VAMIDOTHION JMPR 1973 IDENTITY Chemical name O,O-dimethyl S-[2-(1-methylcarboylethylthio)ethyl] phosphorothioate. Synonyms 10 465 R.P., Kilval(R), Trucidor(R). Structural formulaOther information on identity and properties Physical state: White crystalline solid (pure) Amber waxy solid (technical) Melting point: 40°C (pure) Solubility: Water - about 4 g/ml Benzene, toluene, methyl ethyl ketone, ethyl acetate, acetonitrile, methylene chloride, anisole, cyclohexanone, chloroform - 1 g/ml [xylene - 0.125 g/ml petroleum ether, cyclohexane - insoluble Volatility: Very low. Negligible loss under vacuum (2 mm Hg) at 20°C. Stability: The technical solid decomposes slowly at room temperature but is stable in organic solvents (e.g. cyclohexanone, methyl ethyl ketone). Hydrolyzed by alkali Optical Vamidothion consists of a mixture of optically isomerism: active isomers. Their systemic activity as pesticides is similar, but the D form shows higher contact activity as an araricide. Formulation: Water-miscible solution containing 400 g/l. EVALUATION FOR ACCEPTABLE DAILY INTAKE Biochemical aspects Biodegradation One NC-5 mouse was administered 30 mg 32P vamidothion orally. Urine collected over the following 24 hours contained 32P labelled phosphoric acid, 0-methyl phosphate, 0,0-dimethyl phosphate and an unknown compound. Rat liver homogenate incubated for two hours with 32P labelled vamidothion produced 0,0-dimethyl phosphate, phosphoric acid and an unknown compound which was possibly dimethyl phosphothionate. The same metabolites were produced by incubation of 32P labelled vamidothion with plant leaves. In addition desmethyl vamidothion was detected; this may not have been detected as a metabolite in animals because of the low activity of 32p incorporated into the vamidothion (Morikawa and Saito, 1969). The oxidation product, vamidothion sulfoxide, has been demonstrated to be formed in plants (Desmoras et al., 1961). Effects on enzymes Vamidothion inhibits cholinesterase in vitro and in vivo. A concentration of 40 mg/l caused 50% inhibition of enzyme activity of plasma. Four hours after guinea-pigs had received 40 mg vamidothion/kg orally, 81% inhibition of plasma and 20% inhibition of cellular enzyme occurred. With higher dosage levels the plasma cholinesterase level remained stationary but cellular enzyme activity decreased (Dubost et al., 1960). TOXICOLOGICAL STUDIES Special studies on the metabolites A summary of the results of acute toxicity studies on vamidothion sulfoxide is shown in Table 1. A test for neurotoxicity was carried out in the same manner as for vamidothion itself. Positive controls showed signs of paralysis in 9-14 days while vamidothion sulfoxide was without effect (Anon., 1966b). TABLE 1. THE ACUTE TOXICITY OF VAMIDOTHION SULFOXIDE Species Sex Route LD50 References Mouse Oral 80 Desmoras et al., 1961 Rat F Oral 160 Desmoras et al., 1961 Rivett and Corbett, 1966 Guinea-pig Oral 205 Desmoras et al., 1961 Chicken F s.c. 60 Anon., 1966b A short-term study was carried out on groups of five male and five female rats which were fed diets containing 0, 5, 50, 100 and 200 ppm vamidothion sulfoxide for three months. The degree of depression of cholinesterase activity was similar to that in animals receiving the same dosage levels of vamidothion. The 100 and 200 ppm dosage levels depressed cholinesterase levels to approximately 20% And 12% respectively of the control level. Cholinesterase activity returned to normal within four weeks when vamidothion sulfoxide was withdrawn from the diet. Histological examination of two male and two female rats from each group showed no abnormality attributable to ingestion of the test compound (Rivett and Corbett, 1966). A three generation reproduction study with each generation producing two litters, was carried out on groups of 20 male and 40 female rats (generation Fo, test animals), 40 male and 80 female (generation Fo controls) or 10 male and 30 female (other generations). Animals were administered 0, 5, 15 or 45 ppm of vamidothion sulfoxide in the diet for four weeks before the first mating. The study included tests in which some female test animals were mated with untreated males and some untreated females were mated with treated male animals. A small number of females of the F1b and F2b