0 Grapes 1.0 Kale 2.0 Lemons 2.0 Lettuce 2.0 Melons 1.0 Mustard greens 2.0 Oranges 2.0 Pears 2.0 Peas 2.0 Pecans 0.1 Peppers 2.0 Potatoes 0.2 Safflower seed 0.1 Sorghum forage 0.2 Sorghum grain 0.1 Soybean forage 2.0 Table 1. (continued) Country Crop Concentration Application Rate Pre-harvest MRL (g/1001) (kg/ha) Interval (mg/kg) (days) Soybean hay 2.0 Soybeans 0.05 6) Spinach 2.0 Swiss chard 2.0 Tangerines 2.0 Tomatoes 2.0 Turnips (roots and tops) 2.0 Wheat grain 0.04 6) Wheat, green fodder 2.0 Wheat straw 2.0 Eggs 0.02 6) Meat, fat and meat 0.02 6) by-products of cattle, goats, hogs, horses, poultry and sheep Milk 0.002 6) Venezuela Carrots 21 1.0 Cotton 21 1.0 Fruit 21 1.0 Grapes 21 1.0 Rice 21 1.0 Potatoes 21 1.0 Tobacco 21 1.0 Tomatoes 21 1.0 Vegetables 21 1.0 Table 1. (continued) Country Crop Concentration Application Rate Pre-harvest MRL (g/1001) (kg/ha) Interval (mg/kg) (days) Yugoslavia Fodder beets 42 Fruit 28 0.5 Hops 21 Onions 42 Sugar beets 42 0.5 Tobacco 21 Vegetables (excl. onions) 28 Other field crops 42 Other food crops 0.05 1) = Temporary tolerances 2) = Depending on formulation 3) = Application at time of sowing 4) = Under the limit of determination (0.02 mg/kg) 5) = Tolerances of dimethoate 6) = At or about the limit of determination The nine major applications of omethoate represent approximately 70% of the world demand as indicated in Table 2. RESIDUES RESULTING FROM SUPERVISED TRIALS Results of trials carried out with apples, peaches and hops in Chile, Italy and the Federal Republic of Germany (Bayer, 1984) are summarised in Table 3. These results are generally in agreement with those considered previously and upon which recommendations for MRLs were made. With the exception of one trial on apples from Italy, the results are within the recommended MRLs. This Italian trial yielded a residue of 2.3 mg/kg 37 days after the last of 3 treatments at the rate of 1 kg/ha. The proposed Codex temporary MRL of 2 mg/kg is based on a PHI of 21 days after a similar treatment. The residue value at 64 days after the last treatment (0.46 mg/kg) from the same trial would tend to confirm that the finding at 37 days was probably valid. Results of official trials on Kiwi fruit received from New Zealand are summarized in Table 4. The approved rate of application is 50 g a.i./100 l equivalent to 2.8 kg/ha with a withholding period of 21 days. FATE OF RESIDUES Attention is directed to the references to the fate of residues in the accompanying monograph on dimethoate, the 1976 and 1970 evaluations of dimethoate, and the 1971 evaluation of omethoate. In Animals The work of the following investigators mentioned in the present or earlier dimethoate evaluations should especially be noted: Dauterman et al. (1959); Kaplanis et al (1959); Chamberlain et al. (1961); Beck et al. (1968). Ecker and Coelln (1981) studied the biotransformation of omethoate in rats. Within 8 hours after oral administration of 5 mg/kg of [carbonyl-14C] omethoate to male rats, about 88% of the radioactivity was eliminated with the urine. Of this, 30-50% was unchanged parent compound, about 11% was O-demethyl-omethoate and a further 15-22% was identified as N-methyl-2-(methyldithio)acetamide. It is fairly certain that omethoate is not stored in animal tissues or fat nor excreted in milk unless the intake is at least one to two orders of magnitude higher than livestock could encounter from the direct or indirect use of dimethoate or omethoate in controlling insect pests of crops, pasture or forage. Table 2. Main uses of dimethoate (Bayer, 1984) Crop % of world demand Pome fruit 23 Citrus 16 Cotton 6 Tomatoes 6 Cereals other than rice and maize 5 Rice 5 Vegetables 3 Grapes 3 Maize 1.5 68.5% Table 3. Residues of omethoate in crops resulting from supervised trials Crops Formulation/Dose No. Country Days a. Residue (mg/kg) Bayer Report (kg a.i./ha) Appl. 1.Appl. from-to average* No. Apples Folimat 1000 EC 3 Chile 14 0.38 0.38 1) 4411/81 1.0 - 1.5 2 28 0.15 0.15 1) 4410/81 Folimat 500 SL 3 Italy 37 2.3 2.3 1) 4403/81 1.0 3 64 0.46 0.46 1) 4401/81 2 81 0.36 0.36 1) 4402/81 2 108 0.07 0.07 1) 4400/81 Peaches Folimat 500 SL 3 Italy 20 0.32-1.06 0.69 2) 4404-05/81 0.5 - 1.0 2 28 0.36 0.36 1) 4406/81 81 0.03 0.03 1) 4407/81 Hops Folimat spezial 5 FRG 0 14.5-16.8 15.7 2) 4500-01/81 0.54-2.16 7 6.3- 7.2 6.8 2) 14 2.4 2.4 2) 21 1.7 - 2.9 2.3 2) 28 <0.07- 2.1 1.1 2) 35 <0.07- 0.98 0.5 2) * Values in parenthesis indicate number of individual results. Table 4. Omethoate residues in Kiwi fruit - New Zealand Omethoate residues, mg/kg Trial No. g a.i./ kg/ha No. of Days after treatment 100 l Treatments 1 3 5 8 11 15 21 28 35 1 50 2.8 1 2.6 1.6 1.5 1.0 0.8 0.6 0.3 0.6 - 2 75 4.2 1 8.6 5.1 4.6 4.4 3.5 3.8 2-6 1.9 0.8 3 100 5.6 1 9.4 11.0 7.8 5.5 4.1 3.8 4.3 2.9 1.5 One trial in New Zealand when omethoate was applied to apricots at the rate of 60 g/100 l resulted in less than 0.1 mg/kg omethoate 89 days after application. In Plants Wagner et al. (1981) examined the metabolism of omethoate in sugar beets in greenhouse studies. The formation of degradation products was observed shortly after the foliar application of [carbonyl-14C]omethoate. Only about 8% of unaltered parent compound was found in the plants 21 days after the beginning of the study. The following metabolites were isolated and identified as intermediates of omethoate degradation in sugar beets using nuclear magnetic resonance (NMR) and mass spectrometry. The metabolic pathways are shown in Figure 1. a) Phosphorus-containing alteration products O-Methyl S-methylcarbamoylmethyl phosphorothioate (II in Fig. 1) S-Hydroxymethylcarbamoylmethyl O,O-dimethyl phosphorothioate (III). (Dimethoxyphosphinoylthio)acetic acid (IV) b. Hydrolytic and oxidative alteration products Methylcarbamoylmethyl(dithio) acet acid (V) 2,2'-Dithiobis(N-methylacetamide) (VI) N-Methyl-2-(methyldithio)acetamide (VII) methylcarbamoylmethyl-thio) acetic acid (VIII) c. Biotransformation products 3-Hydroxy-3-(methylcarbamoylmethyl-thiol)propionic acid (IX) 3-Hydroxy-3-methylcarbamoylmethylsulphinyl)propionic acid (X) 2-[2-Carboxymethyl)sulphinyl]-2-hydroxyacetic acid (XI) N-Methyl-3-methylcarbamoylmethyldithio)propionamide (XII) 3-hydroxy-3-(methylcarbamoylmethyldithio)propionic acid (XIII) 2-Hydroxy-N,N'-dimethylbutandiamide (XIV)Citric acid (XV) The mono-, di- and tricarboxylic acids were isolated and identified after derivatization with diazomethane. Approximately 30% of the initial radioactivity was found as 3-hydroxy-3(methylcarbamoylmethylthio)propionic acid (IX), which is the major alteration product of omethoate in sugar beets. The oxidation product X of IX was found at a concentration of 10% of the initial radioactivity 21 days after application of the parent compound. Both compounds were found predominantly in the polar methanol and aqueous leaf percolates. The water-soluble, highly polar demethyl-omethoate (II) reached a concentration of 4.2% of the initial radioactivity 21 days after application of the parent compound. Up to 1.4% of the initial radioactivity was found as 2,2'-dithiobis (N-methylacetamide) (VI), which is also water-soluble but distinctly less polar. The authors were able to isolate "N-hydroxymethyl-omethoate" (III), as a short-lived intermediate in the chloroform percolate of the sugar beet leaves at a maximum concentration of 0.6% of the initial radioactivity. The occurrence of genuine intracellular, biochemical degradation processes was confirmed by isolation and identification of 2-hydroxy-N,N'-dimethylbutandiamide (XIV) and citric acid, XV - both at a maximum of 2.5% of the initial radioactivity, using radioactively labelled material. Vacuum infiltration studies (Maximov, 1951) using unlabelled N-methyl thioglycolic acid amide, which must represent a key intermediate product in omethoate metabolism, showed that (methylcarbamoylmethyldithio)acetic acid (V) was the major alteration product of isolated sugar beet leaves after only 30 minutes. 