Liver Carboxylesterase Activity Research Articles

Sensitivity of cholinesterases and carboxylesterases to pharmaceutical products in Tinca tinca.

Discharges to the aquatic environment of pharmaceuticals represent a hazard to the aquatic organisms. Subchronic assay with 17-alpha-ethinylestradiol (EE2) and in vitro essays with pharmaceuticals of environmental concern were conducted to examine the sensitivity of tissue acetylcholinesterase (AChE) and carboxylesterase (CbE) activities of Tinca tinca to them. Subchronic exposure to 17-alpha-EE2 caused significant effects on brain, liver, and muscle CbE, but no on AChE activities. Most of the pharmaceuticals tested in vitro were considered as weak inhibitors of tissular AChE activity. Depending on the tissues, some compounds were classified as moderate inhibitors of CbE activity while other were categorized as weak enzymatic inhibitors. An opposite trend was observed depending on the tissue, while brain and liver CbE activities were inhibited, the muscle CbE activity was induced. Changes experienced on enzymatic activities after exposure to pharmaceuticals might affect the physiological functions in which these enzymes are involved. In vitro exposure to 17-alpha-EE2 in tench could be an informative, but not a surrogate model to know the effect of this synthetic estrogen on AChE and CbE activities.

Role of geraniol against lead acetate-mediated hepatic damage and their interaction with liver carboxylesterase activity in rats

In this study, the effect of geraniol (50 mg/kg for 30 d), a natural antioxidant and repellent/antifeedant monoterpene, in a rat model of lead acetate-induced (500 ppm for 30 d) liver damage was evaluated. Hepatic malondialdehyde increased in the lead acetate group. Reduced glutathione unchanged, but glutathione S-transferase, glutathione reductase, as well as carboxylesterase activities decreased in geraniol, lead acetate and geraniol + lead acetate groups. 8-OhDG immunoreactivity, mononuclear cell infiltrations and hepatic lead concentration were lower in the geraniol + lead acetate group than the lead acetate group. Serum aspartate aminotransferase and alanine aminotransferase activities increased in the Pb acetate group. In conclusion, lead acetate causes oxidative and toxic damage in the liver and this effect can reduce with geraniol treatment. However, we first observed that lead acetate, as well as geraniol, can affect liver carboxylesterase activity.

Carboxylesterase activities in chondrichthyans of the western Mediterranean Sea

Sharks, rays, skates and chimaeras play an important role as predators in the ecosystems. These species could serve as potential sentinels for the presence of xenobiotics in marine ecosystems. In this study, liver carboxylesterase (CbE) activity was determined for 20 species of chondrichthyans. Carboxylesterase activity, a known esterase involved in the metabolism of pesticides, lipids and certain drugs, was measured using two substrates: 4-nitrophenyl acetate (pNPA) and α-naphthyl acetate (αNA). Rajiformes (rays and skates) showed higher CbE activity than sharks, and the order Chimaeriformes showed the lowest values. In vitro sensitivity to CbE inhibitors was assessed in the shark Scyliorhinus canicula. The substrate αNA was found to be the most adequate as it displayed the highest activity and was more sensitive to the organophosphate dichlorvos in the liver (IC50=2.37μM) and plasma (IC50=0.051μM). The high interspecific variation of CbE activity and its sensitivity to inhibition by fenofibrate suggest that this enzyme could contribute to species-specific differences in drug detoxification.

