DEMETON-S-METHYL AND RELATED COMPOUNDS JMPR 1973 (DEMETON-S-METHYL, DEMETON-S-METHYL SULFOXIDE AND DEMETON-S-METHYL SULFONE) Explanation One member of this family of compounds, oxydemeton-methyl (Demeton-S-methyl sulfoxide), was reviewed at several previous meetings (FAO/WHO, 1965b; 1968b; 1969b). On the basis of the studies available at that time, primarily short-term studies, an acceptable daily intake for man was estimated to be 0-0.0025 mg/kg/day (FAO/WHO, 1965b). When further considered at the 1967 meeting new data, primarily a threegeneration reproduction study, was reviewed and the ADI for man again reaffirmed to be 0-0.0025 mg/kg/day (FAO/WHO, 1968b). The 1968 joint meeting re-evaluated this compound and concluded that the available information revealed that the toxicology was not related to a single defined compound nor was there precise knowledge of materials actually used in agricultural practice (FAO/WHO, 1969b). Furthermore, no long-term data on any of the substances belonging to this group were available for evaluation. That meeting, therefore, recommended that the ADI as established at previous meetings should no longer be considered valid. The further work required to allow full assessment to be made included: specifications of the compound or compounds in actual agricultural use; studies to compare the metabolic fate in animals, plants and man; investigation of the cholinesterase inhibition in man and adequate long-term studies in two species. Portions of these requirements have been met and the new work has been summarized combined with that previously published and discussed in the following monograph addendum. EVALUATION FOR ACCEPTABLE DAILY INTAKE Biochemical aspects Absorption, distribution and excretion Studies on the absorption, distribution and excretion of the demeton-methyl family of compounds is limited to a study on the oral and subcutaneous administration of oxydemetonmethyl to mice. Within 15 hours following either oral or subcutaneous dosing at a level of 10 mg/kg, 97% of the administered dose was eliminated from the body within 15 hours. There was no indication of the metabolic fate of the compound in this study (Muhlmann and Tietz, 1956). Information on identity and properties Demeton-S-methyl Chemical O, O-dimethyl-S-/2-(ethyl-thio)-ethyl/ name: phosphorothioate Synonyms: Metasystox (i) Metaisosystox Bayer 18 436 25/154 E 154 Metilmerkaptofos teolovi (common name in USSR) Structural O formula CH3O " \" P-S-CH2-CH2-S-C2H5 / CH3O Empirical C6H15O3PS2 formula: Appearance and Pale yellowish oily liquid with penetrating odour odour: reminiscent of leeks Molecular 230.3 weight: Boiling point: 74°C at 0.05 mm Hg 92°C at 0.20 mm Hg 102°C at 0.4 mm Hg 118°C at 1.0 mm Hg Vapour 1.2 x 10-4 mm Hg at 10°C pressure: 3.6 x 10-4 mm Hg at 20°C 1.05 x 10-3 mm Hg at 30°C 2.9 X 10-3 mm Hg at 40°C Volatility: 1.6 mg/m3 at 10°C 4.5 mg/m3 at 20°C 12.4 mg/m3 at 30°c 34.0 mg/m3 at 40°C Specific 1.21 at 20°C gravity: 4° Solubility: Approx. 3300 mg/litre in water at room temperature; readily soluble in most organic solvents; limited solubility in petroleum ether Minimum purity: 90% Impurities: O,O,S-trimethylthiophosphate max. 1.5% O-methyl-S-2-(ethylmercapto)-ethylthiophosphate max. 3.0% 2-ethylthioethylmercaptan max. 0.8% bis(2-ethylthioethyl)-disulfide max. 0.8% Various ionic components (sulfonium compounds, max. 2.5% anorganic salts altogether Oligomeric alkyl(thio) max 1.0% phosphates altogether Water max. 0.4% Oxydemeton-methyl Chemical name: O,O-dimethyl-S-/2-(ethyl-sulfinyl)-ethyl/phosphorothioate Synonyms: Metasystox R Demeton-S-methylsulfoxide Bayer 21 097 R 2170 Metaisosystoxsulfoxide Metilmerkaptofosoksid (common name in USSR) Structural O O formula CH3O " " \" " P-S-CH2-CH2-S-C2H5 / CH3O Empirical C6H15O4PS2 formula: Appearance and Yellowish liquid, practically odourless odour: Molecular weight: 246.3 Boiling point: 106°C at 0.01 mm Hg Volatility: 0.09 mg/m3 at 20°C 0.3 mg/m3 at 30°C 0.7 mg/m3 at 40°C Specific gravity: 1.289 at 20°C 4° Solubility: Miscible with water in any ratio; soluble in most organic solvents, but practically insoluble in petroleum ether Minimum purity: 90% Impurities: Demeton-S-methyl max. 2.0% Demeton-S-methylsulfone max. 2.0% O,O,S-trimethylthiophosphate max. 1.5% O-methyl-S-2-(ethylsulfinyl)ethylthio-phosphate max. 1.2% bis(2-ethylsulfinylethyl)-disulfide max. 0.5% Various ionic components max. 0.5% (sulfonium compounds, etc.) altogether Sodium- and ammoniumsulfate max. 0.8% altogether Oligomeric alkyl(thio)phosphates max. 0.5% altogether Water max. 1.0% Demeton-S-Methylsulfone Chemical name: O,O-dimethyl-S-/2-(ethyl-sulfonyl)-ethyl/phosphorothioate Synonyms: Metaisosystoxsulfon Bayer 20 315 M 3/158 E 158 Structural O O formula CH3O " " \" " P-S-CH2CH2-S-CH2CH3 / " CH3O O Empirical C6H15O5PS2 formula: Appearance and White to pale yellowish, microcrystalline; odour: practically odourless Molecular 262.29 weight: Boiling point: 120°C at 0.03 mm Hg 144°C at 0.12 mm Hg Vapour 0.5 × 10-3 mm Hg at 20°C pressure: 1.6 × 10-5 mm Hg at 30°C 4.5 × 10-5 mm Hg at 40°C Volatility: 0.072 mg/m3 at 20°C 0.22 mg/m3 at 30°C 0.60 mg/m3 at 40°C Specific 1.416 at 20°C gravity: 4° Solubility: Miscible with water; soluble in most organic solvents Minimum 94% purity: Impurities: Oxydemeton-methyl max. 1.0% Demeton-S-methyl max. 0.6% O,O,S-trimethylthiophosphate max. 1.0% "thiosulphoneacid" C2H5SO2C2H4-SO2SC2H4SO2C2H5 max. 0.4% Oligomeric alkyl(thio)phosphates max. 1.0% altogether Various ionic components and max. 1.0% traces ethylenechloride altogether Water max. 1.0% Metabolism The metabolism of demeton-methyl in mammals has not been investigated but the metabolism of the homologous diethyl esters have been studied (see Disulfoton Working Paper). Results obtained in studies with both compounds on plants seemingly justify analogously extrapolating the results of animals experiments with demeton to demeton-methyl. With respect to demeton and its related compounds, it is known that the thiono compound is very readily converted to the thiol form (Fukuto and Metcalf, 1954). The rearrangement, particularly in polar solvents, takes place at a taster rate for demeton-methyl than for demeton. The required time in days for a 10% rearrangement in vitro are as follows: O // Days required for P=S to P conversion at: \ \ O S 20°C 30°C 40°C Demeton-S-methyl 104 26 8 Demeton 1 460 320 91 (Henglein and Schrader, 1955) All studies undertaken with demeton revealed that the biochemical mechanisms in mice, insects and plants were similar (March et al., 1955). Major differences involved were concerned with rates of metabolism and degradation; and, as expected rates were greater in the mammal than in the insect and greater in the insect than in the plant. The routes of metabolism and the metabolites formed were the same in each case (oxidation of thioether of both isomers to the sulfoxide and the sulfone). Although this mechanism has not been worked out for the demeton-methyl family of compounds it is reasonable to assume that metabolism will be analogous to that observed previously with the demeton group. Effects on enzymes and other biochemical parameters Data are available on the cholinesterase inhibiting properties of thiometon. In addition, based upon analogous work with disulfoton, thiometon is a poor inhibitor of cholinesterase activity and when it is converted to the phosphorothiolate, activity of cholinesterase will be rapidly depressed. In one study, oxidation of demeton-S-methyl to the sulfoxide and sulfone did not significantly increase the inhibitory power. The I50 values for sheep erythrocyte cholinesterase were 6.5 × 10-5, 4.1 × 10-5, and 2.3 × 10-5 M. for the sulfide, sulfoxide and sulfone respectively (Heath and Vandekar, 1957). In contrast, Wirth (1958) observed that demeton-S-methyl was a more significant inhibitor of human blood serum cholinesterase. 150 values reported for demeton-S-methyl, oxydemeton-methyl and demeton-S-sulfone were 1.65 x 10-6, 2.7 x 10-5, 4.3 x 10-5 M. respectively. Values of 4.66 and 5.10 (pI50) were recorded for thiometon with RBC and serum cholinesterase respectively (Kimmerle and Lorke, 1968). In vitro inhibition of cholinesterase was summarized in 1967 (FAO/WHO, 1968). It was suggested that demeton-S-methyl and demeton-S-methyl sulfoxide (oxydemeton methyl) were essentially equal in cholinesterase inhibiting properties with regard to sheep RBC cholinesterase with an I50 value of 6.5 × 10-5 M. and 4.1 × 10-5 M. respectively. Klimmer (1960) reported a substantial difference in rat, brain cholinesterase inhibition between demeton-S-methyl and oxydemeton-methyl with the 150 values being 9.52 × 10-5 M. and 1.43 × 10-3 M. indicating that demeton-S-methyl is a more significant inhibitor of cholinesterase in rat brain and following thioether oxidation to demeton-S-methyl sulfoxide, cholinesterase depression is significantly reduced. Owing to the pseudo unimolecular reaction kinetics between organophosphates and cholinesterases. the determinations of these values are rarely accurate. Furthermore, such data given by different authors are not comparable in most instances, since they depend on the time of incubation. Subacute feeding studies were performed on rats with demeton-S-methyl sulfoxide and demeton-S-methyl sulfone for the purpose of comparing depression of cholinesterase activity. In a preliminary study demeton-S-methyl sulfoxide was fed 50 ppm and the demeton-S-sulfone was fed at 25 ppm for eight days. Both dietary concentrations caused approximately the same degree of cholinesterase activity depression in plasma and erythrocytes after four days of feeding: the amount of inhibition was found to have increased still more after eight days. In the main study, demeton-S-methyl sulfoxide was fed at 50 and 100 ppm and demeton-S-methyl suffers was fed at 25 and 50 ppm for 21 days. In their effect on the cholinesterase activity of plasma, erythrocytes and brain, both compounds behaved similarly at the respected dietary concentrations with respect to both the time cause and the intensity of depression. To obtain the same degree of depression, demeton-S-methyl sulfone was administered at twice the amount required for demeton-S-methyl sulfoxide. The lowest activity was noted in plasma after 11-14 days and in erythrocytes after 14-18 days (Loser, 1972). Liver function tests were performed at one and 24 hours and seven days following an acute oral administration of 25 mg/kg of demeton-S-methyl sulfone to rabbits. The Bromophthalein test and