Metabolic Fate of O-Ethyl S,S-Diphenyl Phosphorodithiolate (Hinosan®) in Rice Plant

Metabolism and residual fate of O-ethyl S,S-diphenyl phosphorodithiolate (Hinosan®) applied on rice plant was examined by using ³⁵S-labeled or ³²P-labeled compound. Ion exchange chromatography, thin-layer chromatography and gas-liquid chromatography with flame thermionic detector or flame photometric detector were applied for identification of water soluble and toluene soluble metabolites of Hinosan. Degradation of Hinosan at the initial stage of metabolism was mainly the cleavage of P-S linkage, and a large portion of phenyl dihydrogen phosphorothiolate and a minor portion of O-ethyl S-phenyl hydrogen phosphorothiolate were found as water soluble metabolites. Phenylthio radical released on the production of the above mentioned metabolites was recovered as diphenyl disulfide, which was finally converted to sulfuric acid through benzenesulfonic acid. Triphenyl phosphorotrithiolate and O,O-diethyl S-phenyl phosphorothiolate were produced by transesterification between molecules of Hinosan at the initial stage of metabolism. Examination of metabolites in rice grains showed that sulfur and phosphorus atoms in Hinosan were incorporated into neutral or cationic substances probably after several steps of chemical transformation.     

Metabolism of O-Ethyl S,S-Diphenyl Phosphorodithioate (Hinosan®) by Mycelial Cells of Pyricularia oryzae

Metabolism of organophosphorus fungicide Hinosan^® (O-ethyl S, S-diphenyl phosphorodithioate) by mycelia of P. oryzae, rice blast fungus, was studied using ³²P–, ³⁵S– and non-labeled compounds, by ion exchange chromatography, paper chromatography, thin-layer chromatography and gas chromatography, and identifying the metabolites and their derivatives with authentic compounds.

The main metabolic pathway is hydrolysis of one P-S linkage followed by the other P-S linkage or ethyl ester linkage and finally yielding phosphoric acid. A part of the fungicide metabolizes to hydroxylated intermediate metabolite, O-ethyl S-p-hydroxyphenyl S-phenyl phosphorodithioate. No significant difference in rate and mode of metabolism was found in this experiment between susceptible and resistant clones against the fungicide.     

Absorption,Translocation and Metabolism of O,O-Diisopropyl S-Benzyl Phosphorothiolate (Kitazin P®) in Rice Plant

Behavior and metabolism of O,O-diisopropyl S-benzyl phosphorothiolate (Kitazin P©) in rice plant were examined using ³²P, ³⁵S-double labeled compound. Uptake of Kitazin P by the plant was different with the growth stages of the plant, and the rate of uptake was rapid in early growth stage. Kitazin P penetrated into plant tissues was gradually hydrolyzed to produce O,O-diisopropyl hydrogen phosphorothioate which was converted to diisopropyl hydrogen phosphate, isopropyl dihydrogen phosphate and phosphoric acid. As toluene soluble metabolites, eight spots were detected by thin-layer chromatography, but their percentages in toluene soluble fraction were extremely low as compared with that of Kitazin P. Only two metabolites, dibenzyl disulfide and O,O-diisopropyl O-benzyl phosphorothionate were identified by a gas-liquid chromatography with a flame thermionic detector or a flame photometric detector. Diisopropyl hydrogen phosphorothioate was detected as a persistent metabolite even in rice grains.     

Metabolic Transformation and Accumulation of O-Ethyl S,S-Diphenyl Phosphorodithiolate (Hinosan®) in Rice Plants

³²P-labeled organophosphorus fungicide Hinosan was sprayed on rice plants at various growth stages, and metabolic fate of the pesticide in the rice plants was studied. Identification of Hinosan and its metabolites in the n-hexane and water extracts was conducted by TLC and GLC (FPD).