Inhibitory effects of the Food Azo Dyes on Pig Liver Carboxylesterase Activity

Inhibitory effects of the Food Azo Dyes on Pig Liver Carboxylesterase Activity

Possible mechanism for inhibition of morphine formation from 6-acetylmorphine after intake of street heroin

Heroin is de-acetylated in the body to morphine in two steps. The intermediate 6-acetylmorphine (6-AM) is formed rapidly and is considered important for the pharmacological effect of heroin. In urine drug testing, an atypical pattern of morphine and 6-AM is known to occur in low frequency. The aim of this study was to investigate this atypical pattern in more detail and to identify responsible substances for a possible inhibition of the conversion from 6-AM to morphine. Urine samples were selected from a routine flow of samples sent for drug testing. Out of 695 samples containing morphine and 6-acetylmorphine, 11.5% had the atypical pattern of a 6-AM to morphine ratio above 0.26 as derived from a bimodal frequency distribution. An in vitro study of the conversion of 6-acetylmorphine to morphine in human liver homogenates demonstrated that a number of known carboxylesterase inhibitors were able to inhibit the reaction mimicking the situation in vivo. Compound 3 (3,6-Dimethoxy-4-acetoxy-5-[2-(N-methylacetamido)ethyl]phenanthrene) a substance formed from thebaine during the production of heroin was found to be a strong inhibitor. Liquid chromatography–mass spectrometry was used to identify possible inhibitors present in vivo. This part of the investigation demonstrated that several components may contribute to the effect. It is concluded that inhibition of liver carboxylesterase activity is a possible mechanism causing the atypical pattern and that one candidate compound is the result of the heroin production process. An inhibition of 6-AM metabolism is likely to increase the pharmacological effect of heroin and may be related to a higher risk of lethal toxicity.

Evidence for diazinon-mediated inhibition of cis-permethrin metabolism and its effects on reproductive toxicity in adult male mice

The potential toxicity resulting from combinatorial effects of organophosphorus and pyrethroid insecticides are not completely known. We evaluated male reproductive toxicity in mice co-exposed to diazinon and cis-permethrin. Nine-week-old male Sv/129 mice were exposed to diazinon (10μmol/kg/day) or cis-permethrin (90μmol/kg/day) alone or in combination (100μmol/kg/day), or vehicle (corn oil), for 6 weeks. Diazinon and the diazinon–permethrin mixture inhibited plasma and liver carboxylesterase activities. In the mixture group, urinary excretion of cis-permethrin metabolite 3-phenoxybenzoic acid decreased along with increased plasma and testicular concentrations of cis-permethrin, while excretion of diazinon metabolites, diethylphosphate and diethylthiophosphate, did not change, versus mice exposed to each chemical alone, which suggested that inhibition of carboxylesterase decreased the metabolic capacity to cis-permethrin. Though the co-exposure decreased testosterone biosynthesis, increased degenerate germ cells in seminiferous tubule and sperm morphological abnormalities versus controls more clearly than exposure to cis-permethrin alone, the expected potentiation of toxicity was not evident.

Structural Organization and Characterization of the Regulatory Element of the Human Carboxylesterase (CES1A1 and CES1A2) genes

Mammalian carboxylesterases comprise a multigene family, the gene products of which are localized in the endoplasmic reticulum. The carboxylesterases catalyze the hydrolysis of various xenobiotics and endogenous substrates such as ester, amide and thioester bonds and are thought to function mainly in drug metabolism. We have suggested the possibility that individual variation of human liver carboxylesterase activity causes the difference in expression levels of CES1A isozymes. However, little is known about the transcriptional regulation of human carboxylesterase genes. In the present study, we isolated two CES genes encoding human carboxylesterase CES1A, which were designated as CES1A1 (AB119997) and CES1A2 (AB119998). These genes were identical except for exon 1 and the 5' regulatory element. We investigated the transcriptional regulation of these two CES genes. A reporter gene assay and electrophoretic mobility shift assay demonstrated that Sp1 and C/EBPalpha could bind to each responsive element of the CES1A1 promoter but that the Sp1 and C/EBP could not bind to the responsive element of the CES1A2 promoter. Thus, CES1A1 mRNA expression level is much higher than the expression level of CES1A2 mRNA in the liver and lung. It is thought that these results provide information on individual variation of human carboxylesterase isozymes.

