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V C Moser

Publications and source records attributed to V C Moser.

At least 19 recordsLinked to original sources

Evaluation of cognitive function in weanling rats: a review of methods suitable for chemical screening.

Current developmental neurotoxicity (DNT) tests that are used for environmental agents require cognitive testing around the age of weaning as well as adulthood. There are challenges associated with testing weanling rodents that are not present with testing older subjects, including rapid brain development, and the impact of food or water restriction necessary for appetitive paradigms. This review provides an overview of cognitive tests that can be used for laboratory rodents in the context of such DNT studies; as such, those requiring surgery or food/water deprivation are excluded. Potential test methods described herein include spontaneous, avoidance, conditioned, spatial, and sequential behavioral assays; although, some procedures meet scientific and regulatory requirements better than others. Scientific judgment should be exercised in the choice of cognitive measures for weanling rodents in DNT studies, and should include an assessment of the sensitivity and efficiency of the procedure, an understanding of the literature and the neuronal substrates involved, and evaluation of available information on the mode(s) of action of the test chemical.

Animals↗

Neurobehavioral effects of chronic dietary and repeated high-level spike exposure to chlorpyrifos in rats.

This study aimed to model long-term subtoxic human exposure to an organophosphorus pesticide, chlorpyrifos, and to examine the influence of that exposure on the response to intermittent high-dose acute challenges. Adult Long-Evans male rats were maintained at 350 g body weight by limited access to a chlorpyrifos-containing diet to produce an intake of 0, 1, or 5 mg/kg/day chlorpyrifos. During the year-long exposure, half of the rats in each dose group received bi-monthly challenges (spikes) of chlorpyrifos, and the other half received vehicle. Rats were periodically tested using a neurological battery of evaluations and motor activity to evaluate the magnitude of the acute response (spike days) as well as recovery and ongoing chronic effects (non-spike days). Effects of the spikes differed as a function of dietary level for several endpoints (e.g., tremor, lacrimation), and in general, the high-dose feed groups showed greater effects of the spike doses. Animals receiving the spikes also showed some neurobehavioral differences among treatment groups (e.g., hypothermia, sensory and neuromotor differences) in the intervening months. During the eleventh month, rats were tested in a Morris water maze. There were some cognitive deficits observed, demonstrated by slightly longer latency during spatial training, and decreased preference for the correct quadrant on probe trials. A consistent finding in the water maze was one of altered swim patterning, or search strategy. The high-dose feed groups showed more tendency to swim in the outer annulus or to swim very close to the walls of the tank (thigmotaxic behavior). Overall, dietary exposure to chlorpyrifos produced long-lasting neurobehavioral changes and also altered the response to acute challenges.

Animals↗

Neurotoxicological and statistical analyses of a mixture of five organophosphorus pesticides using a ray design.

Environmental exposures generally involve chemical mixtures instead of single chemicals. Statistical models such as the fixed-ratio ray design, wherein the mixing ratio (proportions) of the chemicals is fixed across increasing mixture doses, allows for the detection and characterization of interactions among the chemicals. In this study, we tested for interaction(s) in a mixture of five organophosphorus (OP) pesticides (chlorpyrifos, diazinon, dimethoate, acephate, and malathion). The ratio of the five pesticides (full ray) reflected the relative dietary exposure estimates of the general population as projected by the US EPA Dietary Exposure Evaluation Model (DEEM). A second mixture was tested using the same dose levels of all pesticides, but excluding malathion (reduced ray). The experimental approach first required characterization of dose-response curves for the individual OPs to build a dose-additivity model. A series of behavioral measures were evaluated in adult male Long-Evans rats at the time of peak effect following a single oral dose, and then tissues were collected for measurement of cholinesterase (ChE) activity. Neurochemical (blood and brain cholinesterase [ChE] activity) and behavioral (motor activity, gait score, tail-pinch response score) endpoints were evaluated statistically for evidence of additivity. The additivity model constructed from the single chemical data was used to predict the effects of the pesticide mixture along the full ray (10-450 mg/kg) and the reduced ray (1.75-78.8 mg/kg). The experimental mixture data were also modeled and statistically compared to the additivity models. Analysis of the 5-OP mixture (the full ray) revealed significant deviation from additivity for all endpoints except tail-pinch response. Greater-than-additive responses (synergism) were observed at the lower doses of the 5-OP mixture, which contained non-effective dose levels of each of the components. The predicted effective doses (ED20, ED50) were about half that predicted by additivity, and for brain ChE and motor activity, there was a threshold shift in the dose-response curves. For the brain ChE and motor activity, there was no difference between the full (5-OP mixture) and reduced (4-OP mixture) rays, indicating that malathion did not influence the non-additivity. While the reduced ray for blood ChE showed greater deviation from additivity without malathion in the mixture, the non-additivity observed for the gait score was reversed when malathion was removed. Thus, greater-than-additive interactions were detected for both the full and reduced ray mixtures, and the role of malathion in the interactions varied depending on the endpoint. In all cases, the deviations from additivity occurred at the lower end of the dose-response curves.