The rate of hydrolysis of Hinosan in rice plants seemed to be slower than that of other organophosphorus pesticides. Hexane-soluble components, which were detected throughout the experimental period, consisted mainly of Hinosan. Among the water-soluble metabolites identified were O-ethyl S-phenyl phosphorothioic acid and S,S-diphenyl phosphoro- dithioic acid, which were detected one to four days after the application, and ethyl phosphate and phosphoric acid which increased with the lapse of time.

Upon examination of the radioactivity of Hinosan and its metabolites in rice grains, a certain level was detected in husk, but very little in hulled rice and polished rice.     

Absorption and Translocation of O-Ethyl S,S-Diphenyl Phosphorodithiolate (Hinosan®) in Rice Plants

Absorption and translocation of (O-ethyl S,S-diphenyl phosphorodithiolate (Hinosan) in rice plants were studied by means of techniques of gas-liquid chromatography, radioautograph and ³²P-radioactivity determination. ³²P-labeled Hinosan was used in the present study. Hinosan on the surface of a leaf and on a glass plate was dissipated in a much slower rate than the other phosphorus pesticides tested. Hinosan was chemically transformed to a small extent after taken up into the plant tissues and largely remained in the local region. Up- and downward translocation of Hinosan occurred slightly in the ride seedlings. Translocation and accumulation of Hinosan were also studied concerning with growth stage of rice plants, such as the seedling, the milk-ripening, and the ripening stage. Accumulation in grains was in most cases found to be less than the limit of determination. Translocation of Hinosan was discussed in relation to physiological conditions of rice plants.     

Degradation of methamidophos by <Emphasis Type="Italic">Hyphomicrobium</Emphasis> species MAP-1 and the biochemical degradation pathway

Methamidophos is one of the most widely used organophosphorus insecticides usually detectable in the environment. A facultative methylotroph, Hyphomicrobium sp. MAP-1, capable of high efficiently degrading methamidophos, was isolated from methamidophos-contaminated soil in China. It was found that the addition of methanol significantly promoted the growth of strain MAP-1 and enhanced its degradation of methamidophos. Further, this strain could utilize methamidophos as its sole carbon, nitrogen and phosphorus source for growth and could completely degrade 3,000 mg l⁻¹ methamidophos in 84 h under optimal conditions (pH 7.0, 30°C). The enzyme responsible for methamidophos degradation was mainly located on the cell inner membrane (90.4%). During methamidophos degradation, three metabolites were detected and identified based on tandem mass spectrometry (MS/MS) and gas chromatography-mass spectrometry (GC–MS) analysis. Using this information, a biochemical degradation pathway of methamidophos by Hyphomicrobium sp. MAP-1 was proposed for the first time. Methamidophos is first cleaved at the P–N bond to form O,S-dimethyl hydrogen thiophosphate and NH₃. Subsequently, O,S-dimethyl hydrogen thiophosphate is hydrolyzed at the P–O bond to release –OCH₃ and form S-methyl dihydrogen thiophosphate. O,S-dimethyl hydrogen thiophosphate can also be hydrolyzed at the P–S bond to release –SCH₃ and form methyl dihydrogen phosphate. Finally, S-methyl dihydrogen thiophosphate and methyl dihydrogen phosphate are likely transformed into phosphoric acid.     

Metabolism of S-Benzyl O-Ethyl Phenylphosphonothioate (Inezin®) by Mycelial Cells of Pyricularia oryzae

Gas-liquid chromatographic study revealed that organophosphorus fungicide Inezin® (S-benzyl O-ethyl phenylphosphonothioate) was metabolized to O-ethyl hydrogen phenylphosphonothioate or ethyl hydrogen phenylphosphonate by mycelial cells of Pyricularia oryzae. Metabolic fate of the removed benzyl or benzylthio group was further studied by labeling benzene ring of benzyl radical of the fungicide with ¹⁴C, and dibenzyl disulfide, benzyl alcohol, toluene-α-sulfonic acid and benzoic acid were found as metabolites by ion exchange chromatography and thin-layer chromatography. Gas-liquid chromatographic study also ascertained that a part of Inezin was hydroxylated at m-position of the benzene ring of benzyl radical, but o- or p-hydroxylation of benzyl radical was not seemed to occur.

