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Biomedical subjects

T R Fukuto

Publications and source records attributed to T R Fukuto.

At least 19 recordsLinked to original sources

Liver damage induced in rats by malathion impurities.

Administration of a single oral dose of the malathion impurity, O,O,S-trimethyl phosphorothioate (OOS-Me) or O,S,S-trimethyl phosphorodithioate (OSS-Me), to the rat resulted in hemostatic disorders, e.g. prolongation of blood clotting, prothrombin and thrombin time. Deficiency of coagulation Factors II, V and VII was also observed. OOS-Me and OSS-Me also caused dose-dependent increases of beta-glucuronidase in the blood with a maximum of 15- and 31-fold observed following treatment with 60 mg/kg OOS-Me and 40 mg/kg OSS-Me, respectively. Analysis of serum beta-glucuronidase by isoelectrofocusing electrophoresis showed that the liver endoplasmic reticulum was the source of this enzyme released into the blood. Co-treatment of OOS-Me with 5% O,O,O-trimethyl phosphorothioate (OOO-Me), a potent antagonist of OOS-Me-induced delayed toxicity, prevented hemostatic disorders but had no effect in reducing beta-glucuronidase levels. However, pretreatment of rats with piperonyl butoxide reduced the amount of beta-glucuronidase released into the blood. Of other O,O,S-trialkyl phosphorothioates examined, the O,O-diethyl S-alkyl phosphorothioates showed the highest activity in increasing beta-glucuronidase levels.

Administration, Oral↗

Mechanism of action of organophosphorus and carbamate insecticides.

Organophosphorus and carbamate insecticides are toxic to insects and mammals by virtue of their ability to inactivate the enzyme acetylcholinesterase. This review addresses the mechanism of inhibition of acetylcholinesterase by organophosphorus and carbamate esters, focusing on structural requirements necessary for anticholinesterase activity. The inhibition of acetylcholinesterase by these compounds is discussed in terms of reactivity and steric effects. The role of metabolic activation or degradation in the overall intoxication process is also discussed.

Animals↗

Detection of kidney damage by malathion impurities using a microdissection technique.

O,O,S-Trimethylphosphorothioate (OOS-Me) and O,S,S-trimethylphosphorodithioate (OSS-Me) are impurities in technical grade malathion and related insecticides which have been shown to cause delayed death in rats following a single oral dose of 40-60 mg/kg. In connection with studies on the mode of action of these compounds, work on the microdissection and examination of nephrons was carried out. Nephrons from impurities-treated rats showed swelling, distortion and distension of glomeruli, as well as narrowing of the first part of the proximal tubule (swan neck). These results were similar to those observed from kidney tissue obtained from cadmium-chloride-treated rats and are indicative of OOS-Me and OSS-Me-induced kidney tubule damage.

Animals↗

Dysproteinuria induced in rats by O,O,S-trimethyl phosphorothioate.

Administration of a single oral dose of 60 mg/kg O,O,S-trimethyl phosphorothioate (OOS-Me), a malathion impurity, resulted in a substantial increase in the amounts of amino acids along with a change in the nature of proteins excreted in the urine of treated rats. In contrast to control rats, a small increase in albumin and a small decrease in alpha 1-globulin were observed. However, alpha2-, beta- and gamma 1-globulin, which were not detected in the urine of control rats, were found in substantial amounts in the urine of OOS-Me-treated rats. These findings, coupled with observed increases in urinary glucose levels and consistent specific gravity readings of 1.01 even though treated rats were experiencing oliguria, provide evidence for OOS-Me-induced kidney tubule damage.

Albuminuria↗

Lung injury and delayed toxicity produced by O,S,S-trimethyl phosphorodithioate, an impurity of malathion.