generations were killed after the thirteenth day of pregnancy and the uterus examined for implantation sites, viable and resorbed embryos and macroscopically observable abnormalities. The F1a, F2a and F3a litters were killed at weaning and autopsied. Rats of the F1b and F2b litters not used to produce the next generation were killed at weaning and autopsied. The F3b litters were killed at weaning and the heart, kidneys and livers weighed and spleen, suprarenals, thyroid and (in the case of the highest dosage group) brain examined histologically. The results showed that the dosage levels of vamidothion sulfoxide used had no untoward effect on treated animals, in particular on fertility or reproductive activity of rats. There was no indication of teratogenic activity in this study (Ganter et al., 1969b). Special studies on neurotoxicity Groups of five white leghorn chickens were injected s.c. with 60 and 120 mg vamidothion/kg (1X and 2X LD50 dose). Positive control groups received 20 and 40 mg di-isopropyl-fluorophosphoridono. All birds were treated with atropine and P2AM. No signs of neurotoxicity appeared in vamidothiontreated birds while positive control groups developed paralysis in 9-14 days (Anon., 1966b). Special studies on the pharmacological effects The motility of mice was unaffected by 10 mg vamidothion/kg orally and exploratory activity and conditioned reflexes were normal in rats treated orally with 30 mg/kg. No effect was found on neuromuscular transmission, respiratory rate, ECG or heart rate and the effects of i.v. adrenalin and i.v. acetylcholine were largely unchanged by treatment with vamidothion, Salivary excretion was increased, slightly and isolated intestine and uterus preparations were affected weakly by vamidothion (Julou et al., 1966). Mice were administered 100 mg vamidothion/kg orally (LD50 dose). Some also received atropine, pralidoxime or both. Ten to 20 mg atropine/kg i.p. provided 60-70% and 50 mg pralidoxime/kg i.p. 100% protection against vamidothion (Dubost et al., 1960; Anon., 1966a). Groups of 10 rats received 3 x LD50 dose (300mg/kg) of vamidothion orally. One group received 17.4 mg atropine/kg i.p. when signs of intoxication showed. Another received atropine plus 50 mg P2AM/kg i.p. All control animals died within 45 min., 7-10 animals with atropine died in 7-24 hours and three animals receiving atropine and P2AM died. All of the latter group appeared normal two hours after treatment while those on atropine alone appeared ill (Anon., 1966a). Special studies on reproduction Rat. A three-generation reproduction study, with each generation producing two litters, was carried out on groups of 20 male and 40 female rats which were administered 5, 15 and 45 ppm vamidothion in the diet. The control group consisted of 40 males and 80 females. Animals of the Fo generation received diets for 11 weeks before being mated. The study included tests in which some female test animals were mated with untreated males and untreated females were mated with treated males. A small number of females of the F1b and F2b generations were killed after the thirteenth day of pregnancy and the uterus examined for implantation sites, viable and resorbed embryos and macroscopically apparent abnormalities. The F1a, F2a and F3a, litters were killed at weaning and autopsied. Animals of the F1b and F2b groups not used to produce the next generation were killed at weaning and autopsied. The F3b litters were killed at weaning and the heart, kidneys and liver weighed and the spleen, suprarenals, thyroid and (with the highest dose level only) the brain examined histologically. Haematological studies and examinations of bone marrow of one animal of each sex of each group were carried out. Because of a technical error some animals chosen as parents of the second and third generations may have been produced from untreated male parents; the proportion so produced is uncertain. All females were, however, treated with the correct diets. Results show that at the dosage levels used vamidothion had no untoward activity on rats, in particular on their fertility or reproductive functions, There was no indication that vamidothion is teratogenic (Ganter et al., 1969a). Acute toxicity The results of acute toxicity studies on vamidothion are