No significant difference was found in metabolism of the fungicide between susceptible and resistant clones of the fungi.     

Isolation of the Bromo Analogues of Pyrrolnitrin from Pseudomonas pyrrolnitrica

The metabolism of an organophosphorous fungicide, Kitazin P® (S-benzyl O, O-diisopropyl phosphorothioate) by mycelia of Pyricularia oryzae, the rice blast fungus, was studied by using ³²P- and ³⁵S-doubled-labeled, ³⁵S-labeled and non-labeled compounds.

The mycelia incorporated the fungicide from the medium, metabolized most of it to water-soluble metabolites and released them into the medium. The main metabolite from Kitazin P was identefied as O, O-diisopropyl hydrogen phosphorothioate by ion-exchange chromatographic separation of double-labeled metabolites. S-Benzyl O-isopropyl hydrogen phosphorothioate, diisopropyl hydrogen phosphate and/or isopropyl dihydrogen phosphate were suspected to be minor metabolites. From the toluene-soluble fraction several metabolites were separated by thin-layer chromatography. The most eminent metabolite among them was found to be the m-hydroxy derivative of Kitazin P by thin-layer chromatographic identification of the labeled metabolite and gas-liquid chromatographic identification of the metabolite and its methylated and acetylated products with respective authentic samples. The o- and p-hydroxy derivatives were not found in the metabolites.

No significant difference in the rate and extent of metabolism was found between susceptible and resistant clones against the fungicide, when its concentration was below the growth-inhibitory concentration to the both clones.     

Metabolism of the Fungicide S-n-Butyl S′-p-tert-Butylbenzyl N-3-Pyridyldithiocarbonimidate (S-1358) in Rats

S-1358 was rapidly absorbed, metabolized and readily excreted via urine and feces from orally dosed rats. Excretion of radioactivity was almost complete within 4 days. The radioactivity was distributed mainly in stomach, intestines, liver and kidneys. It seems that S-1358 and its metabolites do not persist in organs and tissues following a single oral dosing.

Major urinary metabolites of the benzyl-labeled S-1358 were p-(1,1-dimethyl-2-hydroxyethyl)benzyl methyl sulfide [B], p-(1,1-dimethyl-2-hydroxyethyl)benzyl methyl sulfone [A], p-(1-methyl-1-carboxylethyl)benzyl methyl sulfide [D], p-(1-methyl-1-carboxylethyl)benzyl methyl sulfone [C] and their glucuronide conjugates. Fecal metabolites were S-n-butyl S′-(1, 1-dimethyl-2-hydroxyethyl)benzyl N-3-pyridyldithiocarbonimidate [MR], A, B, C and D. These metabolites were also found in the bile. The pyridine-labeled S-1358 gave rise to 2-(3′-pyridylimino)-4-carboxylthiazolidine [HM] and 3-aminopyridine [AP] in the urine, and MR and AP in the feces. Intact S-1358 was a major component of the fecal radioactivity.     

Photodecomposition of S-Benzyl O,O-Diisopropyl Phosphorothiolate (Kitazin P®)

Two main steps of photodecomposition were observed at the initial stage on the irradiation of ultraviolet light to Kitazin P® in a thin film. One was the isomerization to a thionate, O-benzyl O, O-diisopropyl phosphorothionate, which was gradually hydrolyzed or oxidized to its oxygen analogue. The other step was the cleavage of P-S bond to produce O, O-diisopropyl phosphonate and α-toluenethiol, the latter of which was degraded to produce α-toluenesulfonic acid via dibenzyl disulfide, and finally sulfuric acid and benzoic acid. O, O-Diisopropyl hydrogen phosphorothioate, O, O-diisopropyl hydrogen phosphate and benzyl alcohol were detected as hydrolyzates. Benzyl alcohol was further oxidized to benzoic acid via benzaldehyde. In addition to these compounds, O, O, S-triisopropyl phosphorothiolate, O, O, O-triisopropyl phosphorothionate, O, O, O-triisopropyl phosphate and benzyl isopropyl sulfide were also detected.     