Individual variability in esterase activity and CYP1A levels in Chinook salmon ( Oncorhynchus tshawytscha) exposed to esfenvalerate and chlorpyrifos

Acetylcholinesterase (AChE) activity has traditionally been monitored as a biomarker of organophosphate (OP) and/or carbamate exposure. However, AChE activity may not be the most sensitive endpoint for these agrochemicals, because OPs can cause adverse physiological effects at concentrations that do not affect AChE activity. Carboxylesterases are a related family of enzymes that have higher affinity than AChE for some OPs and carbamates and may be more sensitive indicators of environmental exposure to these pesticides. In this study, carboxylesterase and AChE activity, cytochrome P4501A (CYP1A) protein levels, and mortality were measured in individual juvenile Chinook salmon ( Oncorhynchus tshawytscha) following exposure to an OP (chlorpyrifos) and a pyrethroid (esfenvalerate). As expected, high doses of chlorpyrifos and esfenvalerate were acutely toxic, with nominal concentrations (100 and 1 μg/l, respectively) causing 100% mortality within 96 h. Exposure to chlorpyrifos at a high dose (7.3 μg/l), but not a low dose (1.2 μg/l), significantly inhibited AChE activity in both brain and muscle tissue (85% and 92% inhibition, respectively), while esfenvalerate exposure had no effect. In contrast, liver carboxylesterase activity was significantly inhibited at both the low and high chlorpyrifos dose exposure (56% and 79% inhibition, respectively), while esfenvalerate exposure still had little effect. The inhibition of carboxylesterase activity at levels of chlorpyrifos that did not affect AChE activity suggests that some salmon carboxylesterase isozymes may be more sensitive than AChE to inhibition by OPs. CYP1A protein levels were ∼30% suppressed by chlorpyrifos exposure at the high dose, but esfenvalerate had no effect. Three teleost species, Chinook salmon, medaka ( Oryzias latipes) and Sacramento splittail ( Pogonichthys macrolepidotus), were examined for their ability to hydrolyze a series of pyrethroid surrogate substrates and in all cases hydrolysis activity was undetectable. Together these data suggest that (1) carboxylesterase activity inhibition may be a more sensitive biomarker for OP exposure than AChE activity, (2) neither AChE nor carboxylesterase activity are biomarkers for pyrethroid exposure, (3) CYP1A protein is not a sensitive marker for these agrochemicals and (4) slow hydrolysis rates may be partly responsible for acute pyrethroid toxicity in fish.

Comparative carboxylesterase activities in infant and adult liver and their in vitro sensitivity to chlorpyrifos oxon

Maturational expression of carboxylesterase activity in laboratory animals has been correlated with age-related differences in sensitivity to many organophosphorus insecticides including chlorpyrifos. Little information is available, however, on the maturational expression of liver carboxylesterases in humans. Human liver carboxylesterase activity was compared in tissues from infants (2–24 months) and adults (20–36 years). There was no significant difference between mean infant and adult carboxylesterase activities. The carboxylesterase activity rank order was: 2 months < 3 months < 20 years < 24 months < 4 months < 36 years < 21 years < 8 months < 34 years < 35 years. Proteins (3 μg) were separated and blotted using antibodies against rat hydrolase S (HS), human carboxylesterase (HCE) types 1 and 2, and CYP3A4. Again, there were no significant differences in staining density between infant and adult tissues with any isozyme. Aliquots of each sample were pre-incubated (30 min, 37 °C) with chlorpyrifos oxon to evaluate in vitro sensitivity. Based on 95% confidence intervals, no significant differences in IC 50 values were obtained in 3-month to 36-year samples (range: 1.42–2.12 nM), while the IC 50 was significantly lower in the 2-month sample (0.45 nM). Carboxylesterase activity across samples was correlated with cytochrome b5 content and HS immunosignal but not with other microsomal activities (total cyt P450 content, testosterone hydroxylation, coumarin hydroxylation, and EROD). The results suggest that, in contrast to rodents, human liver carboxylesterase expression changes relatively little during postnatal maturation.

