Comparing Longitudinal Measures of Cholinesterase as Biomarkers for Insecticide Exposure Among Latinx Children in Rural Farmworker and Urban Nonfarmworker Communities in North Carolina.

OBJECTIVE: In a 2-group prospective design, this study compared seasonal cholinesterase levels of Latinx children in rural farmworker families and comparable urban children to assess the impact of environmental exposure to cholinesterase-inhibiting insecticides. METHODS: Quarterly blood samples and passive dosimeter wristbands were collected over 2 years in 8-year-old children (74 rural, 62 urban). Laboratory analysis assessed total cholinesterase, acetylcholinesterase, and butyrylcholinesterase from blood samples, and insecticides from wristbands. RESULTS: In spring and summer, total cholinesterase and acetylcholinesterase levels were depressed in rural children compared with winter and fall. Butyrylcholinesterase was depressed in rural children in fall compared with spring and summer. Adjustment for insecticide exposure did not affect these associations. CONCLUSIONS: Environmental exposures to cholinesterase-inhibiting insecticides have measurable biochemical effects on blood cholinesterases in rural children from farmworker families.

Cholinesterases and the fine line between poison and remedy.

Acetylcholinesterase (AChE, EC 3.1.1.7) and butyrylcholinesterase (BChE, EC 3.1.1.8) are related enzymes found across the animal kingdom. The critical role of acetylcholinesterase in neurotransmission has been known for almost a century, but a physiological role for butyrylcholinesterase is just now emerging. The cholinesterases have been deliberately targeted for both therapy and toxicity, with cholinesterase inhibitors being used in the clinic for a variety of disorders and conversely for their toxic potential as pesticides and chemical weapons. Non-catalytic functions of the cholinesterases (ChEs) participate in both neurodevelopment and disease. Manipulating either the catalytic activities or the structure of these enzymes can potentially shift the balance between beneficial and adverse effect in a wide number of physiological processes.

The impacts of pesticide and nicotine exposures on functional brain networks in Latino immigrant workers.

Latino immigrants that work on farms experience chronic exposures to potential neurotoxicants, such as pesticides, as part of their work. For tobacco farmworkers there is the additional risk of exposure to moderate to high doses of nicotine. Pesticide and nicotine exposures have been associated with neurological changes in the brain. Long-term exposure to cholinesterase-inhibiting pesticides, such as organophosphates and carbamates, and nicotine place this vulnerable population at risk for developing neurological dysfunction. In this study we examined whole-brain connectivity patterns and brain network properties of Latino immigrant workers. Comparisons were made between farmworkers and non-farmworkers using resting-state functional magnetic resonance imaging data and a mixed-effects modeling framework. We also evaluated how measures of pesticide and nicotine exposures contributed to the findings. Our results indicate that despite having the same functional connectivity density and strength, brain networks in farmworkers had more clustered and modular structures when compared to non-farmworkers. Our findings suggest increased functional specificity and decreased functional integration in farmworkers when compared to non-farmworkers. Cholinesterase activity was associated with population differences in community structure and the strength of brain network functional connections. Urinary cotinine, a marker of nicotine exposure, was associated with the differences in network community structure. Brain network differences between farmworkers and non-farmworkers, as well as pesticide and nicotine exposure effects on brain functional connections in this study, may illuminate underlying mechanisms that cause neurological implications in later life.

Brain Anatomy in Latino Farmworkers Exposed to Pesticides and Nicotine.

OBJECTIVE: Migrant tobacco farmworkers experience regular occupational exposure to pesticides and nicotine. The present study was designed to determine whether there are differences in brain anatomy between Latino farmworkers and non-farmworkers. METHODS: Magnetic resonance brain images were compared between farmworkers and non-farmworkers. In addition, blood cholinesterase activity and urinary cotinine levels were also used to identify associations with pesticide and nicotine exposure. RESULTS: Farmworkers had greater gray matter signal in putamen and cerebellum, and lower gray matter signal in frontal and temporal lobes. Urinary cotinine was associated with the observed differences in brain anatomy, but blood cholinesterase activity was not. CONCLUSIONS: Nicotine exposure was associated with neuroanatomical differences between Latino farmworkers and non-farmworkers. Future studies are needed to differentiate iron deposition from brain atrophy and to further assess the potential role of nicotine and pesticide exposure.

