Gene/Protein Disease Symptom Drug Enzyme Compound
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Query: EC:3.1.1.8 (cholinesterase)
 12,691 document(s) hit in 31,850,051 MEDLINE articles (0.00 seconds)

Phenobarbital and some other enzyme-inducers are known to reduce organophosphate toxicity. One suggested mechanism is the induction of liver cytochrome P450 enzymes catalyzing monooxygenation reactions. The aim of the present study was to elucidate the cytochrome P450 subfamily, or P450 isoenzyme(s), participating in the detoxification of diisopropyl fluorophosphate (DFP) in the rat. DFP resulted in a type I spectrum in liver microsomes from phenobarbital- or RP 52028-treated rats (binding constants 0.32 and 0.17 microM, respectively) and in a purified P450 preparation enriched with CYP2B. The spectrum was reversible by metyrapone, an inhibitor of the CYP2B enzyme subfamily. The 7-pentoxyresorufin O-dealkylase activity was inhibited by DFP in liver microsomes from phenobarbital- or RP 52028-treated rats and in a reconstituted system containing the purified CYP2B preparation. In microsomes from phenobarbital-pretreated rats, the inhibition was of a mixed type, i.e., competitive-non-competitive (Km = 0.5 microM; Ki = 6 microM). The microsomal fractions of livers from phenobarbital- or RP 52028-treated rats detoxified DFP effectively in vitro, as measured by a decrease in the DFP inhibition of cholinesterase activity. This detoxification was antagonized by metyrapone and by an antibody raised against purified CYP2B preparation. Clotrimazole, an inhibitor of P450 enzymes, inhibited the detoxification of DFP in rat liver in vivo. A genetically-modified hamster cell line expressing CYP2B1 oxidized NADPH in the presence of DFP. No such oxidation was detected in the parent cell line. These studies suggest that CYP2B1 metabolizes DFP and may significantly contribute to the detoxification of this organophosphate in vivo.
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PMID:P450 enzyme CYP2B catalyzes the detoxification of diisopropyl fluorophosphate. 782 Aug 84

Polymorphisms have been detected in a variety of xenobiotic-metabolizing enzymes at both the phenotypic and genotypic level. In the case of four enzymes, the cytochrome P450 CYP2D6, glutathione S-transferase mu, N-acetyltransferase 2 and serum cholinesterase, the majority of mutations which give rise to a defective phenotype have now been identified. Another group of enzymes show definite polymorphism at the phenotypic level but the exact genetic mechanisms responsible are not yet clear. These enzymes include the cytochromes P450 CYP1A1, CYP1A2 and a CYP2C form which metabolizes mephenytoin, a flavin-linked monooxygenase (fish-odour syndrome), paraoxonase, UDP-glucuronosyltransferase (Gilbert's syndrome) and thiopurine S-methyltransferase. In the case of a further group of enzymes, there is some evidence for polymorphism at either the phenotypic or genotypic level but this has not been unambiguously demonstrated. Examples of this class include the cytochrome P450 enzymes CYP2A6, CYP2E1, CYP2C9 and CYP3A4, xanthine oxidase, an S-oxidase which metabolizes carbocysteine, epoxide hydrolase, two forms of sulphotransferase and several methyltransferases. The nature of all these polymorphisms and possible polymorphisms is discussed in detail, with particular reference to the effects of this variation on drug metabolism and susceptibility to chemically-induced diseases.
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PMID:Metabolic polymorphisms. 836 90

Neuroblastoma cell lines were used to examine the differential interspecies response (i.e., species selectivity) to organophosphates (OPs). Baseline activities of the major target esterases, i.e., cholinesterase, carboxylesterase, and neurotoxic esterase, were assayed in mouse and several human neural candidate cell lines. These activities were found to be variable within individual cell lines and among the various tested cell lines. Cytotoxicity data using the neutral red fluorometric assay were collected on both human (SH-SY5Y) and mouse (NB41A3) neuroblastoma clones exposed to a variety of OP insecticides. IC50 data indicated that the tested mouse cell line was consistently more sensitive than the human cell line to equimolar doses of various OP compounds (e.g., mipafox, parathion, paraoxon, DFP, leptophos oxon, fenthion, and fenitrothion). This difference in cytotoxic sensitivity was most pronounced in response to compounds requiring metabolic bioactivation (i.e., protoxicants). Cytotoxicity data also demonstrated that the NB41A3 mouse neuroblastoma cell line was more metabolically competent than the SH-SY5Y human cell line in converting the protoxicant parathion to its neurotoxic metabolite, paraoxon. B-lymphoblastoids, genetically engineered with human P450 cDNAs, demonstrated higher cytotoxic sensitivity to parathion than unengineered cells, indicating that cytochrome P450-associated monooxidase activity could also influence cytotoxic sensitivity to parathion in culture. These data suggest that interspecies-selectivity in response to OP-related cytotoxicity is influenced by intercellular differences in metabolism and baseline esterase activities.
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PMID:Differential cytotoxic sensitivity in mouse and human cell lines exposed to organophosphate insecticides. 851 93