summarized in Table 2. Administration of vamidothion in fatal doses produced signs typical of cholinesterase inhibitors. Groups of 20 mice were administered half the LD50 dose of vamidothion plus half the LD50 dose of demeton-methyl, parathion, phencapton, dimetboate, ethion, malathion, azinphos ethyl, mevinphos or phosphamidon and observed for five days. No significant potentiation was observed (Anon., 1966c). Short-term studies Rat. Groups of 10 male rats were administered 3 or 6 mg vamidothion/kg/day orally for one month. It was reported that body weight was unaffected, no animals died and no clinical signs of toxicity occurred. Haematological examination including examination of bone marrow and chemical analysis of urine and blood showed no abnormalities except for blood cholinesterase activity which was depressed by 50% (3 mg/kg/day) or 607 (6 mg/kg/day). Brain cholinesterase levels were not depressed. The weights and histological appearance of organs were unaffected by treatment (Dubost et al., 1960). TABLE 2. SUMMARY OF THE RESULTS OF STUDIES ON ACUTE TOXICITY Species Sex Route Purity LD50 References Mouse Oral p 43 Johnston and Rivett, 1966 Mouse Oral p 34 Dubost et al., 1960 Mouse M+F Oral Tech. 64 Pasquet and Mazuret, 1972a Mouse Oral Tech. 40 Pak, 1970 Mouse s.c. p 34 Johnston and Rivett, 1966 Mouse Dermal p 1450 Johnston and Rivett, 1966 Mouse Dermal Tech. 1060 Pasquet and Mazuret, 1972a Rat M Oral p 100 Johnston and Rivett, 1966 Rat M Oral p 105 Dubost et al., 1960 Rat M+F Oral p 105 Pasquet and Ma.uret, 1972b Rat F Oral p 77 Desmoras et al., 1961 Rat M+F Oral Tech. 168 Pasquet and Mazuret, 1972a Rat Oral Tech. 103 Pak, 1970 Rat F Oral p 64 Johnston and Rivett, 1H6 Rat M s.c. p 48 Johnston and Rivett, 1966 Rat F s.c. p 35 Johnston and Rivett, 1966 Guinea-pig Oral p 85 Dubost et al., 1960 Rabbit Oral Tech. 160 Pak, 1970 Rabbit Dermal p 1160 Quoted in Johnston and Rivett, 1966 Rabbit M+F Dermal Tech. 3000 Pasquet and Mazuret, 1972a Dog M+F Oral p 110 Julou and Pasquet, 1967 Mouse Oral p 50 Desmoras and Fournel, 1961 Mouse Oral l-isomer 68 Desmoras and Fournel, 1961 Mouse Oral d-isomer 34 Desmoras and Fournel, 1961 M = male F = female P = pure Groups of five male and five female rats were fed on diets containing 0, 0.2, 1 and 5 ppm vamidothion for six weeks after which the test substance was withdrawn from the diet. Regular observation of plasma and erythrocyte cholinesterase activity showed that only in the plasma of female rats on the 5 ppm diet was enzyme activity consistently depressed to a significant extent. The enzyme level returned to normal within five weeks. Cholinesterase activity was not depressed significantly at lower dosage levels (Wheldon et al., 1969). Groups of five male and five female rats were fed on diets containing 0, 5 and 50 ppm vamidothion for three months. No ill effect was seen on growth or general health. Blood cholinesterase levels were reduced to approximately 75% and 25% respectively of the control level in the 5 and 50 ppm groups. Cholinesterase levels returned to normal within four weeks when vamidothion was withdrawn from the diet. Histopathological examination of two rats of each sex from the 50 ppm group showed no abnormalities related to ingestion of the compound (Rivett and Corbett, 1966). Groups of rats were administered, by gavage, doses of approximately 2, 5 or 10 mg vamidothion/kg daily for three months. At the end of the test serum acetylcholinesterase activity was decreased to 35%, 12% and 8%, respectively, of the normal value (Pak, 1970). Dog. Groups of three dogs were administered orally 0, 1 and 2 mg/vamidothion/kg/day for one month. Two dogs received 8 mg/kg/day for one month. No effect was seen on growth except for one animal on the highest dose level which developed diarrhoea (cause unknown). Haematological indices and blood coagulation were normal. Slight differences between groups in urine urobilinogen, glucose and bile salts, serum protein, PSP clearance and behaviour could not be attributed to treatment. In particular no neurological abnormalities were seen although erythrocyte cholinesterase was severely depressed (100% inhibition at sixteenth day with 8 mg/kg dosage regime). In six dogs receiving 1 and 2 mg/kg/day no abnormalities were found on gross and histopathologic