O,S,S,-Trimethyl phosphorodithioate (OSS-Me), an impurity present in organophosphorus insecticides, produced morphological alteration of rat and mouse terminal nonciliated bronchiolar epithelial (Clara) cells. The effects of OSS-Me on pulmonary and hepatic microsomal enzymes were studied following its po administration to rats. Oral 28-day LD50 of OSS-Me for rats was 67 mg/kg. The animals were treated with OSS-Me at 40, 100, and 160 mg/kg and killed 24 hr later. The relative lung weights were not affected at this time. Pulmonary microsomal benzo[a]pyrene hydroxylase decreased significantly; activities were less than 36% of control at the lowest dose. In contrast, the effect of OSS-Me treatment on hepatic monooxygenase activity was moderate. Benzo[a]pyrene hydroxylase, p-nitroanisole demethylase, or 7-ethoxycoumarin deethylase were not affected by OSS-Me treatment at any dose. Pulmonary and hepatic malathion carboxylesterase activities decreased following OSS-Me treatment. The decrease was more marked in liver. Time course effects of OSS-Me treatment on these parameters were examined by treating rats at 40 mg/kg, and the animals were killed at 6, 12, 24, and 72 hr after treatment. The lung relative wet weight was increased markedly at 72 hr. The benzo[a]pyrene hydroxylase activity of pulmonary microsomes was decreased at 24 and 72 hr after treatment, the maximum decrease being observed at 72 hr. At this time, glutathione of the lungs was depleted markedly. Significant decreases were not observed in hepatic monooxygenase activities. Liver glutathione content was not reduced at 72 hr. Pulmonary and hepatic malathion carboxylesterase activities decreased throughout the time course. OSS-Me selectively inhibited benzo[a]pyrene hydroxylase activity, depleted glutathione, and caused morphological alteration of Clara cells in lungs of rats. Although the toxic mechanism(s) produced by OSS-Me remains unknown, these results support the view that the lung is a target organ of OSS-Me-induced delayed toxicity.

Administration, Oral↗

Sequential and dose-dependent alterations in rat bronchiolar epithelium during O,O,S-trimethyl phosphorothioate induced delayed toxicity.

The sequential and dose-dependent effects of O,O,S-trimethyl phosphorothioate (OOS-Me) on rat lung bronchiolar epithelium were investigated using scanning electron microscopy. At 12 h after oral treatment (20 mg/kg), there was a small increase in debris in the bronchioles and, by 24 h, there was much debris as well as phagocytic cells in the bronchioles. After 3 days, there was a decrease in the number of bronchiolar Clara cells as determined by the loss of their characteristic apical bulges. Concomitantly, there was a significant increase in lactate dehydrogenase activity in bronchopulmonary lavage fluid. By day 7, the Clara cells appeared to be reforming and, by day 14, the morphology of bronchiolar epithelium had returned to normal. Dose-dependent studies revealed a threshold dose level of OOS-Me between 10 and 20 mg/kg which produced the observed effects in Clara cells. Both sequential and dose-dependent effects of OOS-Me on Clara cells were correlated with changes in bronchopulmonary lavage lactate dehydrogenase activity.

Animals↗

Selective inhibition of rat pulmonary monooxygenase by O,O,S-trimethyl phosphorothioate treatment.

The effects of oral administration of O,O,S-trimethyl phosphorothioate (OOS), an impurity present in widely used organophosphorus insecticides, were studied using pulmonary and hepatic microsomal enzymes of rats. The animals were treated with OOS at 10,20 and 40 mg/kg, and were killed on day 3 after treatment. Their relative lung weights increased markedly at 20 and 40 mg/kg, increasing 94% at the highest dose, whereas the weight of liver decreased. At 20 mg/kg OOS, the cytochrome P-450 content of the lung and liver decreased to 83 and 80% of the control levels respectively. Pulmonary microsomal 7-ethoxycoumarin (7-Ec) O-deethylase decreased in a dose-dependent manner; activities were less than 10% of control at the 40 mg/kg dose. The activity of pulmonary coumarin hydroxylase also decreased following OOS treatment, but the decrease was not dose-dependent since no activity was detectable at doses over 10 mg/kg. In contrast, the effect of OOS treatment on hepatic monooxygenase activity was moderate. 7-Ec deethylase activity was not affected by OOS treatment at any dose level, while p-nitroanisole (p-NA) demethylase activity was decreased only at the 40 mg/kg dose of OOS. Pulmonary malathion carboxylesterase activity was not affected by OOS treatment. In contrast, a dose-dependent decrease was observed in the liver carboxylesterase. Time course effects of OOS treatment on these parameters were examined by treating rats at 20 mg/kg. The animals were killed 0.5, 1,3 and 7 days after the treatment. The 7-Ec deethylase activity of pulmonary microsomes was decreased on days 0.5, 1 and 3 after treatment, the maximum decrease being observed on day 1. Significant decreases were not observed in hepatic microsomal activities of 7-Ec deethylase or p-nitroanisole demethylase throughout the experimental period; rather, these activities were higher on day 7. Hepatic microsomal malathion carboxylesterase was lower on days 0.5, 1 and 3 after OOS treatment.

Animals↗

Effect of drug metabolism inducer and inhibitor on O,O,S-trimethyl phosphorothioate-induced delayed toxicity in rats.