Susceptibility to organophosphorus (OP) insecticides and nerve agents is strongly influenced by genetic and developmental factors. A number of organophosphorothioate insecticides are detoxified in part via a two-step pathway involving bioactivation of the parent compound by the cytochrome P450 systems, then hydrolysis of the resulting oxygenated metabolite (oxon) by serum and liver paraoxonases (PON1). Serum PON1 has been shown to be polymorphic in human populations. The Arg192 isoform (PON1R192) of this HDL-associated protein hydrolyzes paraoxon (POX) at a high rate, while the Gln192 isoform (PON1Q192) hydrolyzes paraoxon at a low rate. The effect of the polymorphism is reversed for the hydrolysis of diazoxon (DZO), soman and particularly sarin. Phenylacetate is hydrolyzed at approximately the same rate by both PON1 isoforms and chlorpyrifos oxon (CPO) slightly faster by the PON1R192 isoform. In addition to the effect of the amino acid substitution on rates of toxicant hydrolysis, two other factors influence these rates. The expression of PON1 is developmentally regulated. Newborns have very low levels of PON1. Adult levels in rats and mice are reached at 3 weeks of age and in humans, sometime after 6 months of age. In addition, among individuals of a given genotype, there is at least a 13-fold difference in expression of PON1 that is stable over time. Dose/response experiments with normal mice injected with purified PON1 and with PON1 knockout mice have clearly demonstrated that the observed differences of in vitro rates of hydrolysis are significant in determining differential sensitivities to specific insecticides processed through the P450/PON1 pathway. Injection of purified rabbit PON1 protects mice from cholinesterase inhibition by chlorpyrifos (CPS) and CPO. Knockout mice are much more sensitive to CPO and DZO than are their PON1+/+ littermates or wild-type mice. A number of recent reports have also indicated that the PON1R192 isoform may be a risk factor for cardiovascular disease. Studies with PON1 knockout mice are also consistent with a role of PON1 in preventing vascular disease.
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PMID:Genetic and temporal determinants of pesticide sensitivity: role of paraoxonase (PON1). 1079 89

Freshwater clams Corbicula fluminea were exposed in aquariums to four doses of trichloroethylene-TCE-(1.56 up to 100 mg/1) or toluene-TOL-(7.5 up to 60 mg/1) for 5 days. At the end of exposure, components of (de)toxification metabolism of phases I and II, parameters related to oxidative stress and propionylcholinesterase activity were assayed. Determination of TCE and TOL concentrations in water revealed an important evaporative loss during the experiment, characteristic of acute and occasional contaminations by such products occurring in the environment. Appropriate statistical methods such as ANOVA, Tukey test and discriminant analysis underlined the relevance of cytochromes P450 and P418, NADH-cytochrome c reductase, catalase, peroxided and peroxidizable lipids and net peroxidation as biomarkers of exposure to these solvents in C. fluminea. This experiment emphasised the importance of a multi-biomarker approach in environmental surveys and will be completed further by mesocosm studies.
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PMID:Potential biomarkers of trichloroethylene and toluene exposure in Corbicula fluminea. 1116 53