examination. (Dubost et al., 1960). Groups of two male and two female beagle dogs were fed on diets containing 0, 0.2, 1 and 5 ppm vamidothion for five to six weeks. Animals on the lowest dosage level were then fed for a further four weeks on diet containing 20 ppm vamidothion, after which they were observed for four more weeks on normal diet. No clinical signs of abnormality were seen in any group. The plasma and erythrocyte cholinesterase levels were slightly depressed in dogs on the highest dosage. These levels returned to normal within two weeks of return to a normal diet. No abnormalities in the appearance or weight of organs were found in any group (Noel et al., 1969). Long-term studies No data are available. Observations in man Groups of 6-11 normal healthy volunteers of both sexes were administered 9.6 or 37.2 µg vamidothion/kg/day orally in aqueous solution on five days each week for three weeks. Other groups received 78.8 or 122.8 µg vamidothion/kg/day in aqueous solution for five weeks. A control group was studied for 25 weeks. No clinical signs or symptoms were found which could be attributed to treatment. Plasma cholinesterase, estimated weekly, showed no consistent depression in any group but erythrocyte cholinesterase was depressed in three of six volunteers receiving 122.8 µg/kg/day. The no-effect level was considered to be 78.8 µg/kg/day, (calculated to be equivalent to 56.3 µg/kg/day if vamidothion was administered every day without a break) (Noel et al., 1970). Serum and erythrocyte cholinesterase levels were determined periodically in workers who had been involved in the manufacture of vamidothion over a period of several months to a few years. Enzyme levels were also determined in experimentalists exposed several times a year to vamidothion over a seven-year period. The actual exposure is uncertain. Fluctuations in enzyme levels in both groups were within the limits of normal (Celice et al., 1966), Comments It has been shown that vamidothion is partly absorbed from the gastric intestinal tract and is excreted in urine. Several metabolic products have been found in urine; these ewe compounds are also produced by liver slices. One metabolite (desmethyl vamidothion) was shown to be produced by plants but has not yet been found as a metabolite in animals. Vamidothion sulfoxide has been examined toxicologically but the toxicity of other metabolites has not apparently been examined. Vamidothion depresses serum cholinesterase activity at lower concentrations than it depresses the activity of erythrocyte cholinesterase, except in dogs. Brain cholinesterase activity is less affected. The dosage level of vamidothion which is without effect in man is just over 50 µg/kg/day. The no-effect level with regard to cholinesterase depression was 1 ppm in the diet of rats and 5 ppm in the diet of dogs. These dietary levels are approximately equivalent to 50 µg/kg/day in rats and 125 µg/kg/day in dogs. Studies showed that vamidothion had no adverse effects on reproduction. Short-term tests were carried out in only small numbers of dogs and rats and although no ill effects other than that on cholinesterase activity were detected, the observations were not sufficiently extensive to eliminate the possibility that the compound has other significant effects, No long-term tests have been reported. TOXICOLOGICAL EVALUATION It is not possible, on the information available, to estimate an ADI for vamidothion. RESIDUES IN FOOD AND THEIR EVALUATION Use pattern Vamidothion is a systemic organophosphorus aphicide and miticide. Its most important use is on apples and pears against the woolly apple aphid. It is also used on other pome fruits, sugar beet and brussels sprouts. and to a lesser extent on grapes, cereal crops, sugar cane and hops. Pre-harvest treatments The recommended uses are as follows: Orchard fruits. In France, Western Europe, Australia, New Zealand and South Africa, a single treatment at 40-50 g a.i./100 l. For low-volume application, a rate of 0.4-0.5 kg a.i./ha is used. In Great Britain an application at 20 g/100 l before flowering, and one or two treatments at 40 g/100 l after flowering are recommended for apple and pear; a single application at 40 g/100 l after flowering for plum and cherry. Grapes. A single treatment at 40-50 g/100 l during active sap movement. A second similar treatment if necessary. Citrus fruits. 