Effects of Gestational Exposure to Chlorpyrifos on Postnatal Central and Peripheral Cholinergic Neurochemistry

The effects of gestational exposure to the commonly used organophosphorus insecticide chlorpyrifos (O,O-diethyl O-[3,5,6-trichloro-2-pyridinyl]phosphorothioate) on postnatal central and peripheral cholinergic neurochemistry were investigated. Pregnant rats were orally dosed daily with chlorpyrifos (0, 3, 5, or 7 mg/kg) in corn oil from gestation day 6 to 20. Pups were sacrificed on postnatal days 1, 3, 6, 9, and 12 for the determination of brain, heart, lung, and serum cholinesterase, and brain choline acetyltransferase activities, along with liver carboxylesterase activity. Exposure to chlorpyrifos did not produce signs of overt toxicity to the dams or developing offspring. Cholinesterase activities were inhibited in a dose-related manner, with brain cholin-esterase inhibition of about 26%, 32%, and 45% on postnatal day 1. Inhibition of brain cholineste-rase persisted in all treatment groups until postnatal day 6 and in the medium and high-dosage groups through postnatal day 9. Liver carboxylesterase activity was also inhibited in a dose-related manner, with a recovery profile parallel to that of brain cholinesterase. Choline acetyltransferase activity was decreased by about 13% in the high-dosage group on postnatal days 9 and 12. These results indicate that gestational exposure to chlorpyrifos results in relatively persistent inhibition of brain cholinesterase and a delayed depression of choline acetyltransferase at a time when brain cholinesterase activity had returned to control levels in the high-dosage group.

In Vivo Interaction between Chlorpyrifos and Parathion in Adult Rats: Sequence of Administration Can Markedly Influence Toxic Outcome

Organophosphorus insecticides (OPs) generally act through a common mechanism of toxicity initiated by inhibition of acetylcholinesterase (AChE). We studied the in vivo interactive toxicity of two common OPs, chlorpyrifos (CPF) and parathion (PS), in adult male rats. Dose–response studies estimated the acute oral LD1 values for the two OPs (CPF = 80 mg/kg po; PS = 4 mg/kg po) and these dosages or relative proportions were used to evaluate interactive toxicity. Three treatment strategies were evaluated: CPF followed by PS 4 h later (CPF-1st), PS followed by CPF 4 h later (PS-1st), and simultaneous (concurrent) exposures. Using LD1 dosages, rats in the CPF-1st and concurrent groups exhibited more cholinergic toxicity (i.e., salivation, lacrimation, urination, and diarrhea signs and involuntary movements) and higher lethality (7/8 and 6/8, respectively, beginning 1 h after PS) than those in the PS-1st group (2/8 lethality, beginning 3 days after CPF). Sequential exposures to lower dosages (CPF vs PS: 60 vs 3 mg/kg; 40 vs 2 mg/kg) led to more extensive neurotoxicity in the CPF-1st group compared to the other groups. Following lower dosages (40 vs 2 mg/kg), brain ChE inhibition was more extensive in the CPF-1st group at all time points (64–85%) and the concurrent group at 4 and 24 h after exposure (46–83%) compared to rats receiving PS first (7–48%). No differences were noted however, in plasma (71–93% inhibition) or liver (72–81%) cholinesterase activities nor were there group-related differences in plasma (50–60% inhibition) or liver (>85% inhibition) carboxylesterase activities. Incubation of liver samples with oxons in the presence or absence of calcium (i.e., 2 mM CaCl2 or EGTA) prior to addition of ChE (striatal sample) substantially blocked ChE inhibition by CPO (IC50: without liver = 4 nM; liver + calcium = 279 nM; liver + EGTA = 48 nM) but had lesser effects on PO-mediated inhibition (IC50: without liver = 17 nM; liver + EGTA = 56 nM; liver + calcium = 57 nM). Liver homogenate from animals preexposed to PS substantially decreased ChE inhibition by CPO when calcium was included (IC50: +EGTA = 8 nM; +calcium = 225 nM), but liver homogenate from animals preexposed to CPF was ineffective at blocking PO-induced inhibition (IC50: +EGTA = 16 nM; +calcium = 16 nM). We conclude that prior inhibition of carboxylesterase activity impacts toxicity of subsequent exposure to PS more than CPF because of more active detoxification of CPO by A-esterase. Together, these findings indicate that interactive toxicity from combined exposures to two OP insecticides can be markedly influenced by the sequence of administration.