SGPT, and SDH activity were not affected. As would be expected, demeton-S-methyl sulfone is a cholinesterase inhibitor. Tests in rats at a dose of 11.25 mg/kg and above resulted in approximately 50% inhibition measured at three hours which maintained its inhibition level through to three days following initial treatment (Kimmerle, 1966c). Following oral administration of demeton-S-methyl and the sulfoxide and sulfone, typical anticholinesterase symptoms were observed. The durations of signs of poisoning were markedly longer than after i.v. injection. Intravenous administration of these compounds (except for the demeton-O-methyl) produced typical signs of anticholinesterase poisoning in rats at doses close to the LD50. The thionate (demeton-S-methyl), however, produced immediate incoordination followed by accelerated respiration and weakness lasting several hours. Lethal amounts of the thionate produced deep anaesthesia with occasional jerking which lasted about 30 minutes. Respiration then became more rapid until the animal died within one to two hours. At no stage were typical anticholinesterase signs of poisoning observed. A similar but weaker anaesthetic stage was observed in rats injected IV with the thionate (demeton-S-methyl) isomer. Signs of poisoning were of longer duration following oral administration indicating a slower absorption from the gut (Heath and Vandekar, 1957). TOXICOLOGICAL STUDIES Acute toxicity Substance Animal Sex Route LD50 (mg/kg) Reference Demeton-S-methyl Rat M & F Oral 35-85 Den-Dyke, Sanderson and Noakes, 1970; Dubois and Doull, 1955; DuBois and Plzak, 1962; Heath and Vandekar, 1957; Hecht, 1955; Kimmerle, 1966c; Kimmerle 1972; Klimmer, 1964; Klimmer and Pfaff, 1955; Writh, 1958; Klimmer, 1961 Guinea-Pig M Oral 110 DuBois and Doull, 1955; Dubois and Plzak, 1962 Rabbit Oral ca. 20-50 Hecht, 1955 Cat Oral ca 5-10 Hecht, 1955 Dog Oral ca. 50 Hecht, 1955 Rat M & F i.p. 2-10 (techn.) Dubois and Doull, 1955; Dubois and Plzak, 1962; Hecht, 1955; Niessen et al., 1963 27.5 (pure) Niessen et al., 1963 Guinea-pig i.p. 12.5 Dubois and Plzak, 1962 Acute toxicity (cont'd.) Substance Animal Sex Route LD50 (mg/kg) Reference Rat M i.v. 8.4 Niessen et al. 1963; 17.3 (pure) Nissen et al. 1963 Rat F i.v. 64.6 (pure?) Heath and Vandekar, 1957 Mouse i.v. 0.5-1.0 Hecht, 1955 6.8 (pure) Hecht, 1960 8.2 (techn.) Hecht, 1960 Mouse M i.v. 4.1 (techn.) Niessen et al., 1963 13.0 (pure) Niessen et al., 1963 Rat dermal 50-100 Ben-Dyke, Sanderson and Noakes, 1970; Dubois, 1960; Klotzsche, 1964 Cat dermal 10-20 Hecht,1955 Oxydemeton-methyl Rat M & F Oral 30-85 Ben-Dyke, Sanderson and Noakes, 1970; Dubois, 1955; DuBois and PIzak, 1962; Gaines, 1969; Heath and Vandekar, 1957; Hecht, 1955; Kimmerle, 1966c; Klimmer, 1960; and Wirth, 1958 Guinea-pig Oral 120 DuBois, 1955; DuBois and Plsak, 1962 Rabbit Oral 50-75 Hecht, 1955 Cat Oral 20-50 Hecht, 1955 Dog Oral 20-50 Hecht, 1955 Chickens Oral 35.0 DuBois, 1962b Hens Oral ca. 100 ml. Kimmerle, 1961 Rat M & F i.p. 5.82-50 DuBois, 1955; DuBois and Plzak, 1962; Hecht, 1955; Klimmer, 1960 Mouse i.v. 8-12 DuBois and Plzak, 1962 Acute toxicity (cont'd.) Substance Animal Sex Route LD50 (mg/kg) Reference Guinea-pig i.p. 30 DuBois and and Plzak, 1982 Rat i.v. 47.2 Heath and Vandekar, 1957 Mouse i.v. 7.5-10 Hecht, 1955 Rat M & F Dermal 100-250 Ben.Dyke, Sanders and Noakes; 1970; DeBois, 1960; Dubois and Plzak, 1962; Gaines, 1969; Hecht, 1955; Klimmer, 1960; Klotzche, 1964 Cat Dermal >100 ccm. Hecht, 1955 Rat M Inhalation >1.32 mg/l Kimmerle and Lorke, 1968 1 h exposure 0.35 mg/l 4 h exposure Dameton-S-methyl Rat M & F Oral 32.4-30 DuBois and Doull, 1955; sulfone DuBois and Plzak, 1962; Heath and Vandekar, 1957; Hecht, 1955; Kimmerle, 1966c; Wirth, 1958 Mouse Oral 28.6 Kimmerle, 1966c Guinea-pig Oral 258.0 Kimmerle, 1966c Guinea-pig Oral 120.0 DuBois and Doull, 1955; Rabbit Oral 40.0-50.0 Hecht, 1955; Kimmerle, 1966c Hen Oral ca. 150 Kimmerle, 1966c Cat Oral 25.0-50.0 Hecht, 1955; Kimmerle, 1966c Dog Oral >30 Hecht, 1955; Kimmerle, 1966c Rat M & F i.p. 17.5-25 DuBois and Doull, 1955; DuBois and Plzak, 1962; Hecht, 1955; Kimmerle, 1966c Acute toxicity (cont'd.) Substance Animal Sex Route LD50 (mg/kg) Reference Guinea-pig i.p. 85 Kimmerle, 1966c Hen i.p. 37.5-50 Kimmerle, 1966c Rat M i.v. 23.7 Heath and Vandekar, 1957 Rat F i.v. 21.7 Heath and Vandekar, 1957 Mouse i.v. 21.7-25 Hecht, 1955; Kimmerle, 1966c Mouse s.c. 21.8 Kimmerle, 1966c Rat Dermal > 500 Hecht, 1955; Kimmerle, 1966c Cat Dermal > 500 Hecht, 1955 Demeton-O-methyl Rat Oral 676 Heath and Vandekar, 1957 i.v. 216 Heath and Vandekar, 1957 Antidotal studies Atropine and PAM were found to have a protective effect in rats against the acute oral toxicity of oxydemeton-methyl and the sulfone. Although PAM and atropine alone were both therapeutic, combinations of both compounds did not Afford any greater protection to rats (Kimmerle, 1966a, 1966b, 1966c; Lorke and Kimmerle, 1968; Dubois and Plzak, 1962). On the other hand, atropine was not effective, either alone or in combination with PAM when tested against demeton-S-methyl (Kimmerle, 1966a; Lorke and Kimmerle, 1969; Klotzsche, 1964). Atropine and PAM were found to be ineffective in protecting against the acute toxic effects of oxydemetonmethyl in hens (Kimmerle, 1961). Special studies (a) Demeton-S-methyl None available. (b) Demeton-S-methyl Sulfoxide Special studies on dermal toxicity Two groups of five female rats each were administered 25 and 50 mg/kg daily by dermal application for 60 days. No mortality occurred in either group over the period of time although the high dose group exhibited signs of cholinergic stimulation in the first two weeks of treatment. Continued treatment with oxydemeton-methyl to rats showed that after prolonged exposure the animals developed a tolerance to the acute signs of poisoning (DuBois, 1962a). Oxydemeton-methyl was administered dermally to male and female rats five days a week for three weeks at doses approximating one-fifth of the LD50. A formulation of oxydemeton-methyl (Metasystox-R) containing 2 lb active ingredient per gallon of formulation was used. The acute dermal LD50 was approximately 112.5 mg/kg (450 mg formulation/ kg) in both male and female rats. Male and female rats given daily dermal exposures to this formulation exhibited a slight inhibition of body weight gain and a marked inhibition of brain cholinesterase activity. Repeated dermal exposure did not affect body weight of various organs nor haematological values examined at the end of this period (DuBois et al., 1966). Histological examination of certain tissues revealed no changes that could be attributed to the presence of oxydemeton-methyl as a Metasystox-R formulation in the diet (Wren of al., 1968). Special studies on mutagenicity Groups of male mice (12 Charles River mice per group) were administered oxydemeton-methyl by intraperitoneal administration at levels of 0, 5, and 10 mg/kg. These animals were then mated with three untreated virgin females per week for six consecutive weeks. The females were sacrificed approximately one week after mating and the ovaries and uterus examined for early resorption. The authors indicate that pre-implantation losses for all groups were not affected by oxydemeton-methyl administration and that the material did not cause a "dominant-lethal" response. Data indicated that females mated to males treated with 10 mg/kg after six weeks had a high number of early resorption sites. During all other weeks the reproduction indices were normal (Arnold et al., 1971). Special studies on neurotoxicity Adult hens administered oxydemeton-methyl orally at doses up to the LD50 level showed no indications of delayed neurotoxic response (Kimmerle, 1961). Special studies on potentiation Studies on the acute potentiation of oxydemeton-methyl in combination with 15 other organophosphates and one carbamate anticholinesterase agents administered simultaneously at one half of the LD50 dose by intraperitoneal injection resulted in less than additive acute toxicity. No evidence of potentiation of acute toxicity was obtained by administration to rats of the pairs of compounds (DuBois, 1961). Oral administration of demeton-S-methyl to male rats in combination with phenamiphos (SRA-3886, ethyl-4-(methylthio) m-tolyl-isopropyl-phosphoroamidate, Bay 68, 138, NemacurR) resulted in no potentiation of the acute toxicity (Kimmerle, 1972). Thiometon did not potentiate the acute toxicity of formothion (FAO/WHO, 1970). Special studies on reproduction In a three generation reproduction study at oxydemetonmethyl dietary levels of 0, 10, 25 and 50 ppm, groups of 10 males and 20 females of each generation, except the third filial, were maintained through two successive matings. Second litter animals were used for composing the succeeding generation groups. The third filial generation was maintained only to weaning age. At 50 ppm in all generations, the number of pregnancies and the number of young per litter were significantly reduced. Histological examination of the second filial generation animals disclosed only reduced oogenesis in three of the 10 in the 50 ppm females, with no apparent effect at 25 ppm. 10 ppm was without effect on the number of pregnancies, the number of young per litter, the number of surviving young up to 21 days and microscopic appearance of major organs. Erythrocyte cholinesterase activity, expressed in percentage of controls, was reduced to 83% in males and 67% in females in the third filial generation, after 21 days; and in the second generation, after 27 weeks, to 83% in the males and to 61% in the females. Erythrocytic cholinesterase activity was more consistently reduced, in proportion to the test level, at the two higher levels. No gross abnormalities nor effect on food consumption or body weight gain were seen at any test level (reviewed in FAO/WHO, 1968). Special studies on teratogenicity Groups of 15 pregnant rabbits were administered oxydemeton-methyl in doses of 0, 0.1 and 0.2 mg/kg from day 6 through day 18 of gestation. Negative controls were treated with empty capsules and positive controls were treated with 37.5 mg/kg/day of thalidomide. At day 29 all animals were sacrificed and young were removed by caesarean section, weighed and observed in an incubator for 24 hours. All young were further observed by gross examination and by alizarin staining of the bone. No deaths or unusual reactions were noted in any of the females nor was there any effect on weight gain that could be attributed to the administration