100% recovery of the initial radioactivity was achieved in a "closed system" 14 days after parent compound application. An "open system" resulted in 81, 80 and 73% recovery 7, 14 and 21 days after the beginning of the study, respectively. Components IV, VII and XIII were obtained from unlabelled experimental batches with higher omethoate concentrations. Oehlmann and Wagner (1983) reported that some of the highly polar metabolites of omethoate formed in sugarbeets and soil did not give interpretable electron impact mass spectra and also that the molecular ion for the main metabolite could not be detected. In the field desorption mass spectra the molecular ions of all 3 reported compounds were found. They reported that the spectroscopic data confirmed the structures of the metabolites. In Soil Attention is directed to the publications by Harris and Hitchon (1970) and Duff and Menzer (1973) reviewed in the dimethoate monograph, and to the 1967 evaluation of dimethoate. The high solubility of omethoate in water (miscible in any ratio: Wagner and Frehse, 1976) greatly increases the likelihood of leaching but this is offset by the readiness with which the compound is biodegraded in biologically active soil. In Water Wagner and Frehse (1976) report the stability of dimethoate and omethoate in water as follows: Stability (half-life in days) Temperature°C pH omethoate dimethoate (1) 25° 2 62 176 (1) " 4 74 160 (1) " 6 32.5 125 (1) " 8 2.8 38 (2) 21° 9 0.3 5.8 (1) Taken from Grimmer et al. 1968 (2) Taken from Santi and de Pietri-Tonelli (1959) Grimmer et al. (1968) also determined the following distribution coefficients: omethoate dimethoate chloroform:water 1.15 8.4 ethyl acetate:water 0.5 5.1 benzene:water 0.25 2.2 In Processing and Cooking Steller and Pasarella (1972) showed that omethoate was not significantly affected by the fermentation process in the production of wine by Kawar et al. (1979) showed that residues of dimethoate in wine stored at 24°C were degraded by hydrolysis with a half-life of 30 days. Residues in wine were unchanged during 1 year in frozen storage. The dimethoate monograph describes this work and gives information concerning the fate of omethoate in the processing of olives into oil and pickled olives. Ten Broeke and Dornseiffen (1973) showed that the washing and cooking of Witloof chicory, as practiced in domestic kitchens, destroyed more than half the omethoate residues present in fresh chicory. (See dimethoate monograph for details). RESIDUES IN FOOD IN COMMERCE OR AT CONSUMPTION Dick et al. (1978) published the results of a survey of pesticide residues in the New Zealand diet. This included organophosphorus insecticides. The study involved the analysis of food composites from a simulated New Zealand total diet which was collected at quarterly intervals during 1974/75 from four major cities. The foods were grouped into 8 classes. The methods used for analysis were tested to determine the recovery of a range of pesticide residues at a concentration of 0.01 mg/kg. The recovery of omethoate from 4 major categories was reported to be 100%. Omethoate was found in the fruit group from each of the 4 cities during 2 or 3 periods of the survey. The concentration in the composites ranged from 0.03 mg/kg to 0.04 mg/kg. The investigators reported daily intakes ranging from 6 to 59 micrograms for individuals in the separate cities during different periods of the year. The temporary ADI is equivalent to 35 mg for an individual weighing 70 kg. Only one of the 16 separate composites represented an intake greater than 35 mg per day. The