Three phosphotrichlorides [phosphorus trichloride (PCl(3)), phosphorus oxychloride (POCl(3)), and thiophosphoryl chloride (PSCl(3))] with an annual U.S. production of >500,000,000 pounds and their diethyl esters are intermediates in the production of organophosphorus pesticides, plastics, flame retardants, and hydraulic fluids. They are classified as highly toxic to mammals based on acute oral and inhalation data with rats. This study considers their mechanisms of toxicity. PCl(3) and POCl(3) inhibit acetylcholinesterase (AChE) and butyrylcholinesterase (BChE) from several species with in vitro IC(50) values of 5-36 and 88-1200 microM, respectively; PSCl(3) is a less potent inhibitor. These phosphotrichlorides have high vapor toxicity to houseflies with in vivo inhibition of brain AChE activity correlating with mortality. PCl(3) and POCl(3) produce cholinergic poisoning signs on ip administration to mice, and all three phosphotrichlorides give marked in vivo inhibition of serum BChE but not brain AChE activity. PCl(3) is a direct acting AChE inhibitor. Our earlier proposed activation of POCl(3) is confirmed here by preparing pure Cl(2)P(O)OH and its potassium and dicyclohexylamine salts that reproduce the action of POCl(3) as in vitro AChE inhibitors and toxicants in mice. PSCl(3) on hydrolysis yields Cl(2)P(O)SH [which oxidizes with peracid to Cl(2)P(O)SOH] as the proposed activation product. Vapors of (EtO)(2)PCl, (EtO)(2)P(O)Cl, and (EtO)(2)P(S)Cl are lethal to houseflies as in vivo AChE inhibitors, the first two acting directly and the last one on oxidative activation to (EtO)(2)P(O)Cl (possibly by P450) or (EtO)(2)P(O)SCl (a phosphorylating agent in a peracid oxidation system). Thus PCl(3), (EtO)(2)PCl, and (EtO)(2)P(O)Cl act directly as AChE inhibitors whereas POCl(3) and PSCl(3) undergo hydrolytic activation and (EtO)(2)P(S)Cl undergoes oxidative activation. In contrast, the toxicity to mice of phosphofluorides [FP(O)Cl(2), F(Cl)P(O)OH, and F(2)P(O)OH; studied as model compounds for comparison] may be due to liberating fluoride ion.
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PMID:Major intermediates in organophosphate synthesis (PCl3, POCl3, PSCl3, and their diethyl esters) are anticholinesterase agents directly or on activation. 1264 35

The role of the polymorphic cytochrome P450 (CYP) 2D6 isoform in catalysing the oxidative biotransformation of the organophosphate pesticide chlorpyriphos and the carbamate aldicarb into structures that inhibit cholinesterase and induce genotoxicity has been investigated in microsomal fraction, using quinine as a specific chemical inhibitor of CYP 2D6. Pesticides were incubated with rat liver microsomes and production of anticholinergic active metabolites was investigated by the inhibition of human serum cholinesterase. Compared to microsomes incubated without quinine, where cholinesterase activity was inhibited to a mean 53% (chlorpyriphos) and 57% (aldicarb) of control, the introduction of P450 2D6 inhibitor quinine into microsomal incubation mixture reduced cholinesterase activity to 72% of control for chlorpyriphos and to 27% for aldicarb, suggesting that P450 2D6 is involved in the activation of chlorpyriphos but does not influence aldicarb toxicity on acetylcholinesterase. Moreover, the potential genotoxicity of these compounds was evaluated by single cell gel electrophoresis (comet assay) on human leucocytes. DNA fragmentation compared to control was markedly increased after incubation with aldicarb plus quinine, confirming that the parent compound is more toxic than the products of CYP metabolism; conversely, DNA damage after incubation with chlorpyriphos was sensibly reduced by quinine indicating the metabolic activation of this pesticide by CYP 2D6. These data suggest that polymorphism of CYP 2D6 can influence the toxicity of organophosphate but not of carbamate pesticides.
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PMID:[Genotoxicity and activation of organophosphate and carbamate pesticides by cytochrome P450 2D6]. 1497 94