of oxydemeton-methyl to the animals. Fetal mortality was not affected by oxydemeton-methyl and there were no abnormalities observed among the fetuses from the low dose group. A single incidence of talipes varus was observed which was believed to have occurred spontaneously although it was not noted in the controls of this test. Positive results were obtained with thalidomide indicating the susceptibility of the strain of animals to teratogenic effects. It is believed that administration of oxydemeton-methyl during the susceptible period of gestation does not result in teratogenic abnormalities in rabbits (Ladd et al., 1971). (c) Demeton-S-methyl sulfone Special studies on neurotoxicity Following acute oral and intraperitoneal administration to hens, demeton-S-methyl sulfone at levels up to and including 200 mg/kg did not induce any neurotoxic effect in hens (Kimmerle, 1966c). Demeton-S-methyl sulfone was found to be non-irritating to the rabbit ear following in contact for 24 hours and after a seven-day observation period. A small quantity of demeton-S-methyl sulfone placed in conjunctival sack of rabbits produced a slight reddening of the conjunctival but no change in the cornea. Constriction of the pupil was noted (Kimmerle, 1966c). Inhalation exposure Groups of rats (10 males and 10 females per group) were exposed for four hours daily for a period of 10 weeks (five exposures per week) to concentrations of 0, 0.0068 and 0.017 mg/litre. Signs of cholinergic stimulation were seen within two weeks at all concentrations tested although no deaths occurred over the course of this experiment. There was a significant decrease in body weight gain over the course of the experiment although haematology was normal. Urine examinations were normal as were the gross and microscopic examinations of tissues and organs. Cholinesterase depression was obvious in all groups with 50% depression being noted at the low concentration (Kimmerle. 1966c). Short-term studies (a) Demeton-S-methyl Rat. Groups of male rats (15 rats per group) wore orally administered demeton-S-methyl daily for up to six months at doses of 0, 1, 5 and 10 mg/kg (Klimmer, 1961). Mortality was evident at 5 and 10 mg/kg and was absent at the lowest treatment level. Cholinergic signs of poisoning evident at the beginning of the study became less evident as the study progressed. No effects were noted at 1 mg/kg/day (equivalent to administration of 10 ppm in the diet). Groups of six male rats were fed demeton-S-methyl in the diet for six months at levels of 0, 50, 100 and 200 ppm (Vandekar, 1958). Cholinergic signs of poisoning were evident at the highest level at the beginning of the study and lessened as time progressed. Depression of cholinesterase activity was evident at all feeding levels. Growth was depressed at 100 ppm. Gross and microscopic examination of tissues showed no change attributed to the demeton-S-methyl in the diet. Weanling male and female rats (Sprague-Dawley strain) Were fed diets containing 0, 2, 5, 10 and 20 ppm demeton-S-methyl for three months. Growth rate, food consumption, physical condition and mortality were not effected at any of the feeding levels. Measurement of serum and erythrocyte cholinesterase were performed at eight weeks and at the end of the feeding period when all animals were sacrificed for gross and microscopic tissue examination. There was no indication of toxic effects at dietary levels of 10 ppm or less (Root and Doull, 1972). (b) Demeton-S-methyl sulfoxide Rat. In groups of 20 rats, administration of oxydemeton methyl by mouth in doses of 5 ag/kg bw daily for three months caused no signs of intoxication or pathological changes, and 10 mg/kg bw for 21 days caused an inhibition of cholinesterase activity after four to six days (reviewed by FAO/WHO, 1968). Groups of six males and six females received oxydemeton-methyl concentrations of 20 ppm or less in the diet for a period of 16 weeks: no significant influence on growth-rate or food consumption was observed. 10 ppm or less caused no significant depression of erythrocyte cholinesterase activity. Gross and microscopic examination of the tissues of rats revealed no indication of toxic effects except for fatty changes in the livers of some of the rats fed 10 ppm and 20 ppm. 50 ppm for six months had no effect on weight gains in a group of six rats and showed no pathological changes attributable to the action of the compound. The brain and blood cholinesterase activity was strongly inhibited. Concentrations of 100 and 200 ppm produced signs of intoxication in the first three weeks of the experiment (Bar, 1963; Vandekar, 1958; reviewed in FAO/WHO, 1968). A group of 20 male rats were orally administered oxydemeton-methyl daily five times per week for 75 days at a level of 5 mg/kg. Behaviour was not affected although growth was depressed. A further study at 5 and 10 mg/kg for 21 days resulted in mortality at 10 mg/kg within one week. Cholinergic signs of poisoning observed in the first week were not evident at the end of the study (Klimmer, 1960). Groups of rats (six male and six female Sprague-Dawley strain rats per group) were fed dietary levels of oxydemetonmethyl in the diet at levels of 0, 2, 5, 10 and 20 ppm for a period of 16 weeks. Behaviour, mortality, growth rate and food consumption data were recorded over this 16 week period. At the conclusion of the experiment gross and microscopic examination of tissues and organs and cholinesterase determination of serum, erythrocyte, brain and submaxillary gland were performed. Gross pathology, including absolute organ weights and organ to body weight ratios was normal at all feeding levels. Histological changes in the livers of rats fed the two highest dietary concentrations consisted of vacuolization of the cytoplasm of the hepatic cells in the periportal region. These changes were apparent in some of the animals fed the control diet but were more pronounced in the animals fed the two highest oxydemeton-methyl-containing diets. The changes were less severe and similar to the controls in the rats fed 2 and 5 ppm. Sections of the liver of animals exhibiting these changes also were found to stain positively for the presence of fat (with oil red, 0). Growth, food consumption, behaviour and body weight changes were not noted during the course of the study. Depression of cholinesterase activity in BBC and brain were observed in both males and females at 20 ppm in the diet. Serum and submaxillary gland cholinesterase appeared to be unaffected in the study, although male submaxillary gland cholinesterase activity was slightly depressed at the highest feeding level. A no-effect level in this study appears to be 5 ppm in the diet based upon somatic effects noted on microscopic examination of liver after 16 weeks. A level of 10 ppm in the diet had no effect on cholinesterase activity (Doull et al., 1962). Groups of rats (12 male and 12 female rats per group) were fed diets containing oxydemeton-methyl for a period of 16 weeks at levels of 0, 2, 5 and 10 ppm. Cholinesterase activity was also determined at the end of the experiment in plasma, RBC, brain and submaxillary gland (Root et al., 1967a). Gross and microscopic pathology was reported on the following tissues: brain, liver, kidney, lymph node, spleen, heart, lung, gonad, thymus, adrenal gland, urinary bladder, stomach, duodenum, pancreas, jejunum. There was no effect on food consumption, growth or survival in any of the levels examined. Haematology and clinical chemistry were not affected although male rats receiving 10 ppm showed a slight decrease in blood glucose. Cholinesterase depression measured at the conclusion of the study showed depression of plasma cholinesterase at 10 ppm in both males and females. Erythrocyte, brain and submaxillary gland inhibition cholinesterase inhibition at 5 ppm in both males and females. A dietary level of 2 ppm was observed to be a no-effect level on cholinesterase. Gross and histologic examination of the tissues of male and female rats containing levels up to 10 ppm Metasystox-R for 16 weeks showed no differences from the controls (Root et al,, 1967a; Hibbs and Nelson, 1967). in a separate study, groups of rats (12 males and 12 females per group) were fed 0 and 20 ppm oxydemeton-methyl for 16 weeks (Root and Meskauskas, 1968). Gross and microscopic analysis of the liver showed no effects attributable to oxydemeton-methyl in the diet. Groups of rats (12 male and 12 female) were fed oxydemeton-methyl in the diet for 13 weeks at dietary concentrations of 0, 1, 1.5, 2, 30, 50 and 100 ppm. Growth in animals fed 2 ppm and below was not affected by the presence of oxydemeton-methyl in the diet. Food consumption was reduced at 100 ppm and growth was reduced at 30 ppm and above. There was no apparent mortality resulting from the incorporation of oxydemeton-methyl in the diet. There was no effect on haematology and blood chemistry and gross pathology was affected only at 100 ppm in the diet. At this high level, organ weights were generally reduced with the exception of the brain which was apparently unaffected., At dietary levels of 1.5 ppm and above erythrocyte cholinesterase was depressed slightly while plasma, brain and submaxillary gland cholinesterase was depressed only at levels of 30 ppm and above. There were no histological findings that could be attributed to the presence of oxydemeton-methyl in the diet at levels up to and including 100 ppm. A no-effect level in this study based upon depression of cholinesterase was 1.0 ppm (Root of al., 1968; Wren and Nelson, 1969). Groups of rats (WISTAR strain SPF rats, 15 male and 15 female per treatment group; 30 male and 30 female rats per control group) were fed dietary concentrations of oxydemetonmethyl of 0, 1, 3, 25 and 125 ppm in the diet for 90 days. Signs of cholinergic stimulation appeared within three weeks at the 125 ppm dose level, continued to increase in severity after the onset of the experiment, and gradually diminished. Food consumption was low in the highest test group and this was reflected in the reduced growth curve for both male and female which was significantly depressed at this high feeding level. There was a slight increase in mortality at the high dose level in males although the females survived the entire test. There were no significant effects at levels up to and including 125 ppm in the diet on clinical chemistry, haematology, urinalysis, kidney function tests, blood, sugar or cholesterol. Plasma cholinesterase was significantly depressed