Longitudinal Assessment of Blood Cholinesterase Activities Over 2 Consecutive Years Among Latino Nonfarmworkers and Pesticide-Exposed Farmworkers in North Carolina.

OBJECTIVE: This study (1) describes patterns of whole blood total cholinesterase, acetylcholinesterase, and butyrylcholinesterase activities across the agricultural season, comparing farmworkers and nonfarmworkers; and (2) explores differences between farmworkers' and non-farmworkers' likelihood of cholinesterase depression. METHODS: Blood samples from 210 Latino male farmworkers and 163 Latino workers with no occupational pesticide exposure collected 8 times across 2 agricultural seasons were analyzed. Mean cholinesterase activity levels and depressions 15% or more were compared by month. RESULTS: Farmworkers had significantly lower total cholinesterase and butyrylcholinesterase activities in July and August and lower acetylcholinesterase activity in August. Farmworkers had significantly greater likelihood of cholinesterase depression for each cholinesterase measure across the agricultural season. SIGNIFICANCE: A repeated-measures design across 2 years with a nonexposed control group demonstrated anticholinesterase effects in farmworkers. Current regulations designed to prevent pesticide exposure are not effective.

Behavioral sequelae following acute diisopropylfluorophosphate intoxication in rats: comparative effects of atropine and cannabinomimetics.

The comparative effects of atropine and the indirect cannabinomimetics URB597 (a fatty acid amide hydrolase inhibitor) and URB602 (a monoacylglycerol lipase inhibitor) on functional and neurobehavioral endpoints following acute diisopropylfluorophosphate intoxication were studied. Male Sprague-Dawley rats were treated with vehicle or DFP (2.5mg/kg, sc), immediately post-treated with either vehicle, atropine (16mg/kg), URB597 (3mg/kg), URB602 (10mg/kg) or a combination of URB597 and URB602, and functional signs of toxicity as well as nocturnal motor activity were measured daily for seven consecutive days. Performance in the elevated plus maze (for anxiety-like behavior) and the forced swimming test (for depression-like behavior) was measured at days 6-8 and 27-29 after dosing. Twenty-four hours after dosing, DFP markedly reduced cholinesterase activity in selected brain regions and peripheral tissues (diaphragm and plasma). Substantial recovery of cholinesterase activity was noted at both 8 and 29days after dosing but significant inhibition was still noted in some brain regions at the latest time-point. DFP elicited body weight reductions and typical signs of cholinergic toxicity, and reduced nocturnal ambulation and rearing. Atropine and the cannabinomimetics (alone and in combination) partially attenuated DFP-induced functional signs of toxicity. None of the post-treatments reversed the DFP-induced reduction in ambulation or rearing, however. No significant treatment-related effects on elevated plus maze performance were noted. DFP-treated rats exhibited decreased swimming and increased immobility in the forced swimming test at both time-points. None of the post-treatments had any effect on DFP-induced changes in immobility or swimming at day 8. At day 29, atropine and the combination of URB597/URB602 significantly blocked DFP-induced changes in immobility, while URB597 and the combination reversed DFP-induced changes in swimming. The results suggest that early blockade of muscarinic receptors and enhancement of eCB signaling can attenuate both acute and delayed effects elicited by DFP.

Effects of chlorpyrifos oxon on M2 muscarinic receptor internalization in different cell types.

The muscarinic M2 receptor is a member of the G protein-coupled receptor (GPCR) superfamily. Agonist activation of GPCR leads to their phosphorylation, desensitization, internalization, and subsequent endocytic recycling or lysosomal degradation. Agonist-induced phosphorylation of M2 receptors is mediated by G-protein receptor kinase 2 (GRK2). The active metabolite of the organophosphorus insecticide chlorpyrifos, i.e., chlorpyrifos oxon (CPO), inhibited agonist-induced phosphorylation of human recombinant M2 receptors by GRK2 in vitro in a concentration-dependent manner. In both intact HEL 299 cells (human embryonic lung fibroblasts expressing M2 receptors) and CHO-M2 cells (stably expressing M2 receptors), the muscarinic agonist carbachol (100 microM) led to receptor internalization as determined by reduced specific binding to the membrane-impermeable radioligand [(3)H]-N-methylscopolamine (NMS). CPO alone (100 microM) exerted no significant effect on NMS binding in either HEL 299 or CHO-M2 cells. In HEL 299 cells, CPO did not influence carbachol-induced internalization, whereas in CHO-M2 cells CPO blocked internalization. In primary striatal neurons, M2 receptors appeared widely and diffusely distributed. Exposure to either carbachol or CPO led to apparent receptor internalization with an increased percent of cells exhibiting punctate domains of immunostaining, while combined exposure to both carbachol and CPO led to a significantly higher percent of cells exhibiting this appearance. The data suggest that CPO may differentially influence agonist-stimulated M2 receptor internalization in a cell-dependent manner.