Chlorpyrifos (CPF) is a broad spectrum organophosphorus insecticide bioactivated in vivo to chlorpyrifos-oxon (CPFO), a very potent anticholinesterase. A great majority of available animal studies on CPF and CPFO toxicity are performed in rats. The use of mice in developmental neurobehavioural studies and the availability of transgenic mice warrant a better characterization of CPF-induced toxicity in this species. CD1 mice were exposed to a broad range of acute (12.5-100.0mg/kg) and subacute (1.56-25mg/kg/day from 5 to 30 days) CPF oral doses. Functional and biochemical parameters such as brain and serum cholinesterase (ChE) and liver xenobiotic metabolizing system, including the biotransformation of CPF itself, have been studied and the no observed effect levels (NOELs) identified. Mice seem to be more susceptible than rats at least to acute CPF treatment (oral LD(50) 4.5-fold lower). The species-related differences were not so evident after repeated exposures. In mice a good correlation was observed between brain ChE inhibition and classical cholinergic signs of toxicity. After CPF-repeated treatment, mice seemed to develop some tolerance to CPF-induced effects, which could not be attributed to an alteration of P450-mediated CPF hepatic metabolism. CPF-induced effects on hepatic microsomal carboxylesterase (CE) activity and reduced glutathione (GSH) levels observed at an early stage of treatment and then recovered after 30 days, suggest that the detoxifying mechanisms are actively involved in the protection of CPF-induced effects and possibly in the induction of tolerance in long term exposure. The mouse could be considered a suitable experimental model for future studies on the toxic action of organophosphorus pesticides focused on mechanisms, long term and age-related effects.
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PMID:Cholinesterase inhibition and alterations of hepatic metabolism by oral acute and repeated chlorpyrifos administration to mice. 1738 47

The metabolism of (alphaS)-cyano-3-phenoxybenzyl (1R, 3R)-cis-3-(2,2-dibromovinyl)-2,2-dimethylcyclopropane carboxylate (deltamethrin) and (alphaS)-cyano-3-phenoxybenzyl 2-(4-chlorophenyl)-3-methylbutyrate (esfenvalerate) by rat and human liver microsomes differs with respect to the biotransformation pathway (oxidation versus hydrolysis) responsible for their clearance. This study aims to further explore the species differences in the metabolism of these chemicals. Using a parent depletion approach, rat and human cytochromes P450 (P450s) were screened for their ability to eliminate deltamethrin or esfenvalerate during in vitro incubations. Rat P450 isoforms CYP1A1, CYP2C6, CYP2C11, and CYP3A2 and human P450 isoforms CYP2C8, CYP2C19, and CYP3A5 were capable of metabolizing either pyrethroid. Human CYP2C9 metabolized esfenvalerate but not deltamethrin. Rat and human P450s that metabolize esfenvalerate and deltamethrin do so with similar kinetics. In addition to the liver, a potential site of metabolic elimination of pyrethroids is the blood via serum carboxylesterase (CE) hydrolysis. The serum of rats, but not humans, contains significant quantities of CE. Deltamethrin and esfenvalerate were metabolized effectively by rat serum and a purified rat serum CE. In contrast, neither pyrethroid was metabolized by human serum or purified human serum esterases (acetylcholinesterase and butyrylcholinesterase). These studies suggest that the difference in rates of oxidative metabolism of pyrethroids by rat and human hepatic microsomes is dependent on the expression levels of individual P450 isoforms rather than their specific activity. Furthermore, these studies show that the metabolic elimination of deltamethrin and esfenvalerate in blood may be important to their disposition in rats but not in humans.
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PMID:Identification of rat and human cytochrome p450 isoforms and a rat serum esterase that metabolize the pyrethroid insecticides deltamethrin and esfenvalerate. 1757 9

A suite of biomarkers were measured in barramundi (Lates calcarifer) from five North Queensland estuaries along a perceived pollution gradient. The biomarkers selected were 7-ethoxyresorufin-O-deethylase (EROD), cytochrome P450, fluorescent aromatic compounds (FACs), DNA integrity, RNA:DNA ratio, cholinesterase activity (ChE), condition factor and hepatosomatic index. The resulting database was subjected to uni- and multi-variate analyses in order to assess the most suitable biomarkers to assess pollution in North Queensland estuaries and to classify the environmental quality of the sites. Principal components analysis (PCA) on the biochemical markers revealed that EROD, EROD/P450, DNA damage and to a lesser extent ChE and FACs were found to be responsive to contaminants in the environment while cytochrome P450, condition factor and the hepatosomatic index were found to be less responsive biomarkers. This study has demonstrated the utility of applying a multibiomarker approach in conjunction with traditional analysis of contaminants in providing valuable information in environmental risk assessment.
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PMID:A multibiomarker approach in barramundi (Lates calcarifer) to measure exposure to contaminants in estuaries of tropical North Queensland. 1769 40


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