60-80 g/100 l. Hops. In England, three applications at 700 g/ha, with a minimum pre-harvest interval of four weeks. In France, Belgium and Germany, one application at 50 g/100 l when the aphid first appears. Rice. Three applications at 50 g/100 l (600 g/ha). Cotton. 40-60 g/100 l high-volume application, repeated, if necessary. Post-harvest treatments None known. Other possible uses Trials against aphids of maize and sorghum have been successful. Aphids and red spider of strawberries, tomatoes and beans have been successfully controlled. A pre-harvest interval of six weeks is recommended. Aphids have been controlled in trials in France, Brazil and Japan by brushing tree trunks with vamidothion during active sap movement. Residues resulting from supervised trials Residue data are available from supervised trials in France, Germany, Switzerland and the United Kingdom (Rhône-Poulenc, 1966, 1969; May and Baker Ltd. 1963), together with limited data on application to sugar cane in Trinidad (May and Baker Ltd, 1973). These data have been deposited with FAO and are summarized in Table 3. Residues of vamidothion are converted to the sulfoxide in or on the plant, and residues reported in the table refer to the sum of the parent compound and the sulfoxide. The combined residue is unusually persistent. The half-life on apples and pears is between 35 and 45 days, and more limited results on peaches, plums, grapes, cherries and straw berries indicate a similar persistence. Half-life periods on cereals and vegetables are generally between 6 and 20 days. Data from supervised trials in Japan (Tomizawa, 1973) show very low residues, usually below 0.02 ppm in a wide range of crops. As these data apparently refer only to the parent compound, they are not quoted in the Table. Fate of residues In plants. As mentioned above, the main biologically active product is the sulfoxide, and this is the main terminal residue. The sulfone is not found to any significant extent, but it has been detected as a metabolite in citrus leaves kept at a low temperature. (Results quoted by Tomizawa, 1973). The other main metabolites are demethyl vamidothion, phosphoric acid and diethyl phosphate (Morikawa and Saito, 1969). In animals. In experiments with 32B-vamidothion (Morikawa and Saito, 1969), 69% of the activity in the urine of dosed mice appeared as phosphoric acid and its mono and dimethyl esters. The remaining 31% was an unknown metabolite. The dimethyl compound was not detectable. In the same series of experiments, rat liver homogenate metabolized 55% of the vamidothion with which it was incubated to the unknown metabolite, 31% to phosphoric acid and 14% to diethyl phosphate. Methods of residue analysis Residues normally consist essentially of a mixture of vamidothion and its sulfoxide. Three methods have been developed by the Rhône-Poulenc Laboratories to determine this mixture after suitable clean-up: gas chromatography after oxidation of both compounds to the sulfone, colorimetric determination of total phosphorus after mineralization, and bioassay (Rhône-Poulenc, 1972). The gas-chromatographic method should be suitable for regulatory purposes. The other two are non-specific but are suitable for determining residues arising from supervised trials: most of the data in Table 3 were obtained by these methods, often by both of them. Identity can be confirmed, and the parent compound and sulfoxide separately determined semi-quantitatively if required, by TLC (Rhône-Poulenc, 1972). Determination by gas chromatography (Desmoras et al., 1972) The sample is blended with buffered methanol or acetone and the organic solvent evaporated. The extract is washed with petroleum ether, in which vamidothion and its sulfoxide are insoluble, and then extracted continuously with dichloromethane. (Vamidothion is readily extracted, but continuous extraction is needed for the sulfoxide.) An aliquot of the solution is evaporated to dryness and oxidized with potassium permanganate in aqueous acetone. The resulting sulfone is extracted with dichloromethane and transferred to benzene for determination by gas chromatography on DEGS (diethylene glycol succinate) stationary phase with