In vitro sensitivity of cholinesterases and [3H]oxotremorine-M binding in heart and brain of adult and aging rats to organophosphorus anticholinesterases.

Organophosphorus (OP) insecticides elicit toxicity via acetylcholinesterase inhibition, allowing acetylcholine accumulation and excessive stimulation of cholinergic receptors. Some OP insecticides bind to additional macromolecules including butyrylcholinesterase and cholinergic receptors. While neurotoxicity from OP anticholinesterases has been extensively studied, effects on cardiac function have received less attention. We compared the in vitro sensitivity of acetylcholinesterase, butyrylcholinesterase and [(3)H]oxotremorine-M binding to muscarinic receptors in the cortex and heart of adult (3 months) and aging (18 months) rats to chlorpyrifos, methyl parathion and their active metabolites chlorpyrifos oxon and methyl paraoxon. Using selective inhibitors, the great majority of cholinesterase in brain was defined as acetylcholinesterase, while butyrylcholinesterase was the major cholinesterase in heart, regardless of age. In the heart, butyrylcholinesterase was markedly more sensitive than acetylcholinesterase to inhibition by chlorpyrifos oxon, and butyrylcholinesterase in tissues from aging rats was more sensitive than enzyme from adults, possibly due to differences in A-esterase mediated detoxification. Relatively similar differences were noted in brain. In contrast, acetylcholinesterase was more sensitive than butyrylcholinesterase to methyl paraoxon in both heart and brain, but no age-related differences were noted. Both oxons displaced [(3)H]oxotremorine-M binding in heart and brain of both age groups in a concentration-dependent manner. Chlorpyrifos had no effect but methyl parathion was a potent displacer of binding in heart and brain of both age groups. Such OP and age-related differences in interactions with cholinergic macromolecules may be important because of potential for environmental exposures to insecticides as well as the use of anticholinesterases in age-related neurological disorders.

Selective inhibition of butyrylcholinesterase in vivo in horses by the feed-through larvacide Equitrol.

The organophosphate insecticide tetrachlorvinphos (TCVP, Rabon) is the active ingredient in "feed-through" larvacides (e.g., Equitrol) for fly control around horse stables. As with other organophosphates, TCVP elicits toxicity by inhibiting acetylcholinesterase, leading to accumulation of the neurotransmitter acetylcholine and cholinergic signs. Relatively little is known, however, on the effects of TCVP-containing larvacides on acetylcholinesterase or other esterases in horses. Previous in vitro studies indicated that horse plasma cholinesterase activity was substantially (>10,000-fold) more sensitive than erythrocyte cholinesterase activity to inhibition by TCVP. In the current study, we examined the relative proportion of acetylcholinesterase and butyrylcholinesterase activities in horse plasma and muscle, and evaluated the in vivo effects of Equitrol on target and non-target esterases following oral feeding in horses. In vitro inhibition studies suggested that essentially all cholinesterase activity in horse plasma was butyrylcholinesterase, while muscle contained >90% acetylcholinesterase activity. For in vivo studies, adult, male horses (364-590kg; n=3/treatment group) were given either sweet feed alone or sweet feed supplemented with Equitrol daily for 21 consecutive days at the recommended rate. Clinical signs (vital signs, abdominal auscultation, ophthalmic exam, body temperature) were recorded on a daily basis. Heparinized blood samples were taken at days -1, 1, 3, 7, 21, 28, and 42 while muscle (semimembranosus) biopsies were taken under aseptic conditions on days -1 and 21. No signs of overt toxicity were noted at any time during the study. Plasma cholinesterase activity was significantly inhibited (33%) in larvacide-treated horses as early as one day after treatment and peak inhibition (69-71%) was noted at days 7 and 21. Following cessation of dosing, plasma cholinesterase activity recovered (46% and 83% of control on days 28 and 42, respectively). Neither erythrocyte cholinesterase activity nor plasma carboxylesterase activity was affected by larvacide treatment in vivo. Muscle cholinesterase activity was highly variable among individual horses (pre-treatment range: 0.50-4.92nmole/min/mg protein), but there was no suggestion of a treatment-related reduction in muscle cholinesterase activity. These in vivo results confirm our previous in vitro studies indicating marked differential sensitivity of horse plasma and erythrocyte cholinesterase to inhibition by TCVP. Furthermore, the results suggest that recommended dosing levels of the TCVP-containing larvacide in horses are unlikely to affect acetylcholinesterase activities or disrupt cholinergic neurotransmission in target tissues.