Oral administration of O,O,S-trimethyl phosphorothioate (OOS), an impurity present in widely used organophosphorus insecticides, causes delayed toxicity in rats, i.e., death occurring as late as 28 days after the treatment. The signs of toxicity include body weight loss (maximum on day 3), red staining around the nose, mouth and eyes, and an increased level of lactate dehydrogenase (LDH) in bronchopulmonary lavage fluid accompanied by morphological alteration of non-ciliated bronchiolar epithelial Clara cells. Pretreatment with phenobarbital, piperonyl butoxide (2 h), SKF 525-A, or small multiple doses of OOS protected against the OOS-induced elevated level of bronchopulmonary lavage LDH, and the other signs of delayed toxicity including morphological alteration of Clara cells. These studies support the view that OOS-induced delayed toxicity is mediated by the cytochrome P-450 dependent metabolism of OOS, and the lung may be the major target organ of delayed toxicity produced by OOS.

Animals↗

Malathion and phenthoate carboxylesterase activities in pulmonary alveolar macrophages as indicators of lung injury.

Malathion and phenthoate carboxylesterase activities were investigated in pulmonary alveolar macrophages (PAM) in Sprague-Dawley rats. PAM was found to be capable of hydrolyzing phenthoate at a faster rate than malathion. Oral administration to rats with O,O,S-trimethyl phosphorothioate (OOS-Me), a pneumotoxic impurity present in technical grades of malathion and phenthoate, increased the activities of these esterases in PAM without affecting an activity in lung microsomal carboxylesterase. The time course study indicated that this increase was maximal on Day 1 following treatment with OOS-Me at 20 and 40 mg/kg of doses. To assess the usefulness of measuring these esterases in PAM as an indicator of lung damage, paraquat and bromobenzene were administered to rats with treatment regimens which have been shown previously to result in histopathologically demonstrable pneumotoxicity. Malathion and phenthoate carboxylesterase activities in PAM were increased by two- to threefold following treatment with paraquat or bromobenzene. These treatments also increased lung microsomal malathion carboxylesterase activity by threefold. Furthermore, infection of rats with Pseudomonas aeruginosa by intratracheal inoculation increased malathion and phenthoate carboxylesterase activities in PAM by two- to threefold without increasing these activities in lung microsomes. These results indicate that PAM may play a significant role in detoxifying airborne malathion and phenthoate when inhaled. Furthermore, the activities of malathion and phenthoate carboxylesterases may be useful for detecting lung injury produced by pneumotoxic chemicals as well as bacterial infection.

Animals↗

An impurity of malathion alters the morphology of rat lung bronchiolar epithelium.

Oral administration of O,O,S-trimethyl phosphorothioate (OOS), an impurity in technical malathion, caused morphological changes in the bronchiolar epithelium of rat lungs. OOS-treated rat lungs had fewer but larger Clara (non-ciliated) cells than lungs from control rats given either corn oil or purified malathion. Moreover, lactate dehydrogenase (LDH) activity in bronchopulmonary lavage fluid was significantly higher in OOS than in control rats. We interpret these data to mean that OOS, and/or its metabolite(s) causes a lesion in the lung. Because of the widespread agricultural use of technical malathion, future work should address the significance of our findings and the possible toxic effect of OOS on lung tissue.

Animals↗

Toxicological properties of trialkyl phosphorothioate and dialkyl alkyl- and arylphosphonothioate esters.

Impurities such as O,S,S-trimethyl phosphorodithioate (TMPD) and the S-methyl isomer of malathion (isomalathion) strongly potentiated the mammalian toxicity of malathion. In contrast, impurities present in the phosphoramidothioate insecticide acephate had an antagonizing effect on its mammalian toxicity. The potentiation of the toxicity of malathion was attributed to inhibition of mammalian liver and serum carboxylesterase. O,O,S-Trimethyl phosphorothioate (TMP), another impurity present in technical malathion and in other organophosphorus insecticides, proved to be highly toxic. Rats given a single oral dose of TMP at a level as low as 20 mg/kg died over a period of three weeks, with death occurring with non-cholinergic signs of poisoning. TMPD also caused similar delayed death in rats. O,O,O-Trimethyl phosphorothioate (TMP=S), also another impurity in technical malathion and a structural isomer of TMP, was a potent antagonist to the delayed toxicity of TMP. Examination of a number of related trialkyl phosphorothioate and dialkyl alkylphosphonothioate esters revealed several of these compounds to be highly toxic to rats.

Animals↗

Phenobarbital pretreatment protects against morphologic changes in rat bronchiolar epithelium caused by an impurity of malathion.