electron capture detection. Recoveries are within a range of 80-110% and the limit of determination is about 0.05 ppm. The method described is more sensitive than methods in which thermionic (Ruzicka et al., 1967) or flame photometric (Mestres, 1973) detection is used. Separate determination of vamidothion and the sulfoxide by GLC without oxidation is unsatisfactory because of the large difference between their retention times. The two compounds can be differentiated if required by first extracting vamidothion by shaking with dichloromethane, then obtaining the sulfoxide by continuous extraction and oxidizing the residues in the two extracts to the sulfone separately. Total phosphorus determination. The residue is extracted, and cleaned-up as in the GLC method and the extract is evaporated to dryness. The residue is digested with nitric and sulfuric acids and phosphorus is determined colorimetrically as molybdenum blue. The limit of determination is about 0.1 ppm. Biological determination. The solvent is evaporated from the dichloromethane extract obtained as described above, and some of the co-extractives are removed by precipitation from acetone solution at -70°C. The acetone in the filtrate from this step is evaporated and replaced with water, and residues of vamidothion plus sulfoxide are determined by bio-assay with Daphnia pulex as the test organism. The procedure has been described in detail by Desmoras (1963). Thin-layer chromatography. Thin-layer chromatography, TLC, is useful as a confirmatory test of identity and to separate the parent compound from the sulfoxide. It is carried out on the cleaned-up dichloromethone extract, using silica gel which has been activated by heating at 120°C for at least one hour. Approximate Rf values of vamidothion, its sulfoxide and its sulfone on silica gel GF254 (Merek), developed with various solvent systems, are listed in Table 4. Separated spots can be detected by esterase inhibition or by spraying with iodoplatinate, palladium chloride or nitrobenzylpyridine. The enzyme inhibition method is the most sensitive, with detection limits of 30-50 ng for the three compounds. TLC of the dichloromethane extract does not satisfactorily indicate the ratio of vamidothion to sulfoxide in the original residue, because some vamidothion is converted to sulfoxide during the continuous extraction. Appraisal Vamidothion is an organophosphorus compound with pronounced systemic activity, effective against aphids and mites not resistant to organophosphorus compounds. It is applied as water-miscible solution to pome fruits, sugar beet, brussels sprouts and, to a lesser extent, cereal crops, grapes, sugar cane and hops. By far the most important use is on apples and pears against woolly apple aphid. Vamidothion is particularly persistent. Numerous studies have been carried out in France, England, Switzerland and Germany and these indicate the half-life in pome fruit to be between 35 and 45 days. The half-life on cereals and vegetables is generally between six and 20 days. The main biologically active metabolite is the sulfoxide which has a higher systemic insecticidal activity than the parent compound. The sulfone is not found in plants to any significant extent. Residues consisting of a mixture of the sulfoxide and the parent compound, can be determined by bio-assay or estimation of total phosphorus. The recommended method, which should be suitable :Per regulatory purposes, is by gas chromatography with electron-capture detection after oxidation to the sulfone. The limit of determination is about 0.05 ppm. TLC can be used for confirmation of identity. The limited data available on sugar cane indicated residues of about 0.2 ppm soon after application, decreasing to below 0.05 ppm before harvest. As the available information on wheat and sunflower was restricted to the whole plant, it was not suitable for judging the probable residue level in the grain and seed. National tolerances In Switzerland a tolerance of 0.6 ppm has been established for residues arising from applications to fruit trees, except cherry, with the end of May as the last date of application. TABLE 3. VAMIDOTHION RESIDUES IN CROPS Dosage rate, Residue (ppm vamidothion + sulfoxide) after interval (days) Crop Country a.i. g/100 l or kg/ha 