Comparative effects of oral chlorpyrifos exposure on cholinesterase activity and muscarinic receptor binding in neonatal and adult rat heart.

Organophosphorus (OP) pesticides elicit acute toxicity by inhibiting acetylcholinesterase (AChE), the enzyme responsible for inactivating acetylcholine (ACh) at cholinergic synapses. A number of OP toxicants have also been reported to interact directly with muscarinic receptors, in particular the M(2) muscarinic subtype. Parasympathetic innervation to the heart primarily regulates cardiac function by activating M(2) receptors in the sinus node, atrial-ventricular node and conducting tissues. Thus, OP insecticides can potentially influence cardiac function in a receptor-mediated manner indirectly by inhibiting acetylcholinesterase and directly by binding to muscarinic M(2) receptors. Young animals are generally more sensitive than adults to the acute toxicity of OP insecticides and age-related differences in potency of direct binding to muscarinic receptors by some OP toxicants have been reported. We thus compared the effects of the common OP insecticide chlorpyrifos (CPF) on functional signs of toxicity and cardiac cholinesterase (ChE) activity and muscarinic receptor binding in neonatal and adult rats. Dosages were based on acute lethality (i.e., 0.5 and 1x LD(10): neonates, 7.5 and 15 mg/kg; adults, 68 and 136 mg/kg). Dose- and time-related changes in body weight and cholinergic signs of toxicity (involuntary movements) were noted in both age groups. With 1x LD(10), relatively similar maximal reductions in ChE activity (95%) and muscarinic receptor binding (approximately 30%) were noted, but receptor binding reductions appeared earlier in adults and were more prolonged in neonates. In vitro inhibition studies indicated that ChE in neonatal tissues was markedly more sensitive to inhibition by the active metabolite of chlorpyrifos (i.e., chlorpyrifos oxon, CPO) than enzyme in adult tissues (IC(50) values: neonates, 17 nM; adults, 200 nM). Chelation of free calcium with EDTA had relatively little effect on in vitro cholinesterase inhibition, suggesting that differential A-esterase activity was not responsible for the age-related difference in cholinesterase sensitivity between age groups. Pre-incubation of neonatal and adult tissues with selective inhibitors of AChE and butyrylcholinesterase (BChE) indicated that a majority (82-90%) of ChE activity in the heart of both neonates and adults was BChE. The rapid onset (by 4h after dosing) of changes in muscarinic receptor binding in adult heart may be a reflection of the more potent direct binding to muscarinic receptors by chlorpyrifos oxon previously reported in adult tissues. The results suggest that ChE activity (primarily BChE) in neonatal heart may be inherently more sensitive to inhibition by some anticholinesterases and that toxicologically significant binding to muscarinic receptors may be possible with acute chlorpyrifos intoxication, potentially contributing to age-related differences in sensitivity.

Effects of combined, multiple stressors on pyridostigmine-induced acute toxicity in rats.