at 25 ppm in both males and females. Erythrocyte cholinesterase was depressed in both males and females at 5 ppm in the diet. Gross histological examination indicated a significantly lower organ weight in several tissues (heart, lung, liver, spleen, kidney, adrenals, and gonads in males and heart, thyroid and spleen of females at 125 ppm in the diet). In females, the reduced organ weights when compared with the reduced body weight resulted in a normal organ to body weight ratio. In other tissues such as thymus, lung, liver, and kidneys the size of which were not reduced the reduced body weight caused the calculation to reflect an increased organ to body weight ratio. No histological change was seen in the tissues examined which could be attributed to the presence of oxydemeton-methyl in the diet (Vince and Spicer, 1971). A no-effect level in this study was 1 ppm. Groups of weanling rats (six rats per group) were fed oxydemeton-methyl in the diet at levels of 0, 1, 5 and 25 ppm for seven days. At the end of one week the animals were sacrificed for the measurement of the hydrolysis of tributyrin and diethyl succinate (DES) by liver and serum and for the measurement of cholinesterase in serum, liver, and brain. Dietary levels of oxydemeton-methyl producing 50% inhibition of aliesterase and cholinesterase over this one week feeding period were obtained by analysis of a plot of the logarithm of dietary concentration and inhibition of the respective enzymes. Dietary level producing 50% inhibition of brain, liver, and serum cholinesterase was 15, 28 and 20.5 ppm, respectively. Dietary level to induce 50% inhibition of DES hydrolysis in liver and serum was 6.1 and 24.0 ppm respectively and for tributyrin hydrolysis in liver and serum the values were 4.2 and >25 ppm respectively (Su et al., 1971). Dog. Diets containing 0, 5, 10 and 20 ppm oxydemeton-methyl have been fed to male and female beagle dogs for periods of 12 weeks. None of these dose levels produced significant changes in food consumption or body weight or gave rise to cholinergic signs. Levels of 10 ppm or less did not cause significant inhibition of serum or erythrocyte cholinesterase activity (Root et al., 1963; reviewed by FAO/WHO, 1965 as oxydemeton-methyl). Groups of dogs (one male and one female per group) were fed dietary levels of oxydemeton-methyl in the diet at levels of 0, 5, 10 and 20 ppm for 12 weeks. There was no change in food consumption or body weight over the treatment period. Serum cholinesterase was depressed at 20 ppm within one week to approximately 80% of normal and remained at this level for the remainder of the study. Red blood cell cholinesterase was continuously depressed from the beginning of the study at 20 ppm in the diet and reached approximately a 30% inhibition level after the 12-week period. In this study, the level of 20 ppm reflected a minimal effect in cholinesterase of red blood cell in dogs (Root et al., 1963). Male and female beagle dogs were fed diets containing 0, 2, 5, 10, and 20 ppm demeton-S-methyl sulfoxide for three months. Observations on growth rate, food consumption, physical activity and mortality indicated no effects at any of the feeding levels. Measurement of serum and erythrocyte cholinesterase were made weekly in the dogs and it was found that no toxic effects in the animals at levels of 10 ppm or less was observed. There was no effect on food consumption, growth or survival over the 12-week feeding period. Male and female dogs at 10 ppm showed a slight increase in SGPT activity with no other effect noted on the haematological examination. There appeared to be no significant somatic effects noted on gross or histological examination. Plasma cholinesterase was unaffected at all feeding levels while RBC brain and liver (especially in females) cholinesterase was depressed significantly at 10 ppm in the diet. The only apparent effect of oxydemeton in dogs is a slight RBC cholinesterase depression and a more substantial decrease in esterases activity of female brain and liver (Root et al., 1967; Root, 1969; Root and Doull, 1972). Two groups of four male and four female dogs were fed oxydemeton-methyl in the diet for 12 weeks. One group was maintained as a control and the second group of dogs was fed a dietary level of 50 ppm for three weeks, 75 ppm for three weeks, and 150 ppm for the final six weeks. At a dietary level of 50 ppm for three weeks no gross detectable cholinergic signs of poisoning were evident. The level when raised to 75 ppm resulted in no overt signs of toxicity. However, upon introduction of 150 ppm oxydemeton-methyl to the diet, severe signs of cholinergic stimulation were evident resulting in death of one of the four dogs. At the conclusion of the study, it was observed that at 150 ppm there was a significant and uniform reduction of liver cholinesterase as well as brain cholinesterase in both sexes. Plasma cholinesterase was depressed within the first week of the experiment (at 50 ppm) to about 46% of normal at which level it remained relatively constant for the entire feeding study. Erythrocyte cholinesterase was continuously depressed at 50 ppm for the entire three-week period of feeding after which it stabilized at a level somewhat below 20% and was maintained at this level for the entire duration of the experiment. Haematological values were slightly altered in males by the presence of oxydemeton-methyl with the clotting time being reduced and the SGPT activity being increased, Similar effects were not noted in females on these two parameters. No other clinical observations were observed to be abnormal. Gross examination of various tissues and organs at the conclusion of the study showed a decrease in spleen weight in both males and females; a substantial increase in male thymus; a decrease in female thymus; an increase in the thyroid gland in males and a decrease in females. Microscopic examination of tissues of these animals showed no significant changes, which could be attributed to the presence of oxydemeton-methyl in the diet (Root et al., 1970; Wren, 1970). Groups of dogs (four male and four female per group) were fed oxydemeton-methyl for two years at dietary levels which varied from 0.5 to 150 ppm in the diet. Groups of four male and four female dogs were fed a normal dry diet for this same period of time. The dietary feedings levels were varied in all three groups of treatments with a low level initiated at 0.5 ppm and fed for 29 weeks after which the diet was switched to 1.0 ppm for weeks 30-43, and was increased to 2 ppm during weeks 43-77 after which it was raised to 4 ppm for weeks 7883 and then reduced to 2 ppm for the remainder of the study. The level of 5 ppm in the diet was fed to the intermediate group for the first 28 weeks after which it was raised to 10 ppm and the animals maintained on this diet for the remainder of the two-year study. The third group of animals (the highest dosed group) received 37.5 ppm for the first 28 weeks after which the level was raised to 75 ppm for weeks 29-77; 100 ppm for weeks 78-79; 125 ppm for weeks 80-83; 150 ppm for weeks 84-88; and 100 ppm for weeks 89-104. There was no effect over the two-year period on growth or food consumption. Behaviour of animals at the highest dose level was abnormal at 125 ppm with signs of poisoning being evident during the short period of time which they were fed at this level and higher. There was no apparent signs of cholinergic stimulation at 100 ppm. Haematological values, urinalysis and clinical chemistry were all normal. No abnormalities were noted with respect to organ weight data or organ to body weight or brain weight ratios in all the test groups. There were no effects noted when tissues of the animals were examined histologically. Cholinesterase from various tissue sources was significantly depressed in several of the groups over the period of this study. Brain cholinesterase was significantly depressed in the highest group while depression was not noted in the intermediate groups at levels up to 10 ppm in the diet. Plasma cholinesterase was also inhibited in the highest group and depressed in the intermediate group especially at 52 weeks and thereafter in the males. There was also a slight depression noted in the females at this time period. There was no apparent depression in either males or females at the 39-week interval which might have been indicative of a dietary switch from 5 to 10 ppm which took place in week 28. As week 39 was essentially normal, the slightly depressed values noted in the 10 ppm level may not reflect a true inhibition of plasma cholinesterase. At the lowest level fed there was a slight depression especially in females at the 52, 78 and 104 weeks although again not coinciding with any dietary change. Red blood cholinesterase was depressed in the highest group and was also depressed in the intermediate group especially in males, at all intervals tested. In females, depression was noted only at week 39 and at each interval thereafter. There appear to be a significant drop at both male and female BBC cholinesterase values, at week 39 which would correspond to the change from 5 to 10 ppm in the diet. At the lowest dose level there is a slight depression noted only at 104 weeks in both males and females. This is presumably a reflection of the change in dietary concentration to 4 ppm which took place at week 78. The possibility exists that the effect of this concentration change would be reflected only at week 104. 