authors comment that omethoate was detected in 60% of the fruit composites whereas a similar survey carried out in 1974 revealed omethoate in only 1% of the samples. It seems highly likely that the omethoate residues were derived from the direct use of omethoate insecticides rather than the metabolism of dimethoate. The Netherlands Government supplied comprehensive information from surveys conducted by the Food Inspection Service, on food commodities produced in The Netherlands and imported. The results of monitoring during 1982 are presented in Table 5 (Netherlands 1984). Since this period the national MRLs have been amended. Additional monitoring data on omethoate from The Netherlands are tabulated in the evaluation of dimethoate. METHODS OF RESIDUE ANALYSIS Some analytical methods for the determination of omethoate residues are included in the present evaluation of dimethoate. Earlier methods are reviewed in the 1967 evaluation of dimethoate and the 1971 evaluation of omethoate. Table 5 Omethoate residues found in monitoring in the Netherlands Food Inspection Services of the Netherlands omethoate 1982 Other witloof french grape citrus endive Parsley chicory apple clementine beans grape fruit orange fruit radish source N N N I I I I I I I I mg/kg 0.000 0.001 - 0.100 1 1 14 2 5 1 1 1 4 1 1 0.101 - 0.200 8 1 1 1 0.201 - 0.400 11 0.401 - 0.600 6 0.601 - 0.800 1 0.800 - 1.000 1 1 > 1.000 1 (2.1) Total 1 1 42 3 5 1 1 1 6 2 1 N = Netherlands I = imported U = unknown --- = national tolerance Multi-residue methods recommended by the Ad Hoc Working Group on Methods of Analysis of the CCPR which apply to both dimethoate and omethoate are noted in the accompanying evaluation of dimethoate. Of these, the methods of Steller and Pasarella (1972) and Wagner and Frehse (1976) are described in more detail below. Steller and Pasarella (1972) reported a gas-liquid chromatographic method for the determination of omethoate and dimethoate residues in plant and animal tissues, milk and eggs, using a 60 cm. × 4 mm. i.d. glass column packed with 11% DC-200 on 60-80 mesh Gas-Chrom Q previously treated with 0.01% Versamid 900. The GLC column was operated at 160°C using a flame photometric detector with a phosphorus filter or at 165°C using an alkali flame ionization detector. The column should be conditioned by injecting omethoate, dimethoate and polyethylene glycol 400. Prior to gas chromatography, it is essential that extracts from cattle and poultry tissues, milk, eggs, cottonseed and oil, safflower seeds, wheat and sorghum grain and alfalfa are cleaned up by silica gel chromatography, primarily to remove oily or waxy extractives which, if not removed, would greatly shorten the effective GLC column life. Steller and Brand (1974) modified these conditions for the determination of omethoate and dimethoate and the potential metabolites de-N-methyl-omethoate, de-N-methyl-dimethoate, N-hydroxymethyl-omethoate, N-hydroxymethyl-dimethoate and N-hydroxymethyl-dimethoate-O-glucoside in grapes. A 120 cm. × 3 mm. i.d. glass GLC column was packed with 1% EGSS-X on Gas-Chrom 0, 60-80 mesh, and operated at 180°C. The retention times were 1.2 minutes for omethoate; 1.5 for dimethoate; 2.3 minutes for des-N-methyl- and N-hydroxymethyl-omethoate; 3.2 minutes for des-N-methyl- and N-hydroxymethyl-dimethoate. The column must be conditioned by firstly injecting Silyl 8 followed by injections of des-N-methyl-dimethoate and grape extracts. The N-hydroxymethyl derivatives are converted to their corresponding des-N-methyl derivatives by heat on the GLC column. Of all the mentioned compounds, only omethoate was present as a metabolite 28 days after the application of dimethoate (sensitivity limit of 0.05 mg/kg). Woodham et al. (1974a,b) determined both omethoate and dimethoate on and in citrus fruits and leaves by a gas chromatographic-flame