A number of studies have evaluated the possibility that stress-induced changes in blood-brain barrier permeability enhanced the central effects of the carbamate acetylcholinesterase inhibitor, pyridostigmine. We previously found relatively little evidence of stress-induced changes in the acute toxicity of pyridostigmine in rats using a variety of restraint, forced running and forced swimming stress conditions. In this study, we evaluated the effects of sequential pre-exposure to multiple stressors on the acute toxicity of pyridostigmine. Rats (n = 8 per treatment group) were either un-stressed or stressed by restraint (60 min), forced running (60 min, 15 m/min, 6 degrees incline) and forced swimming (15 min), and then given either vehicle (saline, 1 ml/kg, po) or pyridostigmine (30 mg/kg, po) immediately after the final stressor. Functional signs of cholinergic toxicity (involuntary movements, autonomic dysfunction) were recorded at 0.5, 1 and 2 h after dosing. Body temperature was measured both before stress and 2 h after dosing. Rats were sacrificed immediately after 2-h functional observations to collect tissues (whole blood, diaphragm, frontal cortex, hippocampus and cerebellum) for measurement of cholinesterase activity. Stressed rats treated with pyridostigmine exhibited higher lethality (2/8) compared to unstressed rats given pyridostigmine (0/8). Pyridostigmine elicited classical signs of cholinergic toxicity, but the rats that died did not show increased cholinergic signs and no significant differences in cholinergic signs were noted between treatment groups. Cholinesterase activity was significantly inhibited in blood (47-50%) and diaphragm (80%) following pyridostigmine exposure regardless of stress conditions. Slight but significant inhibition (11-15%) of cerebellar cholinesterase activity was observed following pyridostigmine exposure, but inhibition was not influenced by stress. We conclude that while acute lethality from pyridostigmine may be increased by combined, multiple stressors, increased lethality does not appear due to enhanced cholinergic toxicity or via increased cholinesterase inhibition in either central or peripheral tissues.

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 microg) 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 degrees C) with chlorpyrifos oxon to evaluate in vitro sensitivity. Based on 95% confidence intervals, no significant differences in IC50 values were obtained in 3-month to 36-year samples (range: 1.42-2.12 nM), while the IC50 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.

Stress regulation of sulfotransferases in male rat liver.

Sulfotransferase (SULT) catalyzed sulfation is responsible for hormone regulation and xenobiotic detoxification. Induction of SULTs by various hormones has been reported. Stress regulation of SULTs has not been reported, however. Here we report that rat liver SULTs can be regulated by physical stress (forced running, EX) and chemical stress (the organophosphorus pesticide parathion, PS). Both EX and PS increased rat liver phenol-sulfating SULT1A1 and hydroxysteroid-sulfating SULT2A1 activities. The increase in SULT1A1 activity did not correlate with protein (Western blot) or mRNA (RT-PCR) results but correlated well with increased non-protein soluble thiols. This suggests a possible Cys modification mechanism for stress regulation of SULT1A1. In vitro studies on GSH/GSSG effects on SULT1A1 activity support this conclusion. In contrast, SULT2A1 activity following physical or chemical stress treatments correlated well with protein and mRNA levels. This suggests a stress regulation mechanism of SULT2A1 at the gene transcription level, possibly occurring via hormones.

Effects of daily stress or repeated paraoxon exposures on subacute pyridostigmine toxicity in rats.

Pyridostigmine (PYR) is a carbamate cholinesterase (ChE) inhibitor used during the Persian Gulf War as a pretreatment against possible chemical nerve agent attack. Because of its quaternary structure, PYR entry into the central nervous system is limited by the blood-brain barrier (BBB). Following reports of unexplained illnesses among Gulf War veterans, however, central nervous system effects of PYR have been postulated through either stress-induced alteration of BBB permeability or via interactions with other neurotoxic agents. We evaluated the effects of daily physical (treadmill running) stress or daily exposure to a subclinical dosage of the organophosphate ChE inhibitor paraoxon (PO) on ChE inhibition in blood, diaphragm and selected brain regions in young adult male Sprague-Dawley rats following subacute PYR exposures. In physical stress studies, rats were placed on a treadmill for 90 min each day for 14 days just prior to PYR (0, 3, or 10 mg/kg per day) administration. In PO-PYR interaction studies, rats were treated with PO (0, 0.05, or 0.1 mg/kg per day) 1 h prior to daily PYR (0 or 3 mg/kg per day) administration for 14 consecutive days. Rats were evaluated daily for signs of cholinergic toxicity and were killed 1 h after the final PYR treatment. Forced running increased plasma corticosterone levels throughout the experiment (on days 1, 3, 7 and 14) when measured immediately after termination of stress. PYR-treated rats in the high dosage (10 mg/kg per day) group exhibited slight signs of toxicity (involuntary movements) for the first 6 days, after which tolerance developed. Interestingly, signs of cholinergic toxicity following PYR were slightly but significantly increased in rats forced to run on the treadmill prior to dosing. ChE activities in whole blood and diaphragm were significantly reduced 1 h after the final PYR challenge, and ChE inhibition in diaphragm was significantly greater in stressed rats than in non-stressed controls following high dose PYR (10 mg/kg per day). No significant effects of treadmill running on PYR-induced ChE inhibition in brain regions were noted, however. Repeated subclinical PO exposure had no apparent effect on functional signs of PYR toxicity. As with repeated treadmill running, whole blood and diaphragm ChE activities were significantly reduced 1 h after the final PYR administration, and ChE inhibition was significantly greater with combined PO and PYR exposures. Brain regional ChE activity was significantly inhibited after daily PO exposure, but no increased inhibition was noted following combined PO and PYR dosing. We conclude that, while some stressors may under some conditions affect functional signs of toxicity following repeated pyridostigmine exposures, these changes are likely to occur via alteration of peripheral cholinergic mechanisms and not through enhanced entry of pyridostigmine into the brain.