2 ppm is considered a no-effect level in dog (Hartke et al., 1973). (c) Demeton-S-methyl sulfone Rat. Groups of rats (six male and six female WISTAR strain rats per group) were orally administered demeton-S-methyl sulfone five days per week for 10 weeks at dosage levels of 0, 1.3, 2.5, 5.0, 9.5 and 19 mg/kg. Behaviour and mortality were observed daily and growth and food consumption were examined weekly. Mortality was observed at the two highest dose levels with typical signs of cholinesterase depression and cholinergic stimulation. In females, levels of 2.5 mg/kg and above resulted in a reduction in growth while in males only the 5.0 mg/kg were so reduced. There was no effect on the haematological values and urine examination for protein, sugar, and sediment showed no differences from the controls. Cholinesterase depression was obvious at all feeding levels with the level of 1.3 mg/kg resulting in approximately 50% depression. Over the course of the study, the enzyme depression appeared to be maintained for five weeks after which there was a further drop in activity which subsequently recovered to values approximately 75% of normal. There was no effect on gross and microscopic pathology in this study (Kimmerle, 1966c). Groups of rats (14 males and 14 females per group) were fed demeton-S-methyl sulfone in the diet at concentrations of 0, 2.5, 10 and 40 ppm for four to six months. Growth was recorded bi-weekly and at the conclusion of the study cholinesterase activity in brain, RBC and plasma were determined. No clinical signs of poisoning were observed over the period of this study and food consumption and weight gain were comparable to the controls. There was no apparent effect on gross pathology as observed at the end of the feeding period and cholinesterase depression in all tissues was obvious brain, plasma and erythrocyte at 10 ppm. 2.5 ppm was judged to be a no-effect level in this study (Klimmer, 1965). Groups of rats (15 male and 15 female WISTAR rats per group, 30 male and 30 female rats were the control group) were fed demeton-S-methyl sulfone in the diet at concentrations of 0, 1, 3, 10 and 30 ppm for three months. Behavioural changes were observed in the animals fed 30 ppm in the diet at the beginning of the experiment. These signs of poisoning were reduced-as the experiment progressed. Food consumption in the animals receiving 30 ppm was reduced as was the growth of males. At 10 ppm and below there was no effect on growth and mortality. There was no apparent effect of demeton-S-methyl sulfone on clinical chemistry, haematological values, urinalysis and kidney function tests. Cholinesterase activity in plasma and erythrocyte was measured at 2, 4, 8 and 13 weeks and was observed to be inhibited at both 10 and 30 ppm in both sexes and marginally was depressed at 3 ppm and above in both sexes. 1 ppm showed no effect on cholinesterase activity. Gross examination of tissues and organs showed no indication of adverse effect due to the compound in the diet. The no-effect level in this experiment was 1 ppm in the diet based upon cholinesterase depression (Loser, 1971b). Histological examination of the following tissues showed no somatic effects of the compound (Newman and Urwin, 1972). Long-term studies (a) Demeton-S-methyl None available. (b) Demeton-S-methyl sulfoxide Rat. Groups of Charles River rats (35 males and 35 females per group) were fed oxydemeton-methyl in the diet for 22 months at dose levels which varied in the experimental design from 0 to 100 ppm. The low dose group received 0.5 ppm for six months followed by 1 ppm for three months, 2 ppm for eight months, 4 ppm for one month, and 2 ppm for the two final months. The intermediate group received 5 ppm for six months then 10 ppm for the remainder of the experiment. The high dose group received 25 ppm for one month, 37.5 ppm for the second month, 50 ppm for the next four months, 75 ppm for the next three months, and then 100 ppm for the remainder of the study. Growth and body weight was affected especially in males. Over the entire course of the study growth in females was not significantly affected. Over the course of the first six months, growth was depressed in males at 0.5 and 5 ppm in the diet and in the highest group which varied from 25 to 50 PPM. At six months, weight gain was depressed with the controls gaining 427 g, the 0.5 ppm gaining 364 g, the 5 ppm gaining 350 g and the high group 309 g over this period. Data for females were all similar to the controls. A comparison of the gain in weight over months 10 to 17 where 2 ppm (the lowest group) was added to the diet show the controls to have gained 104 g while the 2 ppm males gained only 8 g. A plot of the average body weight data showed that there were definitive effects on males at the lowest concentration in the diet. At the conclusion of the 22-month study the total weight gain data showed females to be unaffected while males appeared to be significantly affected at the highest level and moderately affected at the other two levels tested. Haematological and urinalysis were normal and mortality over the course of the study was not related to the oxydemeton in the diet. Serum and alkaline phosphatase (SAP) activity in the high dose group, the only group examined, was elevated sporadically principally in females but does not appear to be related to the administration of oxydemeton. No other clinical chemistry parameter was abnormal. Cholinesterase depression was significant at the higher level in both sexes in plasma, RBC, and brain tissues. At the intermediate level, cholinesterase was significantly depressed again in the RBC and brain and depression was observed in the plasma only at the conclusion of the study. Cholinesterase was unaffected at the lower group level in all tissues over the course of the whole study. No differences were noted between the test and the control animals on gross pathological examination. Kidney, liver and spleen weights were decreased in males. Weight of the liver in males was significantly reduced at the two highest feeding levels. The organ to body weight ratios were unaffected although the organ to brain weight ratios in the two highest groups were significantly reduced. In the kidneys of males, the absolute organ weight was depressed at all feeding levels as was the organ to brain weight ratio but not the organ to body weight ratio. A reduced spleen weight of the male animals on the highest and the lowest but not the intermediate level was observed. Organ to body weight ratios were unaffected but organ to brain weight ratios were similarly reduced. Gross effects were not observed with any other tissues. Histopathological examination of all tissues and organs showed no differences from the control. A no-effect level of 2 ppm in the diet based on cholinesterase depression was observed (Reyna et al., 1973), (c) Demeton-S-methyl sulfone None available. Observations in man In studies on volunteer subjects, the no-effect level determined for oxydemeton-methyl after a 60-day period of administration was 0.05 mg/kg bw. An 0.4 mg/kg level caused depression of serum and erythrocyte cholinesterase activity after a short time but no signs of poisoning were seen. A single application of 1 mg/kg is tolerated without affecting cholinesterase activity whereas 2 mg/kg inhibits the enzyme (Doull, 1973). Comments Demeton-S-methyl and related compounds including demeton-S-methyl sulfoxide (oxydemeton-methyl) and demeton-S-methyl sulfone are alkylthioether dimethyl organophosphate esters structurally analogous to demeton, the diethyl ester, and are absorbed, distributed and metabolized in the same way as demeton in various biological systems. The metabolism of these compounds, by analogy with the diethyl esters, would result in oxidation of the thioether to the sulfoxide and the sulfone. It has been suggested that the sulfoxide, the major terminal residue in plants, is responsible for the toxicological effects, Toxicological data indicate that oxydemeton-methyl is not teratogenic to rabbits, not mutagenic to mice and does not interfere with reproduction in rats. None of these compounds induce delayed neurotoxic signs of poisoning in hens nor do they potentiate the acute toxicity of other anticholinesterase organophosphate or carbamate insecticides. The thioether is the most active in vitro anticholinesterase agent with the sulfoxide and the sulfone being less active. Short-term studies with demeton-S-methyl in rat and dog resulted in a no-effect level of 10 ppm in both species based on cholinesterase depression. Similar studies with the sulfone indicate a marginal anticholinesterase effect at 3 ppm with no effect noted at 1 ppm. Short-term studies with demeton-S-methyl sulfoxide and two-year studies in rats and dogs indicate a no-effect level of 2 ppm based on cholinesterase depression in both species. Fatty degeneration was seen in the liver but only in response to exposure at high dose levels. A close of 0.05 mg/kg/day over a 60-day period was tolerated in man with no evidence of cholinesterase depression. An ADI was established on the basis of the long-term studies in animals and observations in man. TOXICOLOGICAL EVALUATION Level causing no toxicological effect Rat: 2 ppm in the diet equivalent to 0.1 mg/kg bw Dog: 2 ppm in the diet equivalent to 0.05 mg/kg bw Man: 0.05 mg/kg per-day Estimate of acceptable daily intake for man 0-0.005 mg/kg* * The total demeton-S-methyl, demeton-S methyl sulfoxide and demeton-S-methyl sulfone should not exceed this figure. RESIDUES IN FOOD AND THEIR EVALUATION The three compounds are systemic insecticides used for the control of aphids, scales, spider mites, sawflies, leafhoppers and thrips. They are used in numerous crops, particularly cotton, vegetables, potatoes, cereals, tobacco, hops and fruit. Demeton-S-methyl and oxydemeton-methyl are marketed as emulsifiable concentrate formulations in many countries of Europe, Asia, America, Africa and Australia. Demeton-S-methyl sulfone is marketed only in combination with azinphos-methyl as a wettable powder formulation, practically only in European countries. Demeton-S-methyl products are registered in 31 countries, oxydemeton-methyl products in 86 countries, and demeton-S-methyl sulfone in 13 countries. The usage on different crops is as follows: Demeton-S- Oxydemeton- Demeton-S- methyl methyl methylsulfone Field Crop 55% 45% - Vegetables 35% 40% 10% including potatoes Fruit Crops 10% 15% 90% including grapes and citrus fruit Pre-harvest treatment Demeton-S-methyl and oxydemeton--methyl are usually applied in concentration 0.025% a.i. and demeton-S-methyl sulfone as 0.015% a.i. Depending on crops, the pesticides are applied one to five times in a season. Recommended rates of application and safety intervals for different crops are as follows. Application rate Pre-harvest Crop (a.i.) interval Demeton-S-methyl Fruit 500 g/ha 21 days Vegetables 150-250 g/ha 14-21 days Field crops generally 150-300 g/ha 21 days Cotton 500 g/ha 14 days Demeton-S-methyl Sugar cane 200-400 g/ha 14 days Maize 400-600 g/ha 14 days Oxydemeton-methyl Fruit 300-500 g/ha 21 days Vegetables 150-600 g/ha 14-21 days Field crops 150-600 g/ha 14-21 days Demeton-S-methyl sulfone Fruit 300 g/ha 21 days Vegetables 100 g/ha 14-21 days Post-harvest treatments No recommended uses. Other uses All three compounds are recommended for the control of pest on ornamentals. Residues resulting from supervised trials In biological systems, conversion constantly takes place according to the following scheme: demeton-S-methyl --> oxydemeton-methyl --> demeton-S-methyl sulfone Therefore, methods for the analysis of residues must determine the following compounds: after application of demeton-S-methyl: demeton-S-methyl + oxydemeton-methyl + demeton-S-methyl sulfone after application of oxydemeton-methyl: oxydemeton-s-methyl sulfone + demeton-S-methyl sulfone after application of demeton-S-methyl sulfone: demeton-S-methyl sulfone. Residue data are available from supervised trials carried out in different countries on food crops grown under various conditions. In most cases normal dosage rates were applied in accordance with label instructions. However, in some experiments higher dosages were also included. The data of the trials are summarized in Table 1. Those trials carried out before the introduction of GLC wore analysed by the total phosphorus method. TABLE 1. TYPICAL RESIDUE RANGES RESULTING FROM RECOMMENDED APPLICATION RATES AND FREQUENCIES OF APPLICATION OF DEMETON-S-METHYL, OXYDEMETON-METHYL, AND DEMETON-METHYL SULFONE Pre-harvest Residue Country/ Crop interval (ppm) number of trials Apples 14-28 n.d. - 1.3 GFR, USA/18 Pears 14-28 n.d. - 0.1 USA/7 0.2 - 0.6 GFR/1 Peaches 14-28 - 0.2 GFR/1 n.d. - 0.7 USA/3 14-21 0.5 -2.3 S.Afr/1 Plums 14-28 n.d. - 0.75 GFR, USA/4 Strawberries 14-28 n.d. - 0.6 USA/7 Blackcurrants 14-28 0.16 - 0.63 GFR/2 14 4.0 UK/1 Redcurrants 14-28 1.0 - 1.3 USA/2 Raspberries 14-28 0.1 - 0.6 USA/1 Grapes 14-28 0.05 - 2.7 USA/8 0.23 - 0.5 GFR/7 Citrus fruits 14-28 n.d. - 0.5 USA/9 (whole fruit) Brassicas (cabbage, 21 n.d. - 0.45 GFR.S.Afr. brussell sprouts, USA/26 cauliflower, broccoli) Lettuce 14 n.d. - <0.4 GFR, USA/10 14-21 0.05 - 0.5 USA/2 Beans, peas 14 n.d. - 0.3 S.Afr. USA/6 Pumpkins, watermelons, 7 n.d. - 0.2 USA/11 winter-squash n.d. - 0.3 USA/2 14 n.d. USA/11 Cantaloups 7-14 n.d. - 0.3 USA/1 Summer squash 7-25 n.d. - 0.6 USA/6 14-25 n.d. USA/11 Cucumbers 14 n.d. USA/6 Eggplants 1-21 n.d. - 0.2 USA/6 14 0.6 USA/1 Hops 21-35 n.d. - 0.8 GFR/5 Walnuts 21-47 n.d. USA/10 (meat) Cotton-seed n.d. USA/2 Potatoes 3-108 n.d. GFR, Netherlands USA/39 22-49 0.04 - 0.17 GFR/4 Sugar beet 7-63 n.d. GFR, USA/22 Pre-harvest Residue Country/ Crop interval (ppm) number of trials Turnips 7-14 n.d. USA/7 0.1 USA/1 21-28 n.d. USA/13 Cereals -including: 28 n.d. - 0.26 GFR, USA/22 Corn 31/32 0.02 - 0.08 GFR/6 Sorghum, 35-40 n.d. GFR, USA/18 Forage 14-28 n.d. - 3.2 GFR, USA/25 Sugar beet tops, turnip tops, sorghum forage, corn fodder Clover 21-28 2.4 - 5.0 USA/3 Alfalfa 21 n.d. - 5.5 USA/5 Fate of residues In plants No new data were available to amplify that summarized in 1968. In animals When 3 ppm oxydemeton-methyl in green forage was supplied to dairy cattle, practically no residues (40.01 ppm) were found in brain, heart, liver, kidney, steak and fat after a four-week feeding. When fed 12 ppm in forage for the same period the heart contained up to 0.04 ppm, brain up to 0.03 ppm and steak up to 0.06 ppm. When fed 30 ppm for seven days the following residues were determined: liver - n.d. fat - 0.04 ppm kidney - 0.09 ppm heart - 0.11 ppm brain - 0.18 ppm In four-week feeding studies with cows, when 3 ppm oxydemetonmethyl was applied to the ration the residue levels in milk was lower than 0.01 ppm. Likewise the feeding of 9 ppm in the ration produces less than 0.02 ppm residues in milk (Chemagro report 35556, 35557). No residues could be detected (below 0.001 ppm) in eggs of hens fed rations containing 5 ppm oxydemeton-methyl for four weeks. The muscle and fat of these hens was also free of residues (below 0.01 ppm). Giblets contained 0.01 ppm-0.02 ppm (Chemagro Report 27469, 27470). In soil and water Stability of oxydemeton-methyl in three soil types was studied. When 10 ppm was applied 0.05 ppm was found after 15 days. In another experiment residue levels decreased from 2 ppm to n.d. - 0.1 ppm after four weeks and later no residues were detectable. The effect of oxydemeton-methyl on microbial populations was studied (Houseworth and Tweedy, 1972). The pesticide when added to two types of soil at rates of 50 and 250 ppm no effect on soil microorganism populations could be shown over a 56-day period. Studies on leaching, adsorption and stability in water (Flint et al., 1970) showed that 3% of the applied chemical was recovered in run off water from sandy loam, silt loam and high organic silt loam over a period of five weeks. Leaching studies indicated that the compound leaches 30 cm into silt loam, and high organic silt loam following 580 mm and 1350 mm of rainfall, whereas sandy loam soil showed minimal retention of oxydemeton. The half-life of this compound in pond water outdoors at an average temperature of 29°C and pH 7 was 3.7 days. Fate of residues in storage, processing and cooking In sugar beet processing and corn oil deodorization, residues of oxydemeton-methyl, including demeton-methyl sulfone, decreased very markedly (Katague, 1967; Thornton, 1970b). When apples were processed into juice and pomace, 49% of the initial residues were lost (Chemagro Report 38890). Residues on oranges, resulting from application of oxydemeton-methyl, did not decrease significantly following a commercial washing procedure. However, all the processed orange products were free of residues (Olson, 1966). Exposure to SO2 or sun-drying did not result in losses of residues in peaches and prunes (Chemagro Report 21596, 21600). Washing of tomatoes simulating commercial preparation for market did not remove any significant amount of the residue (Thornton, 1973). Residues present on and in grapes after application of oxydemeton-methyl are not reduced during processing into the must and wine (Bayer AG, Leverkusen, Internal Report 328/67, 329/67, 348/67, 349/67). During frozen storage at about -20°C, oxydemeton-methyl residues remain unchanged for long periods as was shown for alfalfa, apples, cabbage, green oat forage and raspberries (Chemagro Report 11573). Residues in food moving in commerce Out of 30 lettuce samples of German origin, one sample contained more than 1.0 ppm of demeton-S-methyl sulfone. Out of 91 apple samples of German origin, four contained residues of "demeton-methyl", viz. less than 0.1 ppm in three samples, and 0.1-0.5 ppm in one sample (Krause and Kirchhoff, 1969). In a survey of fruits and vegetables for organophosphorus insecticides carried out in 1967 in the United Kingdom, a total of 349 samples were analysed. One out of five blackcurrant samples contained 0.95 ppm, one out of 15 cherry samples contained 2.36 ppm, one out of seven radish samples contained 0.07 ppm of demeton-S-methyl. No demeton-methyl residues were found in any of the other samples (Dickes and Nicholas, 1968). In another study conducted in the United Kingdom, 184 samples of raspberries and strawberries, of which 19 were treated with demeton-S-methyl, were analysed for residues. All the 19 samples of raspberries and strawberries that had been treated with demeton-S-methyl were found to be free of residues (Findlay, 1972). The following results were provided by the New Zealand Ministry of Agriculture: A. RANDOM SAMPLING AT RETAIL LEVEL Demeton-S-methyl Crop residue levels 1968 Apples and pears 1 sample in 11 Less than 0.1 ppm 1971 Leaf vegetables 1 sample in 57 Less than 0.01 ppm 1971 Root vegetables 2 samples in 32 Less than 0.01 ppm 1971 Strawberries 1 sample in 7 Less than 0.01 ppm B. RESIDUES IN CROPS KNOWN TO BE TREATED WITH DEMETON-S-METHYL Crop Residue levels 1970 Apples 1 sample N.D. 1972 Strawberries 1 sample Less than 0.005 ppm Methods of residue analysis Advances have been made in the development of methods for the analysis of demeton-methyl compounds since the evaluation in 1968. The basis of most methods is the oxidation of residues containing demeton-S-methyl and oxydemeton-methyl to the sulfone, which can then be determined by GLC. If permanganate is used as the oxidizing agent there is usually no transformation of P = S to P = O, so it is possible to distinguish between P = S sulfone and P = O sulfone. This permits conclusions to be drawn as to whether the residues present result from the application of demeton-S-methyl products or from the use of thiometon products. The same is true for demeton-S and disulfoton. These sulfone pairs may be clearly separated on a 1 m column packed with 10% DC-200 + 1% QF-1 on 80/100 mesh Gas Chrom Q at 195°C (Wagner, 1973). The following retention times are obtained: demeton-S-methyl sulfone 3.75 min thiometon sulfone 4.75 min demeton-S-sulfone 5.0 min disulfoton sulfone 6.15 min The determination of oxydemeton and demeton-S-methyl sulfone in lettuce and sugar beets is described by Thornton and Olson (1971). A sensitive GLC method for all the three compounds in sorghum foliage and wheat plants is described by Thornton and Anderson (1968) who reports a limit of determination of 0.05 ppm. Determination of oxydemeton and metabolite residues in cotton-seed and walnuts is described by Olson (1971a) Limit of determination of the method for these crops is 0.01 ppm. No interferences were observed by Olson (1971b) and Thornton (1970c), Thornton and Olson (1971) when all organophosphorus pesticides registered in the United States of America were examined. If so, they could be resolved by the standard or alternate procedures. A GLC procedure for residues in poultry and eggs is described by Thornton (1970a). The determination of oxydemeton-methyl and other phosphorus compounds in the soil is described by Olson (1970b). Limit of the method - 0.1 ppm. A multi-residue scheme for organophosphorus pesticides residue analyses in total diet samples was described by Abbot et al. (1970). It included three different extraction and clean-up procedures for seven commodity groups. Thirty-one pesticides and some of their metabolites (among them demeton-S-methyl and demeton-S-methyl) were recoverable by this method with a limit of determination of approximately 0.01 ppm for most compounds. National tolerances and safety intervals Unless otherwise stated, the given tolerance levels and safety intervals apply to both demeton-S-methyl (I) and oxydemeton-methyl (II). Safety Country Crop Tolerance interval in ppm in days Australia Fruit, vegetables, cereals 0.5 General 21 (I) Austria General 35 Belgium Fruit, vegetables excl. 0.4 potatoes General 28 Denmark General except lettuce, 28 (II) spinach and other short season crops Finland General except vegetables 35 (II) France General except vegetables 21 (II) and strawberries Germany, Fruit, vegetables, field 21 Federal crops incl. fodder crops, Republic of application under glass generally Vegetables excl. carrots, 0.4a fruit, sugar beets Cereals, potatoes 0.2a Other food crops 0.05a (cont'd) Safety Country Crop Tolerance interval in ppm in days Hungary General 0.5 30 (I) Italy General 0.4b 20 Korea Fruit, vegetables, 30 (I) potatoes, tobacco, fodder crops Morocco General except vegetables 21 (I) Netherlands General 0.4a Potatoes 0.1a Fruit incl. soft fruit, 28 beans, peas, brassicas, potatoes New Zealand General from Oct.