Synthesis of new carboxylesterase inhibitors and evaluation of potency and water solubility.

Carboxylesterases are essential enzymes in the hydrolysis and detoxification of numerous pharmaceuticals and pesticides. They are vital in mediating organophosphate toxicity and in activating many prodrugs such as the chemotherapeutic agent CPT-11. It is therefore important to study the catalytic mechanism responsible for carboxylesterase-induced hydrolysis, which can be accomplished through the use of potent and selective inhibitors. Trifluoromethyl ketone (TFK)-containing compounds are the most potent esterase inhibitors described to date. The inclusion of a thioether moiety beta to the carbonyl further increased TFK inhibitor potency. In this study, we have synthesized the sulfone analogues of a series of aliphatic and aromatic substituted thioether TFKs to evaluate their potency and solubility properties. This structural change shifted the keto/hydrate equilibrium from <9% hydrate to >95% hydrate, forming almost exclusively the gem-diol. These new compounds were evaluated for their inhibition of carboxylesterase activity in three different systems, rat liver microsomes, commercial porcine esterase, and juvenile hormone esterase in cabbage looper (Trichoplusia ni) hemolymph. The most potent inhibitor of rat liver carboxylesterase activity was 1,1,1-trifluoro-3-(decane-1-sulfonyl)-propan-2,2-diol, which inhibited 50% of the enzyme activity (IC(50)) at 6.3 +/- 1.3 nM and was 18-fold more potent than its thioether analogue. However, the sulfone derivatives were consistently poorer inhibitors of porcine carboxylesterase activity and juvenile hormone esterase activity, with IC(50) values ranging from low micromolar to millimolar. The compound 1,1,1-trifluoro-3-(octane-1-sulfonyl)-propan-2,2-diol was shown to have a 10-fold greater water solubility than its thioether analogue, 1,1,1-trifluoro-3-octylsulfanyl-propan-2-one (OTFP). These novel compounds provide further evidence of the differences between esterase orthologs, suggesting that additional development of esterase inhibitors may ultimately provide a battery of ortholog and/or isoform selective inhibitors analogous to those available for other complex enzyme families with overlapping substrate specificity.

GLUCOSE FEEDING EXACERBATES PARATHION-INDUCED NEUROTOXICITY

Excessive dietary intake of sugars could alter various biotransformation processes and the pharmacological and toxicological properties of numerous xenobiotics. In the present study, the effects of glucose supplementation were examined on the neurotoxicity of the organophosphorus (OP) pesticide parathion (PS) and its active metabolite, paraoxon (PO), a potent inhibitor of acetylcholinesterase (AChE). Rats (n = 6-12/treatment group) were given free access to tap water or 15% glucose (w/v) in tap water beginning 7 d prior to OP toxicant exposure. Food, caloric intake, and body weight were measured daily. Animals were challenged with either PS (4.5, 9, or 18 mg/kg, sc) or PO (0.3, 0.5, or 0.7 mg/kg, sc) and clinical signs of neurotoxicity (i.e., autonomic dysfunction, involuntary movements) were recorded daily for the following 13 d. Glucose feeding was associated with a dramatic drop (~50%) in feed intake and an increase (~20%) in total caloric consumption over the 7 d prior to OP exposure. Functional toxicity associated with PS exposure was increased in glucose-fed (GF) rats, but the glucose diet had no apparent effect on clinical signs of toxicity following PO treatment. Glucose feeding increased the magnitude of AChE inhibition in the frontal cortex and plasma at lower dosages (i.e., 4.5 and 9 mg/kg) 3 d following PS treatment. Time-course studies (3, 7, and 11 d after PS exposure, 18 mg/kg, sc) indicated significantly greater brain and plasma AChE inhibition in glucosefed animals at later time points. In contrast, glucose feeding had no effect on the degree of AChE inhibition following PO exposure. Neither liver microsomal oxidative desulfuration of PS, nor liver or plasma paraoxonase, nor liver or plasma carboxylesterase activities were measurably affected by glucose feeding. Downregulation of muscarinic receptors 7 d after PS exposure (18 mg/kg, sc) was more extensive in GF rats. It is postulated that excessive glucose consumption decreases the intake of other dietary components, in particular amino acids, limiting the de novo synthesis of AChE and consequent recovery of synaptic transmission. Due to the shorter duration of inhibition following PO exposure, spontaneous reactivation of AChE may be more important than de novo protein synthesis in recovery of function, and thus with the effects of glucose feeding on its toxicity. Individuals that derive a large proportion of their calories from sugars may be at higher risk of acute toxicity from organophosphorus pesticides such as PS.