Combined forced running stress and subclinical paraoxon exposure have little effect on pyridostigmine-induced acute toxicity in rats.

Pyridostigmine is a short-acting inhibitor of cholinesterase (ChE) used as a pretreatment against potential nerve agent exposure during the Persian Gulf War. As pyridostigmine contains a quaternary ammonium group, it is generally believed to elicit changes in the peripheral nervous system function only. It has been hypothesized, however, that the neurotoxicity of pyridostigmine may be altered by either stress or combined exposures to other toxicants. We evaluated the effects of forced running stress, exposure to the organophosphate anticholinesterase paraoxon, or a combination of both on the acute neurotoxicity of pyridostigmine. ChE (blood, diaphragm, and selected brain regions) and carboxylesterase (CE; liver, plasma) inhibition was also evaluated. Young adult male Sprague-Dawley rats were either given vehicle or paraoxon (0.1 mg/kg, i.m.) and subsets placed in their home cage or forced to run on a treadmill for 60 min. Pyridostigmine (0, 10 or 30 mg/kg, p.o.) was given 60 min after paraoxon dosing and rats were evaluated for cholinergic toxicity just prior to sacrifice 60 min later. No signs of toxicity were noted following paraoxon exposure while both dosages of pyridostigmine (10 and 30 mg/kg, p.o.) elicited signs of functional toxicity. Toxicity was not different with combined paraoxon-pyridostigmine exposures and forced running did not influence toxicity under any conditions. Paraoxon (0.1 mg/kg, i.m.) caused moderate (23-46%) ChE inhibition in blood, diaphragm and brain 2 h after exposure. Pyridostigmine (10 or 30 mg/kg, p.o.) caused extensive inhibition of blood (88-94%) and diaphragm (75-85%) ChE activity but no significant effect on brain regional ChE activity. Forced running stress did not influence the degree of tissue ChE inhibition following either paraoxon, pyridostigmine or paraoxon-pyridostigmine combined exposures. CE activities were inhibited (26-43%) in plasma and liver by paraoxon but inhibition was not influenced by either stress or combined paraoxon-pyridostigmine exposures. These results suggest that subclinical paraoxon exposure and forced running stress, by themselves or in combination, have little effect on acute pyridostigmine toxicity in rats.

Nicotinic autoreceptor function in rat brain during maturation and aging: possible differential sensitivity to organophosphorus anticholinesterases.