-March 0.4 21 General from April-Sept. 0.4 35 Norway General 28 (I) Poland Fruit, vegetables, legumes 30 (II) (no vegetables), root crops and other field crops Fruit, vegetables, legumes 42 (I) (no vegetables), root crops and other field crops Apples, pears, plums Apply up to 14 days post blossom Sweet cherries, currants, Established gooseberries, garden by time of strawberries, raspberries application Fruit and vegetables 0.4 Portugal General 35 (II) South General 2.0 Africa Beans, crucifers generally 10 Brussels sprouts 14 Fruit, potatoes, tomatoes 21 Cueurbits 21 (II) Brinjals, peppers 14 (I) Kafir corn, onions, wheat, 21 (I) groundnuts, cotton, maize (cont'd) Safety Country Crop Tolerance interval in ppm in days Spain Cereals, sugar beets 30 (II) Cotton 35 (II) Fruit Apply only up to petal fall or post-harvest (II) Sweden General 28 Switzerland Leafy and fruiting 0.4b vegetables, legumes, fruit crops, grapes, hops Fruit, grapes, sugar beets 42 (II) Field beans Before flowering begins (II) USSR Fruits 0.7 (I) Fodder 1.0 United Wheat, barley 14 (I) Kingdom Mangold, fodder beets 10 (I) (for clamping) Fodder crops generally 21 (I) All other crops 21 (I) United Fruits, general 1.0 States Melons, pears 0.3 of America Vegetables, general 1.0 Potatoes 0.1 Sugar beets 0.3 Sugar beets tops 0.5 Turnips 0.3 Winter squash 0.3 Pumpkins 0.3 Cotton seed 0.1 Walnuts 0.3 Alfalfa (green) 5.0 Alfalfa (hay and chaff) 11.0 Clover (green) 5.0 Clover (hay and chaff) 11.0 Corn fodder and forage 3.0 (cont'd) Safety Country Crop Tolerance interval in ppm in days Corn grain, fresh corn 0.5 incl. sweet corn (kernels, plus cob with husk removed) Yugoslavia Fruit, grapes, field 28 (II) crops, hops a Sum of demeton-S-methyl (I), oxydemeton-methyl (II) and demeton-S-methylsulfone (III) calculated as demeton-S-methyl (I). b Total as demeton-S-methyl (I). Appraisal Since the evaluation of the oxydemeton-methyl in 1965, 1967, 1968, further data have become available on the following compounds: I - demeton-S-methyl; II - oxydemeton-methyl; and III - demeton-S-methyl sulfone. which are systemic organophosphorus insecticides and acaricides used individually for pre-harvest treatment of a wide range of crops in many countries. One to five applications are recommended at rates ranging from 0.1-0.6 kg/ha depending on the crop. Compounds II and III are also the oxidative metabolites of demeton-S-methyl. Following treatments with either compounds I or II, the residues in the crops consist of oxidized derivatives of compounds I and/or II. Residue data were available from the United States of America, Germany, United Kingdom, South Africa and Netherlands from supervised trials on fruit, vegetables, field crops and fodder, and on the feeding of animals. Information on the fate of residues in storage and processing of some crops was available as was information on the fate of residues in soil and pond water. Data on residues in foodstuffs moving in commerce were also considered. Available multi-residue gas-chromatographic procedures are suitable for regulatory purposes but it is essential to oxidize all components of the residue to compound III (sulfone) in order to increase the accuracy. RECOMMENDATIONS Tolerances The following recommendations are based on pre-harvest intervals of 14-28 days. Animal foodstuffs (green) 5 ppm " " (dry) 10 ppm Currants (red and black), grapes 2 ppm Apples, peaches, plums 1 ppm Blackberries, citrus fruits, gooseberries, 0.5 ppm lettuce, pears, raspberries, strawberries, summer squash Beans, broccoli, brussels sprouts, 0.2 ppm cabbage, cantaloupes, cauliflower, cereals, cucumbers, eggplants, peas, potatoes, pumpkins, raw cereals, watermelons, winter squash Cotton-seed, sugar beets, turnips 0.1 ppm Eggs, fat and meat of cattle, 0.05* ppm sheep, pigs, poultry, milk and milk products, nuts (kernal) These tolerances are to apply to the sum of the residues of demeton-S-methyl, oxydemeton-methyl, and demeton-S-methyl sulfone, determined as the sulfone and calculated as demeton-S-methyl. FURTHER WORK OR INFORMATION Desirable 1. Studies to elucidate fatty degeneration in liver at high doses. 2. Information on residues in animal tissues from the feeding of demeton-methyl group compounds, in the form of plant residues, to domestic animals other than cows and chickens. * At or about the limit of determination. REFERENCES Abbott, D.C., Crisp, S., Tarrant, K. R. and Tatton, J. O'G. (1970) Organophosphorus pesticide residues in the total diet. Pestic. Sci, 1: 10-13 Anderson, C.A. (1962) Colorimetric determination of DI-SYSTON and SYSTOX residues in plant material. Chemagro Report No. 8544 Arnold, D., Keplinger, M.D. and Fancher, O.E. (1971) "Mutagenic Study with Meta-Systox R 50% Technical in Albino Mice". Unpublished report from Industrial Biotest & Laboratories Inc. Bayer AG (1973) - Leverkusen - Pflanzenschutz AT, Biol. Forschung, Institut for Rückstandsanalytik. Unpublished reports filed with FAO Ben-Dyke, R. Sanderson, D.M. and Noakes, D.N. (1970) "Acute Toxicity Data for Pesticides (1970)". World Review of Pest Control, 9: 119-127 Bowman, M.C., Beroza, M. and Gentry, C.R. (1969) GLC determination of residues of disulfoton, oxydemetomethyl, and their metabolites in tobacco plants. J.A.O.A,C. 52: 157-162 Chemagro Corporation, Kansas City, U.S.A. (1963/73) Unpublished research reports filed with FAO Dickes, G.J. and Nicholas, P.V. (1968) A survey of fruits and vegetables for organochlorine and organophosphorus insecticides. J. Assoc. Publ. Analysts, 6: 60-66 Doull, J., Vesselinovitch, D., Cowan, J., Root, M., Meskauskas, J. and Fitch. (1972) Subacute Oral Toxicity of Metasystox-R to Rats. Unpublished report from Univ. of Chicago Doull, J. (1973) Personal communication submitted by Bayer A. G. DuBois, K.P. and Doull, J. (1955) "The Acute Toxicity of P=O Meta-Systox, P=O Meta-Systox Sulfoxide and P=O Meta-Systox Sulfone to Mamais". Unpublished report from the Univ. of Chicago DuBois, K.P. (1960) "The Dermal Toxicity of Meta-Systox R and Meta-Systox I to Rats. Unpublished from the Univ. of Chicago DuBois, K.P. & Plzak, G.J. (1962) Toxicol. Appl. Pharmacol. 4: 621. (Cited in FAO/WHO, 1965) DuBois, K.P. (1961) "The Acute Toxicity of Meta-Systox R in Combination with Other Anticholinesterase Agents". Unpublished report from the Univ. of Chicago DuBois, K.P. (1962a) "Effect of Repeated Daily Dermal Application of Meta-Systox R to Rats". Unpublished report from the Univ. of Chicago DuBois, K.P. (1962b) "Acute Oral Toxicity of Meta-Systox R to Chickens". Unpublished report from the Univ. of Chicago DuBois, K.P., DiGiacomo, R., Root, M, Meskaukas, J. and Doull, J. (1966) Subacute Dermal Toxicity of a Meta-Systox R Formulation to Rats. Unpublished report from the Univ. of Chicago EPPO Pesticide Residue Analysis. (1964) Recommended Methods. European Plant Protection Organisation, Avenue des Champs-Elysées, Paris FAO/WHO (1965b) Evaluation of the Toxicity of Pesticide Residues in Food. FAO Meeting Report PL/1965/10/1. WHO/Food Add./27.65 FAO/WHO (1967b) 1967 Evaluations of Some Pesticide Residues in Food. FAO/PL: 1967/m/11/1. WHO/Food Add./68.30 FAO/WHO (1969b) 1968 Evaluations of Some Pesticide. Residues in Food. FAO/PL: 1968/./9/1. WHO/Food Add./69.35 FAO/WHO (1970b) 1969 Evaluation of Some Pesticide Residues in Food. FAO/PL: 1969/m/17/1. WHO/Food Add./70.38 Findlay, E. (1972) Pesticide residues in foodstuffs in Great Britain. Pesticide residues in raspberries and strawberries. Pestie. Sci. 3: 169-174 Flint, D.R., Church, D.D. and Shaw, H.R. (1970) Soil studies with META-SYSTOX-R. Chemagro-Report No. 28 140 Fukuto, T.R. and Metcalf, R.L. (1954) Isomerization of ß- ethylmercaptoethyl diethyl thionophosphate (Systox). J. Amer. Chem. Soc. 76: 5103-5106 Fukuto, T.R., Metealf, R.L., March, R.B. and Maxon, M.G. (1955) Chemical behaviour of Systox isomers in biological systems. J. Econ. Entomol. 48: 347-354 Fukuto, T.R., Wolff III, J.P. Metcalf, R.L. and March, R.B. (1956) Identification of the sulfoxide and sulfone plant metabolites of the thiol isomer of Systox. J. Econ. Entomol. 49: 147-151 Fukuto, T.R., Wolff III, J.P., Metealf, R.L. and March, R.B. (1957) Identification of the sulfone plant metabolite of the thiono isomer of Systox. J. Econ. Entomol. 50: 399-401 Hartke, K., Burtner, B.R., Kennedy, G.L. jr, and Keplinger, M.L. "Two-year Chronic Oral Toxicity Study with Meta-Systox R in Beagle Dogs". Unpublished study from Industrial Bio-Test Laboratory, Inc. Hartley, G.S. (1952) The anomaly of Systox. World Crops 4: 397 Heath, D.F. and Vandekar, M. (1957) "Some Spontaneous Reactions of //-Dimethyl S-Ethylthioethyl Phosphorothiolate and Related Compounds in Water and on Storage, and their Effects on the Toxicological Properties of the Compounds." Biochem. Journ. 67: 187-201 Heath, D.F., Lane, D.W.J. and Park, P.O. (1955) The decomposition of some organophosphorus insecticides and related compounds in plants. Royal Soc. London Philos. Transactions 239B: 191-214 Hecht, G. (1955) "Verigeichende Prufung der Praparate 25/154, R 2170 and M 3/158". Unpublished report submitted by Bayer A.G. Hecht, G. (1960) "Toxikologische Untersuchung mit Mota-Systox (i)/ Vortrag, gehalten in Tokyo, Korinkaku, am 20.10. 