Metabolism organophosphates

In this way one can measure t for moderately slow-exchange reactions.More complex chemical systems require multiple saturation experiments. The technique may also be used qualitatively with spin-1/2 nuclei to reveal the course of such reactions as metal-hydride catalyzed hydrogenation and organophosphate metabolism... 

Organophosphates and carbamates containing a pyrazole ring, useful as insecticides as discussed earlier (Section 4.04.4.1.2), are metabolized mainly through hydrolysis of the ester function (B-80MI40406). 

Murphy SD. 1982. Toxicity of hepatic metabolism of organophosphate insecticides in developing rats. In Hunt VR, Smith MK, Worth D, eds. Banbury report, Vol. II. Environmental factors in hiunan growth and development symposium, November 1-4, 1981. Cold Spring Harbor, NY Cold Spring Harbor Laboratory, 125-136. 

No studies were located that examined the toxicokinetics of mineral oil, organophosphate ester, or polyalphaolefin hydraulic fluids in humans or animals, with the exception of a study examining absorption in rats after exposure to a hydraulic fluid containing 99.9% cyclotriphosphazene (Kinkead and Bashe 1987) and the absorption and metabolism of Reolube HYD46, another organophosphate hydraulic fluid (Ciba-Geigy 1985). This section, therefore, discusses available information on the toxicokinetics of major components of these classes of hydraulic fluids or of materials that maybe expected to display similar toxicokinetic properties based on similar physical and chemical characteristics. It should be emphasized that many hydraulic fluids are complex mixtures of chemicals that may include some chemicals which may not share toxicokinetic properties with the major components. 

Organophosphate Ester Hydraulic Fluids. No studies were located regarding metabolism in humans after exposure to organophosphate ester hydraulic fluids. 

Studies directly examining the metabolism of organophosphate ester hydraulic fluids in animals are limited. One study identified metabolites in ether extracts of bile obtained from rabbits given single,... 

The mechanism of OPIDN is poorly understood, but, since all organophosphate esters that produce OPIDN are either direct cholinesterase inhibitors or are metabolically converted to cholinesterase inhibitors, inhibition of an esterase of some kind has generally been thought to be involved (Baron 1981). Certain... 

However, there are some data on interactions of phosphate esters with other compounds. Cocaine undergoes metabolism by three major routes one of these routes involves hydrolysis by liver and plasma cholinesterases to form ecgonine methyl ester. It has been suggested that cocaine users with serious complications tend to have lower plasma cholinesterase levels. Thus, it is possible that individuals with decreased plasma cholinesterase levels (such as resulting from organophosphate ester exposure) may be highly sensitive to cocaine (Cregler and Mark 1986 Hoffman et al. 1992). However, there are no experimental data to support this hypothesis. 

Use of the muscle relaxant succinylcholine, which is metabolized by plasma cholinesterase, is contraindicated in cases of organophosphate poisoning (Giurini et al. 1986). 

Comparative Toxicokinetics. The toxicokinetics database is wholly inadequate with respect to comparing toxicokinetics across species, largely because of the dearth of baseline data regarding absorption, distribution, metabolism, and excretion in any species after exposure to mineral oil hydraulic fluids, organophosphate ester hydraulic fluids, or polyalphaolefin hydraulic fluids. Also, no studies were located on the toxicokinetic properties of hydraulic fluids in humans. 

Sultatos, L.G. and S.D. Murphy. 1983. Hepatic microsomal detoxification of the organophosphates paraoxon and chlorpyrifos oxon in the mouse. Drug Metabol. Dispos. 11 232-238. 

McLean, S., M. Sameshina, T. Katayama, J. Iwata, C.E. Olney, and K.L. Simpson. 1984. A rapid method to determine microsomal metabolism of organophosphate pesticides. Bull. Japan. Soc. Sci. Fish. 50 1419-1423. 

Al-Badry MS, Knowles CO. 1980. Phthalate-organophosphate interactions Toxicity, penetration, and metabolism studies with house flies. Arch Environ Contam Toxicol 9 147-161. 

Urine catecholamines may also serve as biomarkers of disulfoton exposure. No human data are available to support this, but limited animal data provide some evidence of this. Disulfoton exposure caused a 173% and 313% increase in urinary noradrenaline and adrenaline levels in female rats, respectively, within 72 hours of exposure (Brzezinski 1969). The major metabolite of catecholamine metabolism, HMMA, was also detected in the urine from rats given acute doses of disulfoton (Wysocka-Paruszewska 1971). Because organophosphates other than disulfoton can cause an accumulation of acetylcholine at nerve synapses, these chemical compounds may also cause a release of catecholamines from the adrenals and the nervous system. In addition, increased blood and urine catecholamines can be associated with overstimulation of the adrenal medulla and/or the sympathetic neurons by excitement/stress or sympathomimetic drugs, and other chemical compounds such as reserpine, carbon tetrachloride, carbon disulfide, DDT, and monoamine oxidase inhibitors (MAO) inhibitors (Brzezinski 1969). For these reasons, a change in catecholamine levels is not a specific indicator of disulfoton exposure. 

Cross-tolerance between disulfoton and another organophosphate, chlorpyrifos, was observed in mice (Costa and Murphy 1983b). Because of this cross-tolerance, a benefit is derived as a result of this interaction. In the same study, propoxur-tolerant mice were tolerant to disulfoton but not vice versa. Propoxur (a carbamate) is metabolized by carboxylesterases, and these enzymes are inhibited in disulfoton-tolerant animals disulfoton-tolerant animals are more susceptible to propoxur and/or carbamate insecticides than are nonpretreated animals. In another study, disulfoton-tolerant rats were tolerant to the cholinergic effects of octamethyl pyrophosphoramide (OMPA) but not parathion (McPhillips 1969a, 1969b). The authors were unable to explain why the insecticides OMPA and parathion caused different effects. 

Amidases can be found in all kinds of organisms, including insects and plants [24], The distinct activities of these enzymes in different organisms can be exploited for the development of selective insecticides and herbicides that exhibit minimal toxicity for mammals. Thus, the low toxicity in mammals of the malathion derivative dimethoate (4.44) can be attributed to a specific metabolic route that transforms this compound into the nontoxic acid (4.45) [25-27]. However, there are cases in which toxicity is not species-selective. Indeed, in the preparation of these organophosphates, some contaminants that are inhibitors of mammalian carboxylesterase/am-idase may be present [28]. Sometimes the compound itself, and not simply one of its impurities, is toxic. For example, an insecticide such as phos-phamidon (4.46) cannot be detoxified by deamination since it is an amidase inhibitor [24],... 

Phosphinates are a class of organophosphorus compounds, the metabolism of which has received less attention than that of phosphates (see above) or phosphorothioates and P-halidc compounds (see below). Many phosphinates are rapid but transient inhibitors of acetylcholinesterase and carboxyl-esterases. And like organophosphates and phosphonates, phosphinates are substrates of arylesterases (EC 3.1.1.2). This is exemplified by 4-nitrophen-yl ethyl(phenyl)phosphinate (9.62), whose (-)-enantiomer was hydrolyzed by rabbit serum arylesterase almost 10 times faster than the (+)-enantiomer [133],... 

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