Animals↗

Further assessment of an in vitro screen that may help identify organophosphorus pesticides that are more acutely toxic to the young.

Some, but not all, organophosphorus pesticides are more acutely toxic to the young as compared to adults. We have developed an in vitro assay that measures the detoxification potential (via carboxylesterase and A-esterases) of tissues. Previous results using this in vitro screen correlated with the marked in vivo sensitivity of the young to chlorpyrifos and also correlated with the equal sensitivity of the young and adult to methamidophos (Padilla et al., 2000). We have now extended these observations to two other pesticides that have already been shown in the literature to be more toxic to the young: parathion (paraoxon) and malathion (malaoxon). In our in vitro assay, liver or plasma from 7-d-old rats were much less efficacious than adult tissues at detoxification of the active metabolites of these two pesticides. Using our in vitro assay we also tested the active metabolite of diazinon, diazoxon, and again found that young liver or plasma possessed much less detoxification capability than adult tissues. From these results, we predicted that young animals would be more sensitive to diazinon, which, in fact, was the case: When postnatal day (PND) 17 or adult rats were given a dosage of 75 mg/kg diazinon, adult brain cholinesterase (ChE) was only inhibited 38%, while the brain ChE in the PND 17 animals showed much more inhibition (75%). We conclude that our in vitro screen may prove to be a useful, quick, convenient test for identifying which organophosphorus pesticides may be more acutely toxic to the young as compared to adults.

Age Factors↗

Neurotoxicity produced by dibromoacetic acid in drinking water of rats.

An evaluation of potential adverse human health effects of disinfection byproducts requires study of both cancer and noncancer endpoints; however, no studies have evaluated the neurotoxic potential of a common haloacetic acid, dibromoacetic acid (DBA). This study characterized the neurotoxicity of DBA during 6-month exposure in the drinking water of rats. Adolescent male and female Fischer 344 rats were administered DBA at 0, 0.2, 0.6, and 1.5 g/l. On a mg/kg/day basis, the consumed dosages decreased greatly over the exposure period, with average intakes of 0, 20, 72, and 161 mg/kg/day. Weight gain was depressed in the high-concentration group, and concentration-related diarrhea and hair loss were observed early in exposure. Testing with a functional observational battery and motor activity took place before dosing and at 1, 2, 4, and 6 months. DBA produced concentration-related neuromuscular toxicity (mid and high concentrations) characterized by limb weakness, mild gait abnormalities, and hypotonia, as well as sensorimotor depression (all concentrations), with decreased responses to a tail-pinch and click. Other signs of toxicity at the highest concentration included decreased activity and chest clasping. Neurotoxicity was evident as early as one month, but did not progress with continued exposure. The major neuropathological finding was degeneration of spinal cord nerve fibers (mid and high concentrations). Cellular vacuolization in spinal cord gray matter (mostly) and in white matter (occasionally) tracts was also observed. No treatment-related changes were seen in brain, eyes, peripheral nerves, or peripheral ganglia. The lowest-observable effect level for neurobehavioral changes was 20 mg/kg/day (produced by 0.2 g/l, lowest concentration tested), whereas this dosage was a no-effect level for neuropathological changes. These studies suggest that neurotoxicity should be considered in the overall hazard evaluation of haloacetic acids.

