Gene/Protein Disease Symptom Drug Enzyme Compound
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Query: EC:3.1.1.7 (acetylcholinesterase)
28,390 document(s) hit in 31,850,051 MEDLINE articles (0.00 seconds)

Carbaryl, a carbamate insecticide, exerts its toxic effect in animals by inhibiting the activity of neural acetylcholinesterase. Differences in sensitivity of this enzyme to inhibition were studied after intraperitoneal administration to chickens and rats. A dose of 900 mg/kg to chickens and 70 mg/kg to rats caused equivalent inhibition of brain cholinesterase activities (57% +/- 6 and 47% +/- 4, respectively) 60 min after administration, which was the time of maximal cholinergic signs. Signs of toxicity (salivation, respiratory distress, muscle tremors and weakness) were more pronounced in rats than in chickens when brain acetylcholinesterase was inhibited to the same extent in both species. Carboxylesterase activities in brain, liver, and plasma were also inhibited 60 min after administration of carbaryl to chickens and rats. Activities of enzymes associated with hepatic microsomes were unaffected. Specific activities of brain esterases, including acetylcholinesterase, carboxylesterase and neurotoxic esterase, were higher in untreated chickens than in untreated rats. Specific activities of liver esterases (carboxylesterase, A-esterase) were, however, 4- and 10-fold lower in untreated chickens than in untreated rats. Total clearance of carbaryl in the chicken, determined after intravenous administration of 5 mg/kg, was 0.26 +/- 0.02 l/kg/min. This value is 5.7 times higher than that reported for the rat, indicating that the relatively lower activities of esterases in the liver of chickens did not affect the clearance of this chemical in the avian species.
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PMID:Toxicity and toxicokinetics of carbaryl in chickens and rats: a comparative study. 150 71

The ability of endogenous carboxylesterase (CaE) to protect against the lethal effects of a variety of organophosphorus (OP) compounds was examined in rats. The in vivo protection provided by endogenous CaE was measured by the difference in the LD50 values of OP compounds in control rats and rats whose CaE activity had been inhibited by sc injection with 2 mg/kg of 2-(O-cresyl)-4H-1,3,2-benzodioxaphosphorin-2-oxide. Endogenous CaE provided significant protection against the in vivo toxicity of soman, sarin, tabun, and paraoxon, but not against dichlorvos, diisopropyl fluorophosphate, or ethoxymethyl-S-[2-(diisopropylamino)ethyl] thiophosphonate (VX). The relationship between the in vivo CaE protection against OP compounds and their relative reactivities with CaE and acetylcholinesterase (AChE) was evaluated by measuring the in vitro bimolecular rate constants (ki) for inhibition of plasma CaE and brain AChE. Except for VX, ki values for CaE inhibition varied less than 10-fold while ki values for AChE inhibition varied 10(5)-fold. The degree of in vivo inhibition of CaE by equitoxic doses of the OP compounds increased as the CaE/AChE ki ratio increased. However, the protective ratio of the LD50 values in control vs CaE-inhibited rats decreased as the CaE/AChE ki ratio increased. This inverse relationship between in vivo CaE protection and relative in vitro reactivity for CaE suggested that CaE detoxication is more important for highly toxic OP compounds (i.e., compounds with high AChE ki values and low LD50 values) than for less toxic compounds.
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PMID:The specificity of carboxylesterase protection against the toxicity of organophosphorus compounds. 160 24

The effect of dichlorvos on inducing changes in blood esterase activities and systemic toxicity was investigated following single topical applications of 1, 3 or 6% dichlorvos concentrations to male calves. Dichlorvos at 1% concentration did not produce any signs of toxicity, whereas 3 and 6% concentrations induced mild to severe toxicity characteristic of anticholinesterase poisoning. Dichlorvos at all concentrations significantly inhibited erythrocyte cholinesterase (25-75%), plasma cholinesterase (30-85%), and serum carboxylesterase (15-51%) activities in male calves. The dose-dependent inhibition was maximum 12 h after insecticide exposure. The extent of inactivation of blood esterases was not correlated with the severity of toxicity. Inhibition of blood cholinesterases by the 6% dichlorvos was still present 21 d after the dichlorvos exposure.
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PMID:The influence of single topical application of dichlorvos on blood esterases and toxicity in male calves. 160 93