Some observations on the chemical and stereochemical specificity of the de-alkylation of organophosphorus esters by a hepatic glutathione transferase

Hepatic glutathione (GSH) S-methyl transferase from rabbit, pig and dog demethylates dimethyl phosphate triesters. No stereospecificity towards racemic ethyl methyl 2-chloro-1-(2,4-dichlorophenyl)vinyl phosphate could be demonstrated but the enzyme exhibited some selectivity towards the (+) and (?) forms of O-methyl S-methyl 1-naphthyl phosphorothiolate. Pig liver enzyme, purified 30-fold, demethylated the prochiral substrate dimethyl 1-naphthyl phosphorothionate with 90% stereo-selectivity.     

Conversion of dibenzothiophene by the mushrooms <Emphasis Type="Italic">Agrocybe aegerita</Emphasis> and <Emphasis Type="Italic">Coprinellus radians</Emphasis> and their extracellular peroxygenases

The conversion of the heterocycle dibenzothiophene (DBT) by the agaric basidiomycetes Agrocybe aegerita and Coprinellus radians was studied in vivo and in vitro with whole cells and with purified extracellular peroxygenases, respectively. A. aegerita oxidized DBT (110 μM) by 100% within 16 days into eight different metabolites. Among the latter were mainly S-oxidation products (DBT sulfoxide, DBT sulfone) and in lower amounts, ring-hydroxylation compounds (e.g., 2-hydroxy-DBT). C. radians converted about 60% of DBT into DBT sulfoxide and DBT sulfone as the sole metabolites. In vitro tests with purified peroxygenases were performed to compare the product pattern with the metabolites formed in vivo. Using ascorbic acid as radical scavenger, a total of 19 and seven oxygenation products were detected after DBT conversion by the peroxygenases of A. aegerita (AaP) and C. radians (CrP), respectively. Whereas ring hydroxylation was favored over S-oxidation by AaP (again 2-hydroxy-DBT was identified), CrP formed DBT sulfoxide as major product. This finding suggests that fungal peroxygenases can considerably differ in their catalytic properties. Using H₂ ¹⁸O₂, the origin of oxygen was proved to be the peroxide. Based on these results, we propose that extracellular peroxygenases may be involved in the oxidation of heterocycles by fungi also under natural conditions.     

Laboratory and field tests in 1966-67 on chemical control of wireworms (Agriotes spp.)

Of sixteen compounds applied to soil in laboratory tests, azinphos-ethyl, P2188 (O,O-diethyl S-chloromethyl phosphorothiolothionate), ‘Dursban’ (O,O-diethyl O-3,5,6-trichloro-2-pyridyl phosphorothioate), P1973 (S-(N-methoxycarbonyl-N-methylcarbamoylmethyl) dimethyl phosphorothiolothionate), B77488 (O,O-diethylphosphorothioate O-esterwith phenylglyoxylonitrile oxime) and R42211 (O,O-diethyl O-(2-diethylamino-6-methyl-pyrimidin-4-yl) phosphorothioate) killed wireworms when first tested, but in second tests with the same soils only ‘Dursban’, P2188 and B77488 did so. Treating seeds with ‘Dyfonate’ (O-ethyl S-phenyl ethyl phosphonodithioate) or with ethion/γ-BHC mixtures killed few wireworms. Three field trials compared the organophosphorus insecticides ‘Dursban’, ‘Dyfonate’ and phorate with organochlorine standards. In trials with barley and potatoes the standard was 3 lb a.i./acre (3·36 kg/ha) of aldrin. The organophosphorus compounds increased plant stands of barley almost as much as aldrin, although they killed fewer wireworms; and they protected fewer potato tubers from wireworm damage. The third trial compared the organophosphorus compounds with 0·5 lb a.i./acre (0·56 kg/ha) γ-BHC sprayed on a site drilled with sugar beet seed dressed with dieldrin. The γ-BHC increased plant stands almost as much as did 3 lb a.i./acre of the organophosphorus insecticides, and killed as many wireworms.     

