Gene/Protein Disease Symptom Drug Enzyme Compound
Pivot Concepts: Gene/Protein Disease Symptom Drug Enzyme Compound   Target Concepts: 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)

Bobwhite quail eggs were injected at 48 or 72 hr of incubation with various doses of the organophosphate (OP) insecticides diazinon or parathion and the embryos were examined after an additional 48 hr of incubation by both histological and cartilage-staining methods. Bobwhite embryos did not display the notochordal folding or vascular enlargement reported for OP-injected chicken embryos. Cartilage staining of embryos injected with insecticide at 72 hr of incubation and recovered at day 12 of incubation revealed severe shortening and contortion of the vertebral axis, as well as tibiotarsal, rib, and sternum defects. Parathion was more potent in causing skeletal defects than diazinon. No type I defects (micromelia, parrot beak) were detected. Radiometric acetylcholinesterase (AChE) assays of whole embryo homogenates were performed for day 6, 9, and 12 diazinon-injected and control embryos. Diazinon effected drastic reductions in AChE activity. Although the AChE and axial skeletal responses of bobwhite embryos to OP injection are similar to those reported in the literature for other species, some major differences in the bobwhite response were noted: namely, the absence of notochordal folding in the young bobwhite embryo and the absence of type I defects at day 12. These differences suggest that further studies with the bobwhite quail would be useful in clarifying the mechanisms involved in OP-induced teratogenesis.
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PMID:Effects of the organophosphate insecticides diazinon and parathion on bobwhite quail embryos: skeletal defects and acetylcholinesterase activity. 280 35

The tissue distribution of diazinon and the inhibition of blood cholinesterase (ChE) activity were investigated in male rats which received a single intraperitoneal (i.p.) dose of diazinon (100 mg/kg body wt) in olive oil. Diazinon concentration in the blood reached a maximum 1-2 h after dosing. Comparing the distribution of diazinon among liver, kidney and brain in treated rats, the diazinon residue was much greater in the kidney than in other organs, being 500 times that in the liver and 11 times that in the brain at 8 h after dosing. Erythrocyte and plasma ChE activities were inhibited rapidly, but ChE inhibition was greater in the erythrocytes than in plasma.
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PMID:Diazinon concentrations and blood cholinesterase activities in rats exposed to diazinon. 399 5

Treatment of rats with chlorpromazine (CPZ, 15 mg/kg i.p. 60 min before sacrifice) did not modify cholinesterase (ChE) activity, but considerably enhanced the inhibition of total ChE induced by physostigmine (PhS, 0.5 mg/kg i.p. 40 min after CPZ) in brain, skeletal muscle, myocardium, lung, liver, and kidney. Additional experiments also showed a prolongation of PhS inhibition by CPZ in brain. The enhanced inhibition of total ChE due to CPZ depended in most peripheral organs on the effect on pseudoChE (as measured by a spectrophotometric method), except in the case of skeletal muscle in which potentiation of PhS effect was observed on true acetylcholinesterase (AcChE). The results indicate that the potentiation by CPZ of PhS inhibition occurs in all organs tested and is relatively non specific. CPZ was found to potentiate slightly the effects of Mevinphos but did not interact with Carbaryl, Diazinon or Azinphos. Furthermore, haloperidol did not potentiate the effects of physostigmine.
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PMID:Interactions between anticholinesterase agents and neuroleptics in terms of cholinesterase inhibition in brain and other tissues of rats. 613 14

An occupational study was conducted for a firm employing 22 pest control operators (PCOs) exposed to three organophosphorus insecticides. Measurements of 8-hour exposure levels were less than: 131.0 microgram/m3 for Vaponite; 41.0 microgram/m3 for Diazinon; and 27.6 microgram/m3 for Dursban. Twenty-four-hour urines analyzed for alkyl phosphates showed the presence of metabolites for these three pesticides. The effect of this exposure is reflected by a statistically significant inhibition of plasma acetylcholinesterase (AChE) among the PCOs as AChE values of either group. Although physical examinations detected no apparent toxic effects in the study group, biological sampling results indicated a need for personal protective equipment during the handling and application of these pesticides.
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PMID:Assessment of occupational exposure to organophosphates in pest control operators. 740 25