Oral administration (20 mg/kg) of O,O,S-trimethyl phosphorothioate (OOS) causes delayed toxicity in rats; ie, death occurs as late as 28 days after treatment. OOS-treated rats show morphologic changes in the bronchiolar epithelium of the lung; nonciliated (Clara) cells are fewer but larger 3 days after treatment. We have now found that pretreatment with the P-450-dependent mixed-function oxidase inducer, phenobarbital, protects against the morphologic changes caused by OOS. These results support the view that the lung is a target organ of the delayed toxicity caused by OOS and that OOS detoxification is mediated by P-450-dependent metabolism.

Animals↗

Characterization of bound phenthoate residues in citrus.

The metabolism and fate of phenyl ring-labeled 14C-phenthoate (0,0-dimethyl S-[alpha-(carboethoxy)benzyl] phosphorodithioate) was examined in the Valencia orange fruit with emphasis on the characterization of bound phenthoate residues in the fruit peel. The products recovered from the citrus fruit wash were unchanged phenthoate, phenthoate oxon, demethyl phenthoate, phenthoate acid, ethyl mandelate, and mandelic acid. The same products, with the exception of phenthoate oxon, were found in the acetone extract of the fruit peel. Enzymatic hydrolysis of the bound residue in the peel with beta-glucosidase, followed by acidic and basic hydrolysis gave ethyl mandelate as the major product, followed by mandelic acid, demethyl phenthoate and phenthoate acid. Phenthoate was metabolized and conjugated in citrus fruits into detoxication products.

Citrus↗

Delayed toxicity and delayed neurotoxicity of phosphonothioate and phosphonothioate esters.

The delayed neurotoxicity to hens and delayed toxicity to rats of the isomeric trimethyl phosphonothioates, trimethyl phosphate, and a series of the methyl and ethyl esters of methyl-, ethyl-, and phenylphosphonate and phosphonothioates were examined. All the O,O-dialkyl phosphonothioates, phosphorothioates, and their corresponding oxons were relatively nontoxic to rats, with oral LD50 values greater than the 150-450 mg/kg tested. The O,S-dialkyl phosphorothioate esters were highly acutely toxic. The rat acute LD50 values for O,S-dimethyl methylphosphonothioate and O,S-diethyl ethylphosphonothioate were 3 and 8 mg/kg. O,S-Diethyl ethylphosphonothioate and O,O, S-trimethyl phosphorothioate were the only compounds tested that showed delayed toxicity to rats. The delayed LD50 values for these two compounds were 7 and 15-20 mg/kg, respectively, with rats dying 3-22 d after treatment The delayed toxic effects were associated with continual loss of weight, reaching 18-46% at the time of death. Of this series of compounds, only O,O-diethyl phenylphosphonothioate and its oxon showed delayed neurotoxicity to hens 45 d after treatment. The minimum effective dose for these two compounds was 25 mg/kg.d administered ip for 10 d. These findings suggest that delayed neurotoxicity in hens is not due to the same mechanism as delayed toxicity in rats.

Animals↗

Nature of N-S bond cleavage of 2,3-dihydro-2,2-dimethyl-7-benzofuranyl (di-n-butylaminosulfenyl) (methyl)carbamate.

The cleavage of the N-S bond in 2,3-dihydro-2,2-dimethyl-7-benzofuranyl (di-n-butylaminosulfenyl) (methyl)carbamate was examined in different buffer solutions (hydrolysis), in buffer solution containing sulfhydryl reagents (thiolysis) and on thin-layer chromatographic plates. In buffer solution and on thin-layer plates, N-S bond cleavage readily occurred to give carbofuran as a major product, with minor amounts of bis-carbofuran-N,N'-disulfide and -trisulfide. The hydrolysis reaction in buffer proceeded with first-order kinetics. Significant amounts of an unknown polar compound were obtained in buffer solution and on thin-layer plates. In the presence of excess cysteine and glutathione at pH 7.0, thiolytic N-S bond cleavage occurred with first-order kinetics to give carbofuran as the sole identifiable product. At pH 5.0, three minor products were obtained along with carbofuran.

Buffers↗

Absorption and metabolism of the chiral isomers of fonofos in the corn and cotton plant.

Root absorption of chiral phenyl-35S-fonofos in cotton and corn plants revealed stereoselective differences between the two enantiomers. (S)p-Fonofos was absorbed at a faster initial rate and to a greater extent than the (R)p enantiomer in both plant species. Approximately 40% and 62% of the applied radioactivity was absorbed into the cotton plant 12 hr after application of (R)p- and (S)p-fonofos, respectively. In the corn plant, approximately 25% and 63% of the applied (R)p- and (S)p-fonofos was absorbed in the first 12 hrs. Little qualitative or quantitative difference in plant translocation between fonofos enantiomers was observed. (R)p-fonofos was found to be metabolized to a greater extent than the (S)p enantiomer in both cotton and corn plants.

Absorption↗