With the aim of proposing a nondestructive biomarker for monitoring the toxicological risk to birds of exposure to the organophosphorus insecticide azamethiphos and the carbamate insecticide methomyl, laboratory studies were performed on serum "B" esterases in Japanese quail (Coturnix coturnix japonica). The birds received two single dose treatments of each compound (azamethiphos and methomyl), i.e., 50 mg/kg and 250 mg/kg respectively. In the first treatment, serum butyrylcholinesterase (BChE) and carboxylesterase (CbE) were drastically inhibited in the azamethiphos-treated group, 24 h after the dose. No inhibition was detected for BChE and CbE activities in the methomyl-treated group, 24 h after the dose. In the second treatment, the birds died or were sacrificed 3 h after the dose. Serum BChE and brain acetylcholinesterase (AChE) were strongly inhibited after treatment with both insecticides. Serum CbE, hepatic microsomal CbE and 7-ethoxyresorufin dealkylation activities were also inhibited. A statistically significant correlation between serum BChE and brain AChE was found at lethal and sublethal doses of these xenobiotics. The experimental results indicate that the nondestructive biomarker BChE can give an early qualitative and semi-quantitative warning of the toxic effects of organophosphate and carbamate insecticides in birds.
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PMID:Serum esterase inhibition in birds: a nondestructive biomarker to assess organophosphorus and carbamate contamination. 163 4

Newly fertilized Bufo arenarum Hensel embryos were exposed continuously or for a brief period (72-120 hr) to malathion (44 ppm) and then resuspended in amphibian Ringer's solution. Continuous exposure depressed acetylcholinesterase (EC 3.1.1.7), butyrylcholinesterase (EC 3.1.1.8) and carboxylesterase (EC 3.1.1.1) activities. The activities of the three enzymes in embryos treated for 72 hr recovered after a delay of 24 hr, but these enzymes showed different rates of recovery in embryos treated for 120 hr. Acrylamide disc electrophoresis showed several bands of esterase activity in control embryos. Continuous exposure to malathion abolished all esterase activity within 48 hr, but if the exposure continued new bands of esterase activity appeared at 120 hr of exposure. The zymograms of embryos exposed for 72 or 120 hr to malathion and then transferred to uncontaminated medium for 120 hr were similar to that of control embryos.
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PMID:Effect of malathion on Bufo arenarum Hensel development--I. Esterase inhibition and recovery. 190 4

2,3-Butanedione monoxime and atropine alone or in combination were evaluated for their ability to alleviate the toxicity and to reverse the biochemical changes induced by dichlorvos in the blood of buffalo calves. Treatment with 2,3-butanedione monoxime plus atropine 30 min after oral administration of dichlorvos (160 mg/kg) eliminated the apparent toxic signs within 10-15 min, completely prevented lethality, and reversed the dichlorvos-induced alterations in the concentrations of serum carboxylesterase, total plasma proteins, blood glucose and plasma cholinesterase within 2, 4, 12 and 168 h, respectively. Treatment with either 2,3-butanedione monoxime or atropine alone was less effective but the former was the more potent of the two in counteracting the biochemical effects of dichlorvos. These antidotal studies suggest that 2,3-butanedione monoxime in conjunction with atropine would provide effective therapy against severe dichlorvos intoxication in buffalo.
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PMID:The therapeutic effects of 2,3-butanedione monoxime and atropine in severe dichlorvos intoxication in buffalo calves. 194 6

Serum cholinesterase (BChE) and carboxylesterase (CbE) activities were investigated in ten species of birds. Multiple forms of serum BChE and CbE were also separated by chromatofocusing. Higher CbE activity and a wider range of CbE and BChE forms were present in the sera of omnivorous/herbivorous birds than carnivores. Omnivores/herbivores studied were the starling, house sparrow, tree sparrow, pigeon, partridge and magpie. Serum CbE activities of these species ranged from 0.46 to 2.93 mumol/min/mL with 2-6 forms separated by chromatofocusing. 0-6 forms of BChE were separated by the same method. The serum CbE activities of the little owl, tawny owl, barn owl and razorbill ranged from 0.19 to 0.58 mumoles/min/mL with 0-2 forms separated by chromatofocusing. No ChE forms were present within the pH gradient. These results may be significant in contributing to the understanding of the selective toxicity of organophosphorus and carbamate pesticides.
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PMID:Species differences in avian serum B esterases revealed by chromatofocusing and possible relationships of esterase activity to pesticide toxicity. 200 98