1960". Unpublished report submitted by Bayer A.G. Henglein, A. and Schrader, G. (1935) Zur Kenntnis der Isomerie-Ersheinungen bei den System-Insektiziden "Systox" and "Meta-Systox". Z. Naturforsch, 10b: 12-19 Hibbs, C.M. and Nelson, D.L. (1967) "Histologic Evaluation of Meta-Systox R Treated Rats". Unpublished report submitted by Bayer A.G. Houseworth, L.D. and Tweedy, B.G. (1972) Effect of META-SYSTOX-R on microbial populations. Chemagro-Report No. 34 991 Houseworth, L.D. and Tweedy, B.G. (1973) Report on parent leaching studies for METASYSTOX-R. Chemagro-Report No. 37 181 Joint Demeton-Methyl Residues Panel. (1962) The determination of demeton-methyl residues in fruits and vegetables. Analyst, 87: 485-492 Katague, D.B. (1967) The effect of processing on META-SYSTOX-R residues in sugar beets. Chemagro-Report No. 20 686 Kimmerle, G. (1961) "Protective action of FAM against R 2170 poisoning and neurotoxic effect of R 2170". Unpublished report submitted by Bayer A.G. Kimmerle, G. (1963) "Meta-Systox (i)". Unpublished report submitted by Bayer A.G. Kimmerle, G. (1966a) "E 154 (88, 5%)/Antidetwirkung". Unpublished report submitted by Bayer A.G. Kimmerle, G. (1966b) "Metasystox R/Antidotwirkung (Ht-Nr. 3653)". Unpublished report submitted by Bayer A.G. Kimmerle, G. (1966c) "Toxicological Studies on Active Ingredient Saver 20 315". Unpublished report submitted by Bayer A.G. Kimmerle, G. (1972) "Acute Toxicity of ERA 3886 in Combination with S 276 and with E 154 in Rats". Unpublished report submitted by Bayer A.G. Kimmerle, G. and Lurks, D. (1968) "Toxicology of insecticidal organophosphates". Fflanzenschutz-Nachrichten Bayer 1/68, 21: 111-142 Klimmer, O.R. (1960) "Opinion on the toxicity of the substance 'R 2170' of Farbenfabriken Bayer A.G." Unpublished report from the Pharm. Institut der Universitat, Bonn Klimmer, O.R. (1961) "Gutachten uber die chronische orale Toxizitat von Metasystox der Farbenfabriken Bayer A.G., Leverkusen". Unpublished report from the Pharm. Institut der Universitat, Bonn Klimmer, O.R. (1964) "Bestimmung der akuten oralen Toxizitat von Metasystox M". Unpublished report from the Institut der Universitat, Boon Klimmer, O.R. (1965) "Insecticide BAYER 20 315/Toxicological Studies". Unpublished report from the Pharm. Institut der Universitat, Bonn Klimmer, O.R. and Pfaff, W. (1955) "Untersuchungen uber die Toxicitat des neuen Kontaktinsekticides 0,0 Dimethyl-thiophosphorsaure-o-(ß-S-athyl)-athylester ('Metasystox')". Arzmeim.-Forsch, 5: 584-587 Klotzsche, C. (1964) "Zur toxikologischen Prufung neuer insecticider Phosphorsaureester". Int. Arch. f. Gewerbepath, u. Gewerbehyg. 21: 92-106 Krause, Ch. and Kirchhoff, J. (1969) Organophosphatruckstande auf Marktproben von Obst und Gemuse sowie auf Getreideerzeugnissen. Nachrichtenbl. Dtsch. Pflanzenschutzdienstes, 21: 81-84 Ladd, R., Jenkins, D.H., Keplinger, M.L. and Fancher, O.E. (1971) "Teratogenic Study with Meta-Systox R 50% Technical in Albino Rabbits". Laws, E.Q. and Webley, D.J. (1959) Determination of demeton methyl residues in plant material. Analyst, 84: 28-32 Loeffler, W.W. (1963) Colorimetric determination of METASYSTOX R residues in plant material. Chemagro-Report No. 11 476 Unpublished report from Industrial Biotest Laboratories Inc. Lorke, D. and Kimmerle, G. (1969) "The Action of Reactivators in Phosphoric-Acid-Ester Poisoning". Naunym Schmiedebergs Arch. Pharmak. exp. Path. 263: 237 Loser, E. (1971a) "R 2170 (Metasystox R Active Ingredient)/Subchronic Toxicological Studies on Rats". Unpublished report submitted by Bayer A.G. Loser, E. (1971b) "E 158 (metaisosystoxulfone)/Subchronic Toxicolological Studies on Rats". Unpublished report submitted by Bayer A.G. Loser, E. (1972) "Metasystox R (R 2170) - Metaisosystoxsulfone, (E 158)/Vergleichende Untersuchungen zur Cholinesterase-Hemung bei Ratten", Unpublished report submitted by Bayer A.G. March, R.E., Metcalf, R.L., Fukuto, T.R. and Maxon, M.G. (1955) Metabolism of Systox in the white mouse and American cockroach. J. Econ. Entomol. 48: 355-363 Metcalf, R.L., Fukuto, T.R., March, R.B. and Stafford, E.M. (1956) The systemic behaviour of Systox thiol isomer sulfoxide and methosulfate in plants. J. Econ. Entomol. 49: 738-741 Metealf, R.L., March, R.B., Fukuto, T.R. and Maxon, M. (1954) The behaviour of Systox-isomers in bean and citrus plants. J. Econ. Entomol. 47: 1045-1055 Metcalf, R.L., March, R.B., Pukuto, T.R. and Maxon, M.G. (1955) The nature and significance of Systox residues in plant material. J. Econ. Entomol. 48: 364-369 van der Merve, J.H. and Taylor, W.B. (1971) Gas chromatographic determination of demeton-S-methyl residues in plant material. Pflanzenschutz-Nachrichten Bayer, 24: 259-264 Mühlmann, R. and Tietz, H. (1956) "Das chemische Verhalten von Methylisosystox in der lebenden Pflanze und das sich daraus ergebende Rusk-standsproblem. Hofchen-Briefe, 9: 116-140 Mühlmann, R. and Schrader, G, (1957) Hydrolyse der insektiziden Phosphorsaureester. Z. Naturforsch, 12b: 196-209 New Zealand Ministry of Agriculture. (1973) Information reported to FAO Newman, A.J. and Urwin, C. (1972) "Pathology Report of E 158 Rat Study". Unpublished report from the Huntingdon Res. Centre, England Niessen, H., Tietz, H., Hecht, G. and Kimmerle, G. (1963) "Uber Vorkonmen von Sulfoniumverbindungen in Metasystox (i) und Metasystox R und ihre physiologische Wirkung". Arch. f. Tox. 20: 44-60 Olson, T.J. (1966) The effect of processing on META-SYSTOX-R residues in oranges and orange products. Chemagro-Report No. 18 586 Olson, T.J. (1969) A confirmatory gas chromatographic procedure for META-SYSTOX-R residue analysis. Chemagro-Report No. 23 999; plus Addendum Chemagro-Report No. 28 504 (1970) Olson, T.J. (1970a) A study of the possible interferences of other pesticides with the analytical method for METASYSTOX-R on crops. Chemagro-Report No. 21 463 Olson, T.J. (1970b) Determination of DASANIT, GUTHION, META-SYSTOX-R3 NEXACUR and TRICHLORFON in soil by thermionic emission gas chromatography. Chemagro-Report No. 27 835 Olson, T.J. (1971a) Determination of META-SYSTOX-R residues in cottonseed and walnuts by thermionic emission gas chromatography. Chemagro-Report No. 21 590 Olson, T.J. (1971b) An interference study for the META-SYSTOX-R residue method for crops. Chemagro-Report No. 30 957 Reyna, N.F,, Kennedy, G.L. jr and Keplinger, N.L. (1973) "22 Month Chronic Oral Toxicity Study with Metasystox-R in Albino Rats". Unpublished report from Industrial Biotest Laboratories, Inc. Root, M., Cowan, J. and Doull, J. (1963) "Determination of the Safe Dietary Level for Metasystox-R in Dogs". Unpublished report from the University of Chicago Root, M., Meskauskas, J., Kinoshita, F., Flynn, M. and Grohs, D. (1967a) "Subacute Oral Toxicity of Metasystox-R to Male and Female Rats". Unpublished report from the University of Chicago Root, M. and Meskauskas, J. (1968) "Addendum to a Report on Subacute Oral Toxicity of Metasystox-R to Male and Female Rats". Unpublished report from the University of Chicago Root, M., Meskauskas, J., Kinoshita, F., Flynn, M. and Grohs, D. (1967b) "Subacute Oral Toxicity of Metasystox-R to Male and Female Dogs". Unpublished report from the University of Chicago Root, M. (1969) "Addendum to Subacute Oral Toxicity of Metasystox-R to Male and Female Dogs". Unpublished report from the University of Chicago Root, M.. Meskauskasy J., Kinoshita, F., Flynn, M. and Kompf, C. (1968) "Subacute Oral Toxicity of Metasystox R to Male and Female Rats". Unpublished report from the University of Chicago Root, M., Meskauskas, J., Kinoshita, F. and Flynn, M. (1970) "Subacute Oral Toxicity of Metasystox-R to Male and Female Dogs". Unpublished report from the University of Chicago Root, M.S. and Doull, J. (1972) "Comparative Subacute Oral Toxicity of Some Organic Phosphates in Rats and Dogs". (5th Annual Meeting - 29 June 1972 - reviewed by abstract only) Su, M.Q., Kinoshita, F.K., Frawley, J.P. and DuBois, K.P. (1971) "Comparative Inhibition of Aliesterase and Cholinesterase in Rats Fed Eighteen Organophosphorus Insecticides". Toxicol. and Appl. Pharm. 20: 241-249 Thomas, W.D.E. (1956) The behaviour of systemic insecticides in plants. A survey of results obtained with 32-P labelled Schradan and demeton-S. J. Sci. Food Agric. 9: 565-573 Thomas, W.D.E., Bennett, S.H. and Lloyd-Jones, C.P. (1955) The absorption, breakdown and systemic behaviour in plants of 32-P-labelled demeton S. Ann. Appl. Biol. 43: 569-593 Thomas, W.D.E. and Glynne Jones, G.D. (1955) The systemic properties of diethyl-S-2-(ethylthioethyl) phosphorothiolate (demeton-S) with reference to the contamination of nectar. Ann. Appl. Biol. 43: 182-191 Thornton, J.S. (1970a) A confirmatory gas chromatographic procedure for META-SYSTOX-R in poultry and eggs. Chemagro-Report No. 27 085 Thornton, J.S. (1970b) Effect of the oil doodorization process on residues of METASYSTOX-R and METASYSTOX-R sulfone in corn oil (Simulated). Chemagro-Report No. 27 638 Thornton, J.S. (1970c) A study of the possible interferences of other pesticides with the analytical method for META-SYSTOX-R on crops. I. Test for the compounds registered on mint. Chemagro-Report No. 29 063 Thornton, J.S. (1973) Effect of washing on residues in tomatoes treated with METASYSTOX-R. Chemagro-Report No. 37 332 Thornton, J.S. and Anderson, C.A. (1968) Determination of residues of Di-Syston and metabolites by thermionic emission flame gas chromatography. J. Agr. Food Chem. 16: 895-898 Thornton, J.S. and Olson, T.J. (1971) Determination of META-SYSTOX-R residues in lettuce and sugar beets by thermionic emission gas chromatography. Chemagro-Report No. 21 000 Thornton, J.S. and Yoksh, R.M. (1970) Determination of META-SYSTOX-R residues in poultry tissues and eggs by thermionic emission flame gas chromatography. Chemagro-Report No. 27 004 Tietz, H. and Frehse, H. (1960) Methods zur Bestimmung von Rückstanden der systemischen Insektizide der Metasystox Gruppe in pflanzlichem Material. Hofeben-Briefe, 13, 212-221 Vandekar, M. (1958) "The Toxic Properties of Demeton-Methyl (Metasystox) and Some Related Compounds". Brit. J. Industr. Med. 15: 158-167 (Cited in FAO/WHO, 1965, 1968) Vince, A.A. and Spicer, J.F. (1971) "Pathology Report on R 2170 (Metasystox-R active substance) Sub-Chronic Toxicological Studies in Rats". Unpublished report from the Huntingdon Res. Centre Wagner, K. (1973) Unpublished. Bayer A.G., Pflanzenschutz AT, Biol. Forschung, Institut fur Ruckstandsanalytik Wirth, W. (1958) "Zur Wirkung System-insecticider Phosphorsaure Ester in Warmbluter-Stoffwechsel". Naunyn SchmiedebergIs Arch. exp. Path. u. Pharmak. 234: 352-363 Wren, D.B. and Nelson, D.L. (1969) "Histologic Evaluation of Metasystox-R Treated Rats". Unpublished report from the Chemagro Corporation, submitted by Bayer A.G. Wren, W.B. (1970) "Microscopic Findings in the Tissues of Male and Female Dogs Administered Metasystox-R Orally (subacute toxicity) 150 ppm". Unpublished report submitted by Bayer A.G. Wren, W.B., Hibbs, C. and Nelson, D.L. (1968) "Subacute Dermal Toxicity of the Metasystox-R Formulation to Rats, Histologic Evaluation of Metasystox-R Treated Rats". Unpublished report from Chemagro Corporation, submitted by Bayer A.G.
See Also: Toxicological Abbreviations Demeton-S-methyl and related compounds (Pesticide residues in food: 1984 evaluations) Demeton-S-Methyl and Related Compounds (Pesticide residues in food: 1989 evaluations Part II Toxicology)