photometric detection procedure (using phosphorus and sulphur interference filters), although on separate columns. They used 15 cm. × 6 mm. o.d. glass columns packed with 3% DC-200 on 100-200 mesh Gas-Chrom 0 for dimethoate and 10% DC-200 on 100-200 mesh Gas-Chrom for omethoate. The temperature of each column was 200°C. Retention times were not given. The recoveries ranged from 60 to 70%. The method of Steller and Pasarella (1972) has superseded an older method described by Bazzi et al. (1970) for the gas-chromatographic determination of dimethoate residues in cattle meat (using an electron-capture detector). Wagner and Frehse (1976) described a method for the gas-chromatographic determination of omethoate residues in plant material, soil and water. It is intended chiefly for the determination of residues after the application of omethoate, but also permits determination of both omethoate and dimethoate or of dimethoate alone. The prepared samples are extracted by macerating with acetone or aqueous methanol, and the macerate is extracted with chloroform or dichloromethane. The extracts are evaporated to dryness, dissolved in acetone and, without further clean-up, analyzed by gas chromatography using an AFID. Columns packed with 10% DC-200 + 1.5% 0F1 or with 10% OV17, on 80-100 mesh Gas-Chrom 0 are the most suitable for the separation of omethoate and dimethoate. APPRAISAL Omethoate was re-evaluated in conjunction with dimethoate in order to determine whether it would be possible to recommend separate MRLs for the two compounds for residues arising both as a consequence of the metabolism of applied dimethoate and from the use of omethoate directly as an insecticide. Extensive information from the open scientific literature on dimethoate was evaluated and recommendations were made. Additional information on omethoate was received from Australia, The Netherlands, New Zealand and the manufacturers. The similarity in the use patterns of dimethoate and omethoate was noted. Results from 22 residue trials on apples, peaches and hops were reviewed. These served to confirm the validity of the MRLs previously recommended. Results of official trials on Kiwi fruit were received from New Zealand. These enabled the meeting to estimate a maximum residue level which was recommended as a temporary MRL. An extensive study of the metabolism of omethoate in sugar beet plants provided a further inside into the fate of omethoate in plants and an indication that residues are converted into natural plant products through a number of well-defined steps. Results from several national monitoring programmes indicate that the incidence and level of omethoate residues in the diet is low and that the intake by consumers does not exceed the ADI. RECOMMENDATIONS The meeting recommends the following temporary MRL for omethoate on the basis of residues found at harvest. Commodity MRL PHI (mg/kg) Kiwi fruit 2 21 The nine major applications of omethoate represent approximately 70% of the world demand as indicated in Table 2. REFERENCES Bayer Omethoate - Information submitted to FAO. Bayer A.G., 1984 Leverhusen. Bazzi, G., Galluzzi, G., and Nesti, V. Gas-Chromatographic 1970 determination of dimethoate residues in cattle meat. Contributi 1968-69, 1st Ric. Agr. Soc. Montecatini X, 25-30 (Oct. 1970) Beck, E.W., Johnson, J.C., Getz, M.E., Skinner, F.B., Dawsey, L.H., 1968 Woodham, D.W. and Derbyshire, J.C. Effects of feeding dimethoate, its oxygen analog and dimethoate-treated silage to cattle. J. Econ. Entom., 61 (3):605-610. Chamberlain, W.F.P.E., Gatterdam and Hopkins, D.E. The metabolism of 1961 labeled dimethoate in sheep. J. Econ. Entomol., 54 (4): 733- 740. Dauterman, W.C., Casida, J.E., Kraake, J.B., and Kowalczyk, T. Bovine 1959 metabolism of organophosphorus insecticides. Metabolism and residues associated with the oral administration of dimethoate to rats and three lactating cows. J. Agr., Food Chem., 7:188. Dick, G.L., Heenan, M.P., Love, J.L., Udy, P.B. and Davidson, F. 1978 Survey of trace elements and pesticide residues in the New Zealand diet. 2. Organochlorine and organophosphorus pesticide residue content. N.Z.J. Sci., 21 (1):71-78. Duff, W.G. and Menzer, R.E. Persistence, mobility, and degradation of 1973 14C-dimethoate in soils. Environ. Entomol. 