Acetates↗

Neurobehavioral evaluations of mixtures of trichloroethylene, heptachlor, and di(2-ethylhexyl)phthalate in a full-factorial design.

One approach to the toxicological evaluation of chemical mixtures is to construct full dose-response curves for each compound in the presence of a range of doses of each of the other compounds, i.e., a factorial design. This study was undertaken as part of an interdisciplinary project to evaluate a mixture of three environmental pollutants. A full-factorial design was undertaken to determine the neurobehavioral consequences of short-term repeated exposure to five dose levels each of three chemicals, in order to characterize potential two- and three-way interactions. Adult female F344 rats received (p.o.) for 10 days either one of five doses of trichloroethylene, di(2-ethylhexyl)phthalate, or heptachlor, or else one of all possible chemical combinations. Neurobehavioral evaluations were conducted using motor activity and an abbreviated functional observational battery. Response-surface analysis was applied to each of the endpoints. Hypotheses were tested based on the estimated model parameters; of primary interest was the overall test for interaction among the three chemicals. In addition, an abbreviated design was created by fitting only a subset of the data to the model. In general, significant overall interactions that deviated from response additivity were detected for most endpoints (11 of 14). All of the interactions on the neurobehavioral endpoints showed either antagonism, or else an interaction that could not be fully characterized. Often the results of the abbreviated dataset analysis were not the same as for the full-factorial design. This study was extremely intensive, in terms of the number of rats and time required for conduct of the study as well as the data analysis. These results underscore the need for more economical approaches to evaluate the toxic effects of mixtures of chemicals.

Animals↗

Neurotoxicological outcomes of perinatal heptachlor exposure in the rat.

The developing nervous system has been identified as a potential target of pesticide exposure. Heptachlor is a cyclodiene pesticide that was widely used for many years, and for which inadvertent exposure to children and fetuses took place in the early 1980s; yet little is known regarding the developmental neurotoxicity of it and other cyclodienes. The aim of this study was to determine whether perinatal heptachlor exposure results in persistent alterations in nervous system function. Pregnant Sprague-Dawley dams were dosed from gestational day (GD) 12 to postnatal day (PND) 7, whereupon the rat pups were dosed directly until PND 21 (group A) or PND 42 (group B). Dose levels were 0, 0.03, 0.3, or 3 mg/kg/day, po. There were no dose-related effects on maternal weight, litter size, or pup growth. GABA(A) receptor binding (using [(35)S] tert-butylbicyclophosphorothionate; TBPS) and GABA-stimulated Cl- flux were evaluated in control and high-dose brain tissues taken on PND 7, 21, and 43. The B(max) values for [(35)S]-TBPS binding in brainstem, but not cortex, were decreased in female rats across all ages tested. There were no such changes in male rats, nor were K(D) values altered in either tissue or gender. GABA-stimulated Cl- flux was decreased in female cortex synaptoneurosomes only on PND 21. The ontogeny of the righting response (PND 2-5) was delayed in the high-dose females. All subsequent testing took place a week to months after dosing ceased. The functional observational battery (FOB) showed treatment-related, but not necessarily dose-related, changes in different aspects of the rat's reactivity and activity levels. Group-A rats also showed altered within-session habituation of motor activity. There were no heptachlor-related differences in motor activity following challenge with a range of chlordiazepoxide doses. Cognitive assessments were conducted in both groups of rats. There were no statistically significant differences among treatment groups in a one-trial passive avoidance test, although there was a trend toward less learning. In group B, rats (both sexes), heptachlor altered spatial learning in the Morris water maze during two weeks of daily training (2 trials/day). On probe trials, heptachlor-treated rats did not show significant preference for the correct quadrant (all dose groups in males, high dose in females). These rats did not show alterations on subsequent working-memory training (where the platform position was relearned each day). Thus, perinatal exposure to heptachlor produced neurochemical and persistent neurobehavioral changes, including alterations in spatial learning and memory.