Age- and gender-related differences in sensitivity to chlorpyrifos in the rat reflect developmental profiles of esterase activities.

Young rats are more sensitive than adults to a single oral dose of chlorpyrifos, an organophosphorus pesticide. A direct comparison of chlorpyrifos effects in young (postnatal day 17; PND17), adolescent (PND27), and adult (70 days) Long-Evans rats was conducted to determine quantitative and possibly qualitative differences in sensitivity in terms of behavioral changes and cholinesterase (ChE; total cholinesterase activity) inhibition at these three ages. Male and female rats were administered chlorpyrifos orally at one of two doses (PND17, 5 or 20 mg/kg; PND27, 20 or 50 mg/kg; adult, 20 or 80 mg/kg) and tested at either 3.5 or 6.5 h after dosing. Behavioral testing included observational evaluations and measurements of motor activity and was followed immediately by tissue collection for ChE determination in brain and blood. For both behavioral changes and ChE inhibition, peak effects occurred at 3.5 h in adult male and PND27 rats (both sexes) and at 6.5 h in adult female and PND17 rats (both sexes). Comparisons of the 20 mg/kg dose across ages showed generally less ChE inhibition and fewer behavioral effects with increasing age, except that the adult females were similar to the PND27 rats. The high dose used for each age group produced similar brain ChE inhibition (80-90%) and generally similar behavioral effects. Interestingly, a few end-points in the young rats were less affected than in adults at this level of ChE inhibition. The degree of ChE inhibition in the brain more closely paralleled the blood inhibition in the younger rats, compared to the adults. Carboxylesterase (CaE) and A-esterase are known to play an important role in the detoxification of organophosphates and may be partially responsible for these sensitivity differences. Liver and plasma CaE and A-esterase activities were measured in untreated male rats on PND1, 4, 7, 12, 17, and 21 and in adults of both sexes (82-92 days old). Preweanling rats had considerably less activity of both enzymes, and adult females had less liver CaE activity than males. These differences in detoxifying enzymes correlate with the age-related differences in behavioral and biochemical effects, as well as the gender differences seen in adult rats, and thus may be a major influence on the differential sensitivity to chlorpyrifos.

Use of biochemical biomarkers as a screening tool to focus the chemical monitoring of organic pollutants in the Biobio river basin (Chile)

Sediment and water from the Biobio river basin (Central Chile) were used in a simulated field-exposure experiment with juvenile rainbow trout. After two weeks of exposure, brain acetylcholinesterase (ACNE), liver carboxylesterase (CbE) and cytochrome P4501A1 (CYP1A1) activities were measured. Esterase activities did not show significant variations between trout exposed to sediment and water. Sediment was found to contain pollutants that induced CYP1A1 catalytic activity. Chemical analysis of these inducers revealed that PAHs were the main contaminants (mean content of 5,818 ng g-' d.w.) causing measurable effects in biota. This study shows that from an ecotoxicological point of view, it is useful to test certain biochemical biomarkers before monitoring chemicals in the aquatic environment.