Acetylcholine (ACh) release is modulated pre-synaptically by both muscarinic and nicotinic receptor-mediated processes. While muscarinic autoreceptors inhibit ACh release, nicotinic autoreceptors enhance ACh release and thus disruption of these processes could potentially affect cholinergic toxicity following exposure to anticholinesterases. Marked age-related differences in sensitivity to some organophosphorus (OP) anticholinesterases have been reported. We compared nicotinic autoreceptor function (NAF) during maturation and aging and evaluated its potential modulation by the common OP insecticide, chlorpyrifos (CPF). Cortical synaptosomes were pre-loaded with [3H]choline, superfused (0.6 ml/min) with physiological buffer and [3H]ACh release was evoked with potassium (KCl, 9 mM), with or without co-addition of exogenous ACh to stimulate nicotinic autoreceptors. Fractions of perfusate were subsequently collected and area under the curve (AUC) for [3H] was analyzed by scintillation counting. The difference in evoked release due to co-addition of exogenous ACh was defined as NAF. Under these conditions, atropine (ATR, 0.1 microM) appeared requisite for NAF; thus this muscarinic antagonist was subsequently added to all perfusion buffers. In synaptosomes from adult tissues, exogenous ACh (3-100 microM) significantly increased release in a concentration-dependent manner. The nicotinic antagonist mecamylamine (MEC, 100 microM) substantially reduced the potassium-evoked release elicited by co-addition of ACh (10 microM). Interestingly, the nicotinic agonists nicotine (NIC) and dimethylphenylpiperazinium (DMPP; 0.1-10 microM) had no effect on release. The active metabolite of CPF (i.e. chlorpyrifos oxon (CPO), 1-10 microM) inhibited NAF in vitro. Maturation-related expression of NAF was noted (AUC with co-addition of 10 microM ACh: 7-day rats, 7+/-6; 21-day rats, 44+/-6; 90-day rats, 196+/-37; 24-month rats, 173+/-52). NAF was substantially reduced (67-91%) 96 h after maximum tolerated dosages of CPF in adult and aged rats (279 mg/kg, sc) but not in juveniles (127 mg/kg, sc), even though AChE inhibition was similar among the age groups (>80%). Together these data suggest that NAF is differentially expressed during maturation and that this neuromodulatory process may be selectively altered by some OP insecticides, potentially contributing to age-related differences in response to AChE inhibitors. As NAF has been postulated to be activated under conditions of 'impaired' cholinergic function, selective alteration of this pre-synaptic process by OP anticholinesterases may be also important in age-related conditions associated with cholinergic hypofunction.

Neither forced running nor forced swimming affect acute pyridostigmine toxicity or brain-regional cholinesterase inhibition in rats.

Stress-induced change in the distribution of the drug pyridostigmine (PYR) has been proposed as a contributing factor to unexplained illnesses in Persian Gulf War veterans. We evaluated the effects of two stress models, forced running and forced swimming, on acute PYR (30 mg/kg, p.o.) toxicity and cholinesterase (ChE) inhibition in the blood and selected brain regions of young adult male Sprague-Dawley rats (6 weeks of age). Plasma corticosterone levels were measured at 0, 1 and 3 h after termination of forced swimming or forced running to confirm the induction of stress. PYR was given either immediately before stress (15 min swimming; 20 min running) or immediately after stress (15 min swimming; 90 min running) and cholinergic toxicity and ChE inhibition were evaluated at 1, 2 or 4 h after PYR exposure. Additionally, rats were subjected to either swimming (15 min) or running (90 min) stress, anesthetized, injected with horseradish peroxidase (HRP, 100 mg/kg, transcardial) and brain-regional HRP activity measured as an indicator of altered blood-brain barrier integrity. Both forced swimming and forced running resulted in significant elevations of plasma corticosterone levels. PYR caused cholinergic toxicity at all time-points evaluated. Swimming and running stress had little influence on expression of PYR-induced toxicity, however. Blood ChE activity was generally inhibited 77-91% at 1-4 h after PYR, but rats pretreated with PYR prior to forced swimming showed lesser inhibition (64%) 1 h after dosing, possibly because of swimming-induced hypothermia and delayed absorption of the drug. Minimal changes in ChE activity were noted in frontal cortex, cerebellum and hippocampus following PYR exposure (maximal inhibition 28%), and neither swimming nor running stress affected the degree of inhibition. Neither stress model increased HRP accumulation in any brain region. The results suggest that stress associated with forced running or forced swimming has little effect on acute PYR toxicity, entry of PYR into the brain or PYR-induced brain-regional ChE inhibition.

Age-related effects of chlorpyrifos on muscarinic receptor-mediated signaling in rat cortex.

