Parathion metabolic activation

Results of methyl parathion assays involving effects on chromosomes have also been contradictory. For sister chromatid exchange, Waters et al. (1982) reported a positive response in Chinese hamster ovary cells only in the presence of metabolic activation system, while methyl parathion tested positive without a metabolic activation system in Chinese hamster V79 cells (Chen et al. 1981), cultured normal human lymphoid cells (Chen et al. 1981 Gomez-Arroyo et al. 1987 Sobti et al. 1982), and Burkitt s l5miphoma cells (Chen et al. 1981). Chen et al. (1981) found a significant dose-related increase in sister chromatid exchange in both hamster and human cultured cells, but dose-related cell cycle delays were less pronounced in human cell lines than in V79 cells. Negative results were obtained for chromosomal aberrations in human lymphocytes without a metabolic activation system (Kumar et al. 1993). 

The discovery of prontosil was fortuitous and was not based on rationale design. There are a large number of pesticides which fall in the same category as prontosil, i.e., they are active by virtue of their susceptibility to metabolic or chemical modification to active intermediates. The classical example of an insecticide of this type is parathion, a phosphorothionate ester which in animals or plants is oxidatively desulfurated to the potent anticholinesterase paraoxon O). The insecticidal activity of parathion was known for several years before the purified material was shown to be a poor anticholinesterase and that metabolic activation to paraoxon was necessary for intoxication. 

Organophosphate insecticides (e.g., malathion, parathion, diazinon) undergo metabolic activation to... 

Many differences in overall toxicity between males and females of various species are known (Table 9.1). Although it is not always known whether metabolism is the only or even the most important factor, such differences may be due to gender-related differences in metabolism. Hexobarbital is metabolized faster by male rats thus female rats have longer sleeping times. Parathion is activated to the cholinesterase inhibitor paraoxon more rapidly in female than in male rats, and thus is more toxic to females. Presumably many of the gender-related differences, as with the developmental differences, are related to quantitative or qualitative differences in the isozymes of the xenobiotic-metabolizing enzymes that exist in multiple forms, but this aspect has not been investigated extensively. 

Disposition in the Body. Parathion is activated in the liver by metabolism to paraoxon. Parathion and paraoxon are further metabolised to diethylthiophosphoric acid (DETP), diethyl-phosphoric acid (DEP), and 4-nitrophenol which are the major urinary excretion products although DETP and DEP are unstable in stored urine. Urinary 4-nitrophenol concentrations may be indicative of the extent of exposure to parathion. 4-Nitrophenol is rapidly excreted in the urine and is not detectable 48 hours after exposure by inhalation or ingestion, but excretion is more prolonged after exposure of intact skin due to the much slower absorption of parathion by this route. Aminoparathion has been detected in postmortem blood and tissues. 

Figure 8. Metabolic activation of the insecticides parathion and schradan...

Compounds that affect activities of hepatic microsomal enzymes can antagonize the effects of methyl parathion, presumably by decreasing metabolism of methyl parathion to methyl paraoxon or enhancing degradation to relatively nontoxic metabolites. For example, pretreatment with phenobarbital protected rats from methyl parathion s cholinergic effects (Murphy 1980) and reduced inhibition of acetylcholinesterase activity in the rat brain (Tvede et al. 1989). Phenobarbital pretreatment prevented lethality from methyl parathion in mice compared to saline-pretreated controls (Sultatos 1987). Pretreatment of rats with two other pesticides, chlordecone or mirex, also reduced inhibition of brain acetylcholinesterase activity in rats dosed with methyl parathion (2.5 mg/kg intraperitoneally), while pretreatment with the herbicide linuron decreased acetylcholine brain levels below those found with methyl parathion treatment alone (Tvede et al. 1989). 

Permethrin, a pyrethrin pesticide, decreased the inhibition of brain cholinesterase activity by methyl parathion, but methyl parathion decreased the LD50 of permethrin when the two pesticides were simultaneously administered to rats (Ortiz et al. 1995). The potentiation of permethrin lethality may be due to the inhibition by methyl parathion of carboxylesterase, which metabolizes permethrin. 

For example ca. 4 pmole of parathion can be metabolized (to a 4-nitrcphenol hydrolysis prodix t) in one hour by a suspension of 10 cells (Shen and Dcwd unpublished data). Dechlorination of 1-chloro 2 4-dinitrdDenzene, by a cell-free extract (1000 g supernatant) occurred at a rate of 20 nmole/min/mg protein (Shen and DcMd unpublished data). This dechlorination reaction appears to be performed by a glutathione transferase-like enzyme, since the reaction is glutathione dependent. Both a-glucosidase and 3-glucosidase activity have also been detected (Shen and Dcwd uipublished data). 

The binding of sulfur and/or an activated intermediate of the phosphorus-containing portion of the parathion molecule to the endoplasmic reticulum leads to a decrease in the amount of cytochrome P-450 detectable as its carbon monoxide complex and to a decrease in the rate of metabolism of substrates such as benz-phetamine ( 19). Neither paraoxon nor any other isolatable metabolite of parathion decreases the amount of cytochrome P-450 or inhibits the ability of microsomes to metabolize substrates such a benzphetamine (19). 

Inhibition of the cholinesterase enzymes depends on blockade of the active site of the enzyme, specifically the site that binds the ester portion of acetylcholine (Fig. 7.48). The organophosphorus compound is thus a pseudosubstrate. However, in the case of some compounds such as the phosphorothionates (parathion and malathion, for example), metabolism is necessary to produce the inhibitor. 

Dichlorvos is of moderate acute toxicity, with an oral LD50 value in rodents from 50 to 150mgkg. While the LC50 for inhibiting mammalian brain acetylcholinesterase is similar between dichlorvos and paraoxon (i.e., the active metabolite of parathion), the acute LD50 values for these agents are considerably different, due in part to the more rapid metabolism and elimination of dichlorvos. 

The effect of proteins on pollutant toxicity includes both quantitative and qualitative aspects. Experiments show that animals fed proteins of low biological value exhibited a lowered microsomal oxidase activity when dietary proteins were supplemented with tryptophan, the enzyme activity was enhanced. Alteration of xenobiotic metabolism by protein deprivation may lead to enhanced or decreased toxicity, depending on whether metabolites are more or less toxic than the parent compound. For example, rats fed a protein-deficient diet show decreased metabolism but increased mortality with respect to pentobarbital, parathion, malathion, DDT, and toxaphene (Table 6.4). On the other hand, rats treated under the same conditions may show a decreased mortality with respect to heptachlor, CC14, and aflatoxin. It is known that, in the liver, heptachlor is metabolized to epoxide, which is more toxic than heptachlor itself, while CC14 is metabolized to CC13, a highly reactive free radical. As for aflatoxin, the decreased mortality is due to reduced binding of its metabolites to DNA. 

Such a pathway does, however, exist in insects. In the latter species, parathion and malathion act as prodrugs. They are metabolized by oxidative desulfurization to give the active anticholinesterases which irreversibly bind to the insects acetylcholinesterase enzymes and lead to death. In mammals, the same compounds are metabolized in a different way to give inactive compounds which are then excreted (Fig. 11.59). 

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