Desulfurization of Benzothiophene by the Gram-Negative Bacterium, Sinorhizobium sp. KT55

Sinorhizobium sp. KT55 was the first Gram-negative isolate to be capable of utilizing benzothiophene as the sole source of sulfur. By GC-MS analysis of metabolites of benzothiophene by this strain, benzothiophene sulfone, benzo[e][1,2]oxathiin S-oxide and o-hydroxystyrene were detected, suggesting that the benzothiophene desulfurization pathway of this strain is benzothiophene → benzothiophene sulfoxide → benzothiophene sulfone → benzo[e][1,2]oxathiin S-oxide →o-hydroxystyrene. Desulfurization activity of this strain was significantly repressed by methionine, cysteine, sulfate, dimethyl sulfoxide, and Casamino acids. Received: 5 January 2001/Accepted: 6 February 2001     

Highly enantioselective oxidation of phenyl methyl sulfide and its derivatives into optically pure (S)-sulfoxides with Rhodococcus sp. CCZU10-1 in an n-octane–water biphasic system

Enantiopure sulfoxides can be prepared via the asymmetric oxidation of sulfides using sulfide monooxygenases. The n-octane–water biphasic system was chosen for the bio-oxidation of a water-insoluble phenyl methyl sulfide (PMS) by Rhodococcus sp. CCZU10-1. In this n-octane–water system, the optimum reaction conditions were obtained. (S)-phenyl methyl sulfoxide ((S)-PMSO) with >99.9 % enantiomeric excess formed at 55.3 mM in the n-octane–water biphasic system. Using fed-batch method, a total of 118 mM (S)-PMSO accumulated in 1-L reaction mixture after the 7th feed, and no (R)-PMSO and sulfone were detected. Moreover, Rhodococcus sp. CCZU10-1 displayed fairly good activity and enantioselectivity toward other sulfides. In conclusion, Rhodococcus sp. CCZU10-1 is a promising biocatalyst for synthesizing highly optically active sulfoxides.     

Asymmetric Hydrolysis of Prochiral Diesters with Pig Liver Esterase. Preparation of Optically Active Intermediates for the Synthesis of (+)-Biotin and (+)-α-Methyl-3,4-dihydroxyphenylalanine

With pig liver esterase, 1,3-dibenzyl-4,5-cis-bis(alkyloxycarbonyl)-2-oxoimidazolidine (1) was asymmetrically hydrolyzed to (4S,5R)-1,3-dibenzyl-5-alkyloxycarbonyl-2-oxoimidazolidine-4-carboxylic acid (2). This acid 2 was reduced with lithium borohydride to (4S,5R)-1,3-dibenzyl-5-hydroxymethyl-2-oxoimidazolidine-4-carboxylic acid lactone (3), which is known to be converted to (+)-biotin (4). With the same esterase, diethyl 3,4-dimethoxyphenylmethyl-(methyl)malonate (5) was asymmetrically hydrolyzed to (R)-ethyl hydrogen 3,4-dimethoxy-phenylmethyl(methyl)malonate (6), which can be converted to (S)-α-methyl-3,4-dihydroxyphenyl-alanine(l-α-methyldopa) (9).     