0-2 5-11 13-18 20-30 34-39 41-49 52-69 72-95 >100 Apple France 50 g/100 l 3.0 2.5 2.0 1.6 1.3 1.1 50 g/100 l 0.1 2 x 50 g/100 l 1.7 2 x 50 g/100 l 0.3 0.3 Germany 60 g/100 l 0.7 < 0.1 0.5 0.5 0.4 1.0 kg/ha 1.1 0.6 0.3 1.8 kg 0.75 0.2 2 x 1.8 kg/ha 0.7 0.2 Switzerland 50 g/100 l 0.85 < 0.65 0.8 50 g/100 l 0.5 England 40+80 g/100 l 3.5* 1.6* 1.7* 2.4* 40+80 g/100 l 3.4 Pear France 50 g/100 l 0.1 2 x 50 g/100 l 0.2 0.2 England 40 g/100 l 1.5* 0.6* 1.9* >0.2* 40+80 g/100 l 2.1* 1.8* Peach France 50 g/100 l 0.1 2 x 50 g/100 l 0.4 0.3 Cherry England 80 g/100 l >0.4* >0.4* >0.4* Plum England 80 g/100 l 1.9 TABLE 3. (Cont'd.) Dosage rate, Residue (ppm vamidothion + sulfoxide) after interval (days) Crop Country a.i. g/100 l or kg/ha 0-2 5-11 13-18 20-30 34-39 41-49 52-69 72-95 >100 Grape France 50 g/100 l 0.2 2 x 50 g/100 l 0.25 0.15 Hop France 3 x 50 g/100 l <0.1 " (fresh and dry cones) 3 x 100 g/100 l <0.1 " (fresh cones) England 25+40 g/100 l < 0.5 Wheat (whole plant) France 50 g/100 l 9 4.1 1.4 0.4 0.4 50 g/100 l approx. 10 4.2 1.9 " (grain) 50 g/100 l 0.25 50 g/100 l 0.1 Sugar beat (leaves) France 50 g/100 l 1.1* 0.2* " " (root) 50 g/100 l 0.2 Sunflower (leaves) France 75 g/100 l 60 23 19 10 7 5 Strawberries Scotland 50 g/100 l 0.6* 0.6* 0.6* 50 g/100 l 0.3 Broad beans France 50 g/100 l 81 64 51 40 23 13 (glasshouse,leaves) French beans France 50 g/100 l 87 35 21 8.5 (glasshouse, leaves) Sugar cane Trinidad 0.9 kg/ha 0.2 0.1 0.9 kg/ha 0.2 < 0.05 " " (juice) 0.9 kg/ha < 0.05 * Separate crop treatments. TABLE 4. Rf VALUES OF VAMIDOTHION, ITS SULFOXIDE AND ITS SULFONE ON SILICA GEL* IN SEVERAL SOLVENT SYSTEMS Approximate Rf Developing solvent Vamidothion Sulfoxide Sulfone Dichloromethane-methanol (90:10, v/v) 0.65 0.4 0.55 Ethyl acetate-methanol (75:25, v/v) 0.65 0.5 0.65 Acetonitrile-methanol (97:3 v/v) 0.5 0.1 0.65 Acetone-dimethylformanide (99:1, v/v) 0.6 0.35 0.65 * Silica gel GF254 (Merck) activated at 120°C for one hour before use. RECOMMENDATION As no acceptable daily intake could be established no tolerances are recommended. Following officially acceptable use in various countries residues of vamidothion can occur in the following commodities up to the levels indicated. The guide-lines indicated below are unlikely to be exceeded as a result of the recommended use of vamidothion. Guide-line levels (based on a pre-harvest interval of six weeks) Apples and pears 2 ppm Brussels sprouts 1 ppm Sugar beet 0.5 ppm Grapes 0.5 ppm Hops 0.2 ppm FURTHER WORK OR INFORMATION Required (before an acceptable daily intake can be established) 1. Long-term studies in at least one animal species. 2. Adequate short-term studies in several species including a non-rodent species. 3. Studies to identify metabolites and investigate their toxicity. 4. Studies on the nature and level of residues in animal products from the feeding of residues at levels occurring on food wastes. 5. Information showing the fate of residues in the major crops in countries with different meteorological and growth conditions. REFERENCES Anon. (1966a) Vamidothion. Etude dos Antidotes. Submitted by Société des Usine Chimiques, Rhône-Poulenc. Unpublished report Anon. (1966b) Vamidothion. Essai do neurotoxicité, submitted by Société des Usines Chimiques, Rhône-Poulenc. Unpublished report Anon. (1966e) Vamidothion. Etude de la potentialisation sur souris avec des insecticides comerciaux, submitted by Société dos Usines Chimiques, Rhône-Poulene. Unpublished report Celice, J., Fournel, J. and Koenig F. (1966) Evaluation des risques l'intoxication par le vamidothion (10.465 R.P.) au cours de sa fabrication et do son experimentation plein champ, submitted by Société dos Usines Chimiques, Rhône-Poulene. Unpublished report Desmoras, J. (1963) Biological determination of vamidothion in plants. Mededel. Landbouwhogeschool Opzoekingasta, Staat Gent, 28: 731-742 Desmoras, R. and Fournel, J. (1961) Insecticides. Activités insecticides ot toxicités des 12.151.R.P. et 12.164 R.P. isomeres optiques du 10.465 R.P. Submitted by Société des Usines Chimiques, Rbône-Poulenc. Unpublished report Desmoras, R., Fournel, J. and Koenig F. (1961) Insecticides. Activités insecticides et toxicités comparées des 10.465 R.P. et 11.905 R.P. Submitted by Sociétés des Usines Chimiques, Rhône-Poulene. Unpublished