Subchronic Toxicity Studies of Sucrose Acetate Isobutyrate (SAIB) in the Ratand Dog

Preliminary short-term toxicity studies of sucrose acetate isobutyrate (SAIB) in the dog demonstrated that addition of this additive to the diet was associated with an increase in liver size and elevated serum alkaline phosphatase activity with no evidence of pathological change by light microscopy. To determine the basis for these changes, a 12-week oral toxicity study of SAIB was conducted in the dog and a similar study was performed in the rat. SAIB was fed in the diet to groups of six beagle dogs of each sex at 0, 0.5, 1.0, 2.0 and 4.0%. SAIB was also fed to groups of 40 Sprague--Dawley rats of each sex at levels of 0, 2.5, 5.0 and 10.0%. In the rat study, in addition to routine toxicology parameters, hepatic microsomal enzyme induction was determined using a zoxazolamine hypnotic test, urinary ascorbic acid excretion and determination of hepatic carboxylesterase activity. Sodium phenobarbital was fed to groups of 20 rats of each sex at a dose of 100mg/kg body weight/day by gavage as a positive control for hepatic microsomal enzyme induction. In the dog study, routine toxicological tests were supplemented by tests for bromsulfophthalein (BSP) retention, histochemical staining of liver sections for glycogen, phosphorylase, succinate dehydrogenase, and acid and alkaline phosphatases. Levels of liver lipid, protein, glycogen and carboxylesterase activity were also determined. Electron microscopic examinations were made on liver sections from the dog study at the end of the 12-week SAIB feeding period and after a 2-week withdrawal period. Administration of SAIB to rats did not reveal evidence of any effect on hepatobiliary function, and there was no indication of microsomal enzyme induction. Body weight gain of male rats fed SAIB was decreased, probably as the result of decreased palatability of the diet; SAIB did not affect body weight gain in females. The changes observed in the dogs fed SAIB included increased serum alkaline phosphatase activity with no change in serum alanine aminotransferase, aspartate aminotransferase or lactic dehydrogenase activity and no change in serum electrolyte, serum protein, glucose or bilirubin levels. No haematological changes were observed. BSP retention was observed at all SAIB dose levels. There were no SAIB-related pathological changes in any organ when examined by light microscopy. Examination by electron microscope revealed dilatation of bile canaliculi and an increase in smooth endoplasmic reticulum compared with controls. Histochemical studies also indicated increased enzyme activity of the bile canaliculi. The electron-mocroscope-revealed changes were completely reversed during a 2-week treatment withdrawal period. The dog study did not establish a no-effect level for changes in hepatobiliary function induced by feeding SAIB.

Differences between genetic stocks of chickens in response to acute and delayed effects of an organophosphorus compound

The influence of genotypes of the major histocompatibility complex (MHC) on susceptibility to acute and delayed effects of an organophosphorus ester was measured in adult White Leghorn chickens from lines differing in response to sheep red blood cell (SRBC) antigen. Chickens from lines selected for high (HA) or low (LA) antibody response to SRBC and homozygous for B13B13 or B21B21 genotypes at the MHC were administered a single subcutaneous injection of diisopropyl phosphorofluoridate (DFP) at dosages of 0, 0.25, 0.50, or 1.0 mg/kg body weight using corn oil as the carrier. Criteria for toxicological responses included clinical, biochemical, and pathological measures. Clinical signs of acute cholinergic poisoning and delayed neuropathy were dose related. Brain and blood cholinesterase and carboxylesterase activities were more sensitive to inhibition by DFP than were liver cholinesterase and carboxylesterase activities. Cholinergic signs 3 h after administration of DFP were more pronounced in line HA than in line LA chickens. Pathological evidence of delayed neuropathy 2 wk after DFP administration was also more evident in HA than LA chickens. Although less pronounced than that for lines, differences in neurotoxic manifestations following DFP administration were greater for chickens of B21B21 than B13B13 genotypes. Activity of A-esterases, which hydrolyze organophosphorus esters without being inhibited by them, was lower in plasma of line HA than line LA chickens. Differences among the genotypes in activity of other esterases were not found in chickens not receiving DFP. These results indicated that responses of chickens to the neurotoxicant DFP were influenced by the background genome of the chickens.