Identification of methylated flavonoid regioisomeric metabolites using enzymatic semisynthesis and liquid chromatography-tandem mass spectrometry

Discrimination of isomeric methylated metabolites is an important step toward identifying genes responsible for methylation, but presents substantial challenges because authentic standards are often unavailable and mass spectra of isomers have been considered indistinguishable. In this report, an approach is described for identifying methyl group positions in multiply methylated flavonoid metabolites using combinations of tandem mass spectrometry, liquid chromatography retention, and site-selective methylation by recombinant O-methyltransferases from Solanum habrochaites LA1777. The basis for observed fragment ions in tandem mass spectra of multiply methylated myricetin was further established using enzymatic incorporation of deuterium-labeled methyl groups using S-adenosylmethionine-d ₃ as precursor.

     

New Synthesis of Optically Active O-Aryl O-Ethyl Phenylphosphonothionates

The mixed anhydride method was applied to synthesize O-aryl O-ethyl phenylphosphonothionate. The reaction of O, O-diethyl phosphorochloridate with O-ethyl phenylphosphonothioic acid afforded O, O-diethyl phosphoric O-ethyl phenylphosphonothioic anhydride in a good yield. This anhydride was converted to O-aryl O-ethyl phenylphosphonothionates by reacting with the appropriate sodium phenoxide. This esterification occurred without racemization and produced optically pure O-ethyl O-(4-nitrophenyl) phenylphosphonothionate (EPN) and O-(4-cyanophenyl) O-ethyl phenylphosphonothionate (cyanofenphos).     

In Vitro Antioxidative Activity of (−)-Epicatechin Glucuronide Metabolites Present in Human and Rat Plasma

Recently we identified four conjugated glucuronide metabolites of epicatechin, (?)-epicatechin-3′-O-glucuronide (E3′G), 4′-O-methyl-(?)-epicatechin-3′-O-glucuronide (4′ME3′G), (?)-epicatechin-7-O-glucuronide (E7G) and 3′-O-methyl-(?)-epicatechin-7-O-glucuronide (3′ME7G) from plasma and urine. E3′G and 4′ME3′G were isolated from human urine, while E7G and 3′ME7G were isolated from rats that had received oral administration of (?)-epicatechin (Natsume et al. (2003), Free Radic. Biol. Med. 34, 840–849). It has been suggested that these metabolites possess considerable in vivo activity, and therefore we carried out a study to compare the antioxidant activities of the metabolites with that of the parent compound. This was achieved by measuring superoxide scavenging activity, reduction of plasma TBARS production and reduced susceptibility of low-density-lipoprotein (LDL) to oxidation. (?)-Epicatechin was found to have more potent antioxidant activity than the conjugated glucuronide metabolites. Both (?)-epicatechin and E7G had marked antioxidative properties with respect to superoxide radical scavenging activity, plasma oxidation induced by 2,2′-azobis-(2-aminopropane) dihydrochloride (AAPH) and LDL oxidation induced by copper ions or 2,2′-azobis(4-methoxy-2,4-dimethylvaleronitrile) (MeO-AMVN). In contrast, the other metabolites had light antioxidative activities over the range of physiological concentrations found in plasma.     

Identification of quinine metabolites in urine after oral dosing in humans

A gas chromatographic–mass spectrometric method was used to separate quinine and its metabolites present in urine after oral dosing of 300 mg quinine in humans. The technique allowed the separation of quinine and ten metabolites. Four of these metabolites were definitely identified as 3-hydroxyquinine, 2′-quinone, O-desmethylquinine and 10,11-dihydroxydihydroquinine, by comparing their methane chemical ionization mass spectra with those of authentic standards prepared by organic synthesis. Six other metabolites are described for the first time in human urine. From their electron impact and chemical ionization mass spectra, we propose these compounds to be 3-hydroxy-2′-quinone, O-desmethyl-2′-quinone, O-desmethyl-3-hydroxyquinine, O-desmethyl-3-hydroxy-2′-quinone, 10,11-dihydroxydihydro-2′-quinone and 10,11-dihydroxydihydro-O-desmethylquinine. These secondary metabolites probably arose from further biotransformation of the four primary metabolites.