2 (3):309-318. Ecker, W., and Coelln, R. Biotransformation of omethoate. PF-Report: 1981 1574 Aug.7, 1981 from PH-E Isotope Laboratory, at the Institute of Pharmacokinetics, Wuppertal. Mobay Chemical Corporation (Unpublished). Grimmer, F., Dedek, W. and Liebnitz, E. Zur Kenntris der 1968 N-Butylchomalogen des Dimethoate. I. Hydrolysegesch- Wurdigkeit und-mechanismus. Z. Naturforsch. 23. 13-17. Harris, C.R. and Hitchon, J.L. Laboratory evaluation of candidate 1970 materials as potential soil insecticides. II. J. Econ. Entomol., 63 (1):2-7. Kaplanis, J.N., Robbins, W.E., Darrow, D.I., Hopkins, D.E., Monroe, 1959 R.E., and Treiber, G. The metabolism of dimethoate in cattle. J. Econ. Entomol. 52 (6):1190-1194. Kawar, N.S., Iwata, Y., Dusch, M.E. and Gunther, F.A. Behaviour of 1979 dialifor, dimethoate and methidathion in artificially fortified grape juice processed into wine. J. Environ. Sci. Health, Part B, 14 (5):505-513. Maximow, N.A., Kurzes Lehrbuch der Pflanzenphysiologie, S. 354-361. 1951 Verlag Kultur and Fortschritt, Berlin. Netherlands Information on pesticides included in the JMPR priority 1984 list. Submission to FAO dated 4 May 1984. Oehlmann, L. and Wagner, K. Metabolism of omethoate in soil and sugar 1983 beet. Anal. Chem. Symp. Ser., Chromatogr. Mass Spectrom. Biomed, 14, 2:53-6. Santi, R. and de Pietri-Tonelli, P. Mode of action and biological 1959 properties of dimethoate. Nature 183:398 (quoted by Dauterman et al., 1960). Steller, W.A. and Pasarella, N.R. Gas-liquid chromatographic method 1972 for the determination of dimethoate and dimethoxon residues in plant and animal tissues, milk and eggs. J. Assoc. Offic. Anal. Chem., 55 (6):1280-1287. Steller, W.A. and Brand, W.W. Analysis of dimethoate-treated grapes 1974 for the N-hydroxymethyl and de-N-methyl metabolites and for their sugar adducts. Agr. Food Chem., 22 (3): 445-449. Ten Broeke, R. and Dornseiffen, J.W., Residuen van dimethoate en 1973 omethoate in witlof in diverse stadia de hueshoudelijke bereiding. Report KvW 173/WRV (73) 34.6.2.1 Keuringsdienst van Waren - Amsterdam November 1973. Wagner, K. and Frehse, H. Method for the determination of residues of 1976 Folimat insecticide/acaricide. Pflanzenschutz-Nachrichten Bayer, 29 (1):54-66. Wagner, K., Neitzel, H., Oehlmann, L. and Pahlke, H. Metabolism of 1981 omethoate in sugar beets. Bayer AG Report RA-6/OEL,2 Bayer AG Leverkusen, Federal Republic of Germany, Jan. 23, 1981. Woodham, D.W., Reeves, R.G., Williams, C.B., Richardson, H. and 1974a Bond,C.A. Residues of dimethoate and its oxygen analogue on and in citrus leaves following helicopter treatment of the trees with dimethoate ultra-low volume concentrate and high volume spray. J. Agr. Food Chem., 22 (4):731-733. Woodham, D.W., Hatchett, J.C. and Bond, C.A. Comparison of dimethoate 1974b and dimethoxon residues in citrus leaves and grapefruit following foliar treatment with dimethoate wettable powder with and without surfactant. J. Agr. Food Chem., 22 (2):239-242.
See Also: Toxicological Abbreviations Omethoate (WHO Pesticide Residues Series 1) Omethoate (WHO Pesticide Residues Series 5) Omethoate (Pesticide residues in food: 1978 evaluations) Omethoate (Pesticide residues in food: 1979 evaluations) Omethoate (Pesticide residues in food: 1980 evaluations) Omethoate (Pesticide residues in food: 1981 evaluations) Omethoate (Pesticide residues in food: 1985 evaluations Part II Toxicology)