Chlorpyrifos (CPF) is a widely used organophosphorus pesticide. Earlier work from our laboratory and others has demonstrated that the sensitivity to CPF exposure changes markedly during maturation. A number of studies suggest that in addition to inhibiting acetylcholinesterase (AChE), CPF oxon may also interact directly with m2 and/or m4 subtypes of muscarinic acetylcholine receptors (mAChRs). In the present study, we investigated the in vivo effects of CPF exposure on phosphoinositide (PI) hydrolysis and cAMP formation, second-messenger systems coupled to m1, m3 and m5 (PI hydrolysis) or m2 and m4 (cAMP formation) mAChRs. Neonatal (7-day), juvenile (21-day) and adult (90-day) rats were treated with either peanut oil s.c. or CPF s.c. at 0.3x or 1x the maximum tolerated dosage (MTD: 45, 127 and 279 mg/kg for 7-day, 21-day and 90-day rats, respectively). Neurochemical end-points including AChE activity, muscarinic receptor ([3H]quinuclidinyl benzilate, and [3H]oxotremorine) binding, PI hydrolysis, and cAMP formation in cortex were evaluated at 4 h, 24 h, or 96 h after treatment. Under these conditions, relatively similar maximal degrees of cholinesterase (ChE) inhibition were noted, but times to peak inhibition varied among these age groups (24 h in neonates and juveniles, 96 h in adults). Total muscarinic receptor (QNB) binding was reduced in all three age groups with 1x MTD exposure, at both 24 h and 96 h in neonates and juveniles, but only at 96 h in adults. Oxotremorine binding was also reduced at 96 h after MTD exposure in all three age groups. Neither basal nor carbachol-stimulated IP accumulation was affected in any age group or at any time point following CPF exposure. In contrast, basal cAMP formation was significantly increased by MTD exposure in all three age groups 4 h after exposure, and at 4 h, 24 h, and 96 h after exposure in juveniles. Forskolin/Mn2+-stimulated cAMP formation was increased in neonates and juveniles at 96 h, and in juveniles also at 24 h, but was significantly decreased in adults at 96 h after MTD exposure. Oxotremorine-mediated inhibition of cAMP formation was significantly greater at 96 h after MTD exposure in all three age groups. These results provide further evidence that the cortical cAMP signaling pathway may be particularly sensitive to CPF exposure in neonatal, juvenile, and adult rats, possibly due to a direct interaction between CPF (or its oxon) and mAChRs or other components of the adenylyl cyclase cascade.

In vitro effects of chlorpyrifos, parathion, methyl parathion and their oxons on cardiac muscarinic receptor binding in neonatal and adult rats.

Organophosphorus insecticides elicit toxicity by inhibiting acetylcholinesterase. Young animals are generally more sensitive than adults to these toxicants. A number of studies reported that some organophosphorus agents also bind directly to muscarinic receptors, in particular the m(2) subtype, in tissues from adult rats. As both the density and agonist affinity states of cardiac muscarinic receptors (primarily m(2)) have been reported to change in an age-related manner, we evaluated the relative in vitro sensitivity of cardiac muscarinic receptors in tissues from neonatal (7-11 days of age) and adult (90 days of age) rats to selected organophosphorus compounds (chlorpyrifos, parathion, methyl parathion and their oxygen analogs or oxons). The effects of the cholinergic agonist carbachol (100 pM-5 microM) or an organophosphorus toxicant (50 pM-10 microM) on muscarinic receptor binding were determined using the nonselective muscarinic ligand [3H]quinuclidinyl benzilate or the m(2)-preferential ligand [3H]oxotremorine-M acetate. Carbachol displaced [3H]oxotremorine labeling in adult and neonatal membranes in a relatively similar manner (IC(50)=7-20 nM). The oxons all displaced [3H]oxotremorine binding in a concentration-dependent manner, with chlorpyrifos oxon being the most potent (IC(50): neonates, 15 nM; adults, 7 nM) and efficacious (maximum displacement: neonates, 42%; adults, 56%). Interestingly, methyl parathion was an extremely potent displacer of [3H]oxotremorine binding in adult tissues (IC(50)=0.5 nM, maximum displacement=37%) but had no effect in neonatal tissues. The displacement of [3H]oxotremorine binding by chlorpyrifos oxon (10 microM) was still apparent after washing the tissues, suggesting the oxon irreversibly blocked agonist binding to the receptor while interaction with MePS appeared reversible. As effective concentrations of the oxons were relatively similar to their anticholinesterase potencies, these findings suggest that direct interaction with cardiac muscarinic receptors by some organophosphorus agents may occur at relevant exposure levels and contribute to cardiac toxicity.