The embryonic chick has long been a model for developmental biology and has often been recommended as a model system in developmental toxicology. More recently, several investigators have shown that the chick embryo also provides a good model for identifying the neurotoxic effects of environmental pollutants, especially cholinesterase-inhibiting pesticides. Although numerous studies detail the structural development of chick embryos, few describe embryonic levels of enzyme synthesis and their changes during development. In this study, the development of esterase activity in chick embryos was measured from day 9 of incubation until 46 days after hatching. Brain acetylcholinesterase (AChE) activity was detected on day 9 of incubation at a concentration of 0.364 mumoles/min/g tissue. An increase between AChE activity and age of the embryos was observed. In the liver, the nonspecific cholinesterases (ChE) and carboxylesterase activities during incubation were not different from activities after the chicks had hatched. Plasma ChE and carboxylesterase activities did not change with age after hatching. Brain neuropathy target esterase (NTE) activity was not detected on day 9 of incubation and was extremely low (6.12 nmoles/15 min/mg protein) the next day, but increased rapidly with increasing age. This study demonstrates that chick embryos have developed esterase activities in the brain and liver by day 10 of incubation and again confirms that the insensitivity of chick embryos and young chicks to organophosphorus ester-induced delayed neurotoxicity is not due to absence of NTE. In addition, the results provide baseline data for evaluating the response of embryonic and immature chicks to neurotoxicants and teratogens.
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PMID:Development of esterase activities in the chicken before and after hatching. 204 34

Rats have very high endogenous levels of serum carboxylesterase (CAE) compared to primates. This difference accounts for the lower sensitivity of rats to toxic organophosphates, which interact with CAE instead of the more critical acetylcholinesterase. Pretreatment of rats with CAE inhibitors potentiates the effects of organophosphates. In this study, the effects of three putative CAE inhibitors, 2-(o-Cresyl)-4H-1:3:2-benzodioxaphosphorin-2-oxide (CBDP), bis-p-nitrophenyl-phosphate (BNPP), and tetraisopropyl pyrophosphoramide (Iso-OMPA), on the hydrolysis of several commercially available substrates were determined. Respective kinetic constants Km and Vmax were derived and effects of inhibitors compared using saturating amounts of substrate. Data presented here indicate significant differences in substrate affinity (Km), reactivity (Vmax), as well as effects of inhibitors. CBDP inhibits hydrolysis of specific naphthyl and paranitrophenyl esters at relatively low concentrations (1-10 microM). In contrast, significantly higher concentrations (mM) of BNPP and Iso-OMPA were required for inhibition of serum esterase activity. Of the inhibitors tested, Iso-OMPA in general exhibited the smallest inhibitory effect on ester hydrolysis. Although inhibition of hydrolysis of specific paranitrophenyl and naphthyl esters occurred in the presence of similar amounts of CBDP, the degree of inhibition differed significantly (50-75% vs. greater than 90%, respectively). These data suggest that there exists in rat serum, a pool of naphthyl ester esterase activity that is very sensitive ex vivo (greater than 90% inhibition) to CBDP and may be very useful in validating a rodent model for soman toxicity.
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PMID:Effects of three reputed carboxylesterase inhibitors upon rat serum esterase activity. 205 4

1. The inhibition of cholinesterase and carboxylesterase activities in the diisopropyl fluorophosphate (DFP) intoxication, and the inducibility of organophosphate (OP) detoxicating enzymes was studied in rats. 2. In phenobarbital (PB)-, but not in beta-naphthoflavone (NF)-pretreated rats, the activities of DFP-inhibited cholinesterases were 70-120% higher than in non-pretreated rats. Also the inhibition of the microsomal and cytosolic carboxylesterase activity in liver was efficiently antagonized by BP, but not by NF. 3. In vitro the microsomes from PB-treated rats detoxicated DFP probably by O-dealkylation, since no fluoride was released from DFP. Glutathione S-transferase did not detoxicate DFP. 4. 7-Pentoxyresorufin O-dealkylase, a specific enzyme of cytochrome P450IIB subfamily, was induced by PB, flumecinol, isosafrole and NF by 167- 61-, 26- and 1.6-fold, respectively. 7-Ethoxyresorufin O-deethylase, a marker enzyme of cytochrome P450IA subfamily, was induced by those agents 5-, 4-, 31- and 94-fold, given in the same order. Glutathione S-transferase, paraoxonase and DFPase activities were increased 0-72% by the tested inducers. 5. The results suggest that the cytochrome P450IIB subfamily, inducible by PB, participates in DFP detoxication by O-dealkylation. Its induction probably causes the protection against the cholinesterase inhibition by OPs.
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PMID:Inhibition of cholinesterases by DRP and induction of organophosphate-detoxicating enzymes in rats. 216 59


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