report Desmoras, J., Laurent, M. and Buys, M. (1972) Unpublished report No. 15,893 submitted by Rhône-Poulene Dubost, J.P., Fournel, J., Ganter, P., Julou, L. and Myon, M. (1960) Produit No. 10.463 R.P. Toxicité ague, tolerance locale, activités anticholinesterasique et antidotes, toxicité chronique chez le rat et le chien. Submitted by Société dos Usines Chimiques, Rhône-Poulenc. Unpublished report Ganter, P., Julou, L., Pasquet, J., Delesque, M. and Durel, J. (1969a) Vanidothion (10.465 R.P.) activités sur les fonctions de reproduction du Rat (Essai sur 3 generations). Submitted by Société des Usines Chimiques, Rhône-Poulenc. Unpublished report Ganter, P., Julou, L., Pasquet, J. and Delesque, M. (1969b) Vamidothion (11.905 R.P.) activité sur les fonctions de reproduction du rat (Essai sur 3 generations). Submitted by Société des Usines Chimiques, Rhône-Poulenc. Unpublished report Johnston, J.P. and Rivett, K.F. (1966) Vamidothion. Acute toxicity to mammals. Unpublished report of May & Baker, Ltd. submitted by Société des Usines Chimique, Rhône-Poulenc Julou, L., Ducrot, R., Gardens, M.C., Detaille, J. Fee, C., Garret, C. and Pasquet, J. (1966) Etude pharmacologique du vamidothion (10.465 R.P.) comparativement au parathion (3.470 R.P.). Submitted by Société des Usines Chimiques, Rhône-Poulenc. Unpublished report Julou, L. and Pasquet, J. (1967) Vamidothion (10.465 R.P.), toxicité aigue chez le chien par vole orals. Submitted by Société des Usines Chimiques, Rhône-Poulenc. Unpublished report May and Baker Ltd. (1963) Unpublished report May and Baker Ltd. (1973) Unpublished report Mestres, R. (1973) Personal communication Morikawa, O. and Saito, T. (1966) Degradations of vamidothion and dimethoate in plants, insects and mammals. Bochu Kagaku, 31: 130-135 Morikawa, O. and Saito, T. (1969) Degradation of vamidothion and Dimethoate in plants, insects and mammals. Unpublished report of the Laboratory of Applied Entomology, Nagoya University, Japan, submitted by Société des Usines Chimique, Rhône-Poulenc Noel, P.R.B., Coote, S. and Street, A.E. (1969) Vamidothion (10.465 R.P.). Determination of no-effect level in Beagle dogs. Unpublished report of Huntingdon Research Centre submitted by Société des Usines Chimique, Rhône-Poulenc Noel, P.R.B., Haynes, G. and Street, A.E. (1970) Vamidothion. Determination of no-effect level in human volunteers. Unpublished report of Huntingdon Research Centre submitted by Société des Usines Chimique, Rhône-Poulenc Pak, L.V. (1970) The toxicity of vamidothion on warm-blooded animals. Gig. truda i Praftabol, 2: 58-9 Pasquet, J. and Mazuret, A. (1972a) Vamidothion (10.465 R.P.) - Kilval ou formule S.A.E. 1700 (solution A 400 9/litro) Submitted by Société des Usines Chimiques, Rhône-Poulenc. Unpublished report Pasquet, J. and Mazuret, A. (1972b) Vamidothion (10.465 R.P.) - Toxicité aigue chez le rat par voie orals, Submitted by Société des Usines Chimiques, Rhône-Poulenc. Unpublished report Rivett, K.F. and Corbett, K. (1966) Insecticides Vamidothion. The acute and chronic oral toxicity of vanidothion and its sulphoxide. Unpublished report of May and Baker Ltd, submitted by Société des Usines Chimiques, Rhône-Poulenc Rhône-Poulenc. (1966) Méthodes de dosage et évolution des résidues. Report R.P. -D.S.Ph./D.S. An. Nord No. 11: 082 Rhône-Poulenc. (1969) Dosage de résidus dans les végétaux. Résumé des résultats. Report R.P.-D.S.Ph. No. 14, 158. Unpublished. [Results obtained during the period 1961-1968 are summarized] Rhône-Poulene. (1972) Report No. R.P.-D.S.Ph./D.S. An. Nord No. 17, 002. Unpublished Ruzicka, J., Thomson, J. and Wheals, B.B. (1967) The gas chromatographic examination of organophosphorus pesticides and their oxidation products. J. Chromatogr., 30: 92-99 Tomizawa, C. (1973) Personal communication Wheldon, G.H., Odey, R.J. and Street, A.E. (1969) Toxicity of vamidothion to rats during dietary administration over six weeks. Unpublished report of Huntingdon Research Centre submitted by Société des Usines Chimiques, Rhône-Poulenc
See Also: Toxicological Abbreviations Vamidothion (ICSC) Vamidothion (Pesticide residues in food: 1982 evaluations) Vamidothion (Pesticide residues in food: 1985 evaluations Part II Toxicology) Vamidothion (Pesticide residues in food: 1988 evaluations Part II Toxicology)