Survivors of soman poisoning: recovery of the soman LD50 to control value in the presence of extensive acetylcholinesterase inhibition.

Initially, mice were pretreated with atropine (17.4 mg/kg; IP) and the oxime reactivator HI-6 (50 mg/kg; IP) 5 min prior to an injection of soman (287 micrograms/kg, SC); approximately 2.1 x LD50 dose). More than 95% of the mice survived this dose of soman with atropine and HI-6 pretreatment. In these survivors of soman poisoning the return of the soman LD50 value to control value (124 micrograms/kg, SC) was determined at various times after the initial soman exposure. Mice which survived exposure to a lethal dose of soman by pretreatment with atropine and HI-6 were sensitized to the lethal effects of soman upon reexposure. The SC soman LD50 at 4 h, after surviving the initial soman exposure, was 20 micrograms/kg. The normal soman LD50 (as evidenced by a LD50 value which was not significantly different from the control value) returned within 4 days, at which time there was still extensive acetylcholinesterase inhibition in all brain regions (striatum, pons-medulla, cerebellum, hypothalamus, hippocampus), diaphragm and erythrocytes. Serum carboxylesterase recovered to control levels within 48 h, whereas liver carboxylesterase activity was not inhibited following the initial soman exposure. The results demonstrate that there is an excess of acetylcholinesterase which is required for normal response in the toxicological sense.

Alteration of hepatic carboxylesterase activity by soman: inhibition in vitro and enhancement in vivo.

1. Hydrolysis of the drug esters procaine, chloramphenicol succinate, and prednisolone succinate was studied. Addition of soman to guinea pig liver microsomes caused a dose-dependent inhibition of hydrolysis of all three substrates; at the highest soman concentration (1 microM), ester hydrolysis was totally abolished. 2. Ester hydrolysis was also measured in liver microsomes from guinea pigs pretreated with soman at a low dose (10% of LD50) or at a high dose (90% of LD50) either 1 h or 12 h before killing. Plasma-cholinesterase activity was decreased in all pretreated animals. Liver carboxylesterase activity, measured with the three drug substrates and by hydrolysis of 4-nitrophenyl acetate was increased by all pretreatments. 3. This enhancing effect varies with the substrate and increases with dose of soman. The 12 h pretreatment produced a greater increase in activity than did the 1 h pretreatment. 4. These studies indicate that soman is a potent inhibitor of carboxylesterase activity in vitro but increases the activity of the liver enzyme when administered in vivo.

Effects of multiple oral doses of two carbamate insecticides on esterase levels in young and adult chickens

Young chickens were administered oral doses of either aldicarb (0.2 mg/kg body wt/day) or carbaryl (100 mg/kg body wt/day) for 7 days as this regimen had been demonstrated, in previous studies, to alter locomotor activities. In addition to histological examination, activities of brain acetylcholinesterase (AChE) and neurotoxic esterase (NTE), liver and plasma cholinesterase (ChE), and carboxylesterase were measured at different intervals after dosing to determine whether these parameters could be used to indicate, predict, or monitor changes in locomotor activity. Effects on enzyme activities following administration of these carbamates were compared in young and adult chickens. Activities of brain AChE, plasma ChE, plasma carboxylesterase, and liver ChE were inhibited in young chicks by both carbaryl and aldicarb, with inhibitions greater after carbaryl treatments. Enzyme activities were not, however, inhibited in adult chickens. Carbamate treatment did not cause histological damage nor did it inhibit activities of NTE and liver carboxylesterase activities either in young or adult chickens. In this study, esterase determinations and histological studies could not be used to predict or support carbamate-induced functional deficits.