We investigated the effects of a turf application of the insecticide diazinon AG500 on Canada geese (Branta canadensis) on a golf course in coastal Washington (USA). On both 19 and 26 March 1987, 1 ha of turf on a golf course located in Birch Bay, Washington was treated with diazinon AG500 at a target application rate of 2.2 kg active ingredient per hectare (AI/ha). Treated areas were then irrigated with 6 mm water. Grass and water samples were collected from three different sites one day before and 1, 3, 7 and 14 days after each application. Diazinon residues > or = 20 ppm were found in golf course grasses for one week after each application. Diazinon residues in study area ponds and creeks were > or = 17 ppb. Samples from two irrigation puddles one day post-application had 1.00 and 0.20 ppm of diazinon, respectively. Numbers of geese present declined following diazinon application; however, no goose mortality was observed. Geese spent 422 and 538 min feeding on the treated areas after the first and second diazinon applications, respectively. One goose feeding in treated areas demonstrated signs of poisoning (lethargy, ataxia) for several hours. Two other geese feeding in the treated areas may have been slightly intoxicated. During carcass searches, three American wigeon (Anas americana) carcasses were found. Based on brain cholinesterase (ChE) levels and gastrointestinal (GI) tract residues of diazinon present, we concluded that these wigeon died from diazinon poisoning. Numerous songbirds (Passeriformes) also fed on the treated turf but no apparent response to the insecticide was observed.
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PMID:Response of Canada geese to a turf application of diazinon AG500. 835 49

The serum cholinesterase (ChE) isoenzyme in rats shows 6 bands after polyacrylamide gradient gel electrophoresis. The effects of organophosphates (fenthion, chlorpyrifos, diazinon, bromophos, propaphos, haloxon, and DFP) on serum ChE isoenzyme bands were studied in 32 male and 32 female 6-w-old Sprague-Dawley rats. Each organophosphate was randomly administered to 4 male and 4 female rats. Blood samples were collected from the abdominal aorta under halothane anesthesia 6 h after dosing. The isoenzyme patterns were determined simultaneously with erythrocyte and serum ChE activities. Changes were observed in all 6 bands of the serum ChE isoenzymes after administration of fenthion, chlorpyrifos and propaphos. Diazinon had no influence on band 6, and DFP and bromophos had no influence on band 5. Haloxon did not effect any of the serum ChE isoenzyme bands. Serum ChE was most suppressed by fenthion, followed by DFP, bromophos, chlorpyrifos, propaphos and diazinon in that order of effect. Serum ChE activity was not suppressed by haloxon. Erythrocyte ChE activity was suppressed by every organophosphate. This experiment demonstrated a correlation between the organophosphate suppression of serum ChE activity and the concentration of serum ChE isoenzyme band 6.
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PMID:Effects of selected organophosphate insecticides on serum cholinesterase isoenzyme patterns in the rat. 872 19

The toxicokinetics, tissue distribution, and anticholinesterase (antiChE) activity of diazinon were investigated in the rat. Plasma concentrations most adequately fitted a two-compartment open model after i.v. administration of 10 mg/kg and a one-compartment model after oral administration of 80 mg/kg. Diazinon elimination half-life following i.v. and oral dosing was 4.70 and 2.86 h, respectively. The oral bioavailability was found to be low (35.5%). Hepatic extraction ratios after i.v. administration of 5 or 10 mg/kg were 54.8% and 47.7%, respectively, suggesting that low systemic oral bioavailability can be explained by a first-pass effect in the liver. Diazinon was found to be approximately 89% protein-bound in plasma within the concentration range 0.4-30 ppm. The highest concentration of diazinon after i.v. administration was found in the kidneys, when comparing to liver, kidney, brain. Both red blood cell (RBC) acetylcholinesterase (AChE) and plasma ChE activities were inhibited rapidly (44% and 17% at 10 min, and 36% and 13% min for i.v. and oral administration, respectively), but inhibition of RBC AChE was greater than that of plasma ChE.
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PMID:Diazinon toxicokinetics, tissue distribution and anticholinesterase activity in the rat. 898 4

Recent monitoring of the Sacramento-San Joaquin River system (CA) indicates that levels of the organophosphate pesticide, diazinon, exceed National Academy of Science guidelines and these levels result in toxicity in USEPA acute toxicity tests with Ceriodaphnia dubia. Since organophosphates (OPs) inhibit acetylcholinesterase (AChE), the present study examined the effects of diazinon on the embryonic nervous system of a model teleost, medaka, Oryzias latipes. Preliminary histological screens revealed limited retinal cell necrosis in control embryos with apparent increased necrosis in diazinon-exposed embryos. Subsequently, embryos were exposed to 1.8 x 10(-5), 4.4 x 10(-5), or to 8.8 x 10(-5) M diazinon and replicates were frozen for biochemical analysis or were fixed for histopathological analysis at days 3, 5, and 7 of development. Diazinon exposure significantly inhibited AChE activity within whole embryos and in homogenates of retinas from treated animals. Histological examination of embryos indicated that as the retina underwent differentiation into distinct cell layers, between days 5 and 7, small foci of necrotic cells became apparent within the inner nuclear layer and isolated individual pyknotic cells were observed in the ganglion layer. Quantification of foci of necrotic cells revealed that 8.8 x 10(-5) M diazinon increased number and area of these lesions. Enzyme histochemistry localized AChE activity to regions equivalent to sites of necrosis. Separate exposures of embryos to the OP, diisopropylphosphorofluoridate, produced large foci of necrotic cells at sites equivalent to those seen following diazinon exposure.
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PMID:Organophosphate-induced acetylcholinesterase inhibition and embryonic retinal cell necrosis in vivo in the teleost (Oryzias latipes). 986 74

Pesticide pollution in coastal ecosystems of Sinaloa, Mexico is considered to be a cause for slow growth, increase of diseases and sometimes massive mortality of shrimp. So it was necessary to develop fast techniques to detect pesticide pollution in shrimp habitats. Enzymatic and osmoregulation tests in shrimp exposed to DDT, Lindane, Chlordane, Lorsban, Gusathion, Folidol, Diazinon and Tamaron were carried out. Activity reductions from 11 to 2 units/ml in acetylcholinesterase and from 1 to 0 units/l in transaminases (GOT and GPT) were detected. Also increases in osmoregulation were observed in shrimp exposed to Folidol, Diazinon and Gusation, whereas decreases with DDT, Lindane and Lorsban at salinity 50/1000. We conclude that pesticides are causing alterations in these biochemical functions and this kind of tests represent a rapid and inexpensive method for pesticide pollution detection.
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PMID:Enzymatic and osmoregulative alterations in white shrimp Litopenaeus vannamei exposed to pesticides. 1066 12

Diazinon is an organophosphorus compound (OP) widely used in pesticides. The relationship between dose of diazinon, inhibition of acetylcholinesterase, and effect on neuromuscular transmission has been studied in a mouse model. Inhibition of acetylcholinesterase activity occurred within 1 h, was maximal by 3 h and remained inhibited for at least 24 h. Blood, brain, diaphragm, and soleus acetylcholinesterase activities were differentially affected by diazinon. Brain and soleus activities were not affected by low doses. Multiple daily dosing of diazinon caused a cumulative decrease in acetylcholinesterase activity, although to a lesser extent in brain and soleus. Diazinon had no effect on the activity of neuropathy target esterase. Plasma and brain levels of diazinon peaked at 15 min after dosing and declined with a half-life of 2.5 h. Metabolic products of diazinon were cleared from the urine within 24 h. Increased miniature end-plate current half decay times occurred in a dose-dependent manner. Single doses of diazinon caused an increase in the jitter (variability of latencies) of evoked action potentials recorded in the diaphragm but did not affect end-plate potential (EPP) jitter. Multiple lower doses of diazinon caused an increase in EPP jitter after 28 days. This effect on nerve function was delayed and occurred when acetylcholinesterase activity had returned to control levels. The results indicate that diazinon produces long-term electrophysiological changes in neurotransmission following repeated dosing in the mouse. This has implications for the current use of diazinon; however, there is a need to further define the mechanism of this effect.
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PMID:Electrophysiological and biochemical effects of single and multiple doses of the organophosphate diazinon in the mouse. 1089 49


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