Animals↗

The effects of perinatal tebuconazole exposure on adult neurological, immunological, and reproductive function in rats.

Studies are under way to address concerns of potential persistent immunotoxic, reproductive, and neurotoxic effects of perinatal exposure to several pesticides. Tebuconazole, a triazole fungicide, was evaluated as part of this project. Sprague-Dawley dams were administered tebuconazole (0, 6, 20, or 60 mg/kg) by oral gavage daily from gestational day 14 to postnatal day (PND)7; the pups were then dosed daily at the same levels from PND7-42. Separate groups of rats were used for testing of immunological parameters, neurobehavioral testing using a screening battery of functional tests, and cognitive evaluations. Other groups of rats were evaluated for reproductive development and function, while yet others were sacrificed at the end of the dosing period for histological analyses of major organs systems, including neuropathological assessments. Pup viability and body weight were decreased in the highest dose group. There were no differences in the fertility indices in the exposed rats mated as adults. In the sheep RBC-immunized high-dose rats, spleen weights and cellularity were increased, and the ratio of cell types was altered compared to controls. There were, however, no biologically significant changes in the immune function of these rats. At necropsy on PND46 or 152, kidney, liver, and spleen weights were altered by tebuconazole treatment, but a dose-response relationship was not clear for most organs; only decreased kidney and increased liver weights were consistent in both sexes. Histological analyses were generally unremarkable outside of the brain. One month after the end of dosing, acquisition of learning the platform location in a water tank (i.e., Morris water maze) was impaired in the high-dose group; there were no differences in neuromuscular ability, motor activity, or swim speed to account for this finding. Furthermore, there was no effect on recall of the position during a free-swim trial. Neuropathological evaluations revealed pyknotic cells across hippocampal cell fields in animals of all tebuconazole treatment groups, with the highest incidence in the 20 and 60 mg/kg/day dose groups, coincident with cell loss within pyramidal cell layer of CA3-4 cell fields of the hippocampus and layer V of the neocortex. Thus, perinatal exposure to tebuconazole produced neurobehavioral deficits and neuropathology in rats, but did not alter immunological or reproductive function.

Animals↗

Dopamine transporter binding in the rat striatum is increased by gestational, perinatal, and adolescent exposure to heptachlor.

Heptachlor is a persistent cyclodiene pesticide that affects GABAergic function. Recent reports indicate that heptachlor exposure also alters dopamine transporter (DAT) expression and function in adult mice. The aim of this study was to determine whether gestational, perinatal, and/or adolescent heptachlor exposure in rats altered dopamine-receptor and DAT binding. Adolescent exposure to dieldrin was included to evaluate the generality of the findings. Sprague-Dawley rats received doses (po) ranging from 0 to 8.4 mg/kg/day of heptachlor, or dieldrin, 3 mg/kg/day, during different developmental periods. There were dose-related decreases in maternal weight gain and pup survival, as well as delayed righting reflex, at heptachlor doses > or =3 mg/kg/day. There were no changes in striatal dopamine receptor-D1 ([(3)H]SCH-23390) and -D2 ([(3)H]spiperone) binding in preweanling pups exposed perinatally to heptachlor, and no differences in the response of adult rats to the motor activity-increasing effects of d-amphetamine. However, there were significant (27-64%) increases in striatal DAT binding of [(3)H]mazindol in preweanling rats exposed only gestationally. In rats exposed perinatally and/or during adolescence, there were also increases (34-65%) in striatal DAT binding at postnatal days (PND) 22, 43, and 128. Adolescent exposure to dieldrin also increased DAT binding. In other rats exposed perinatally and throughout adolescence, even the lowest dose of heptachlor 0.3 mg/kg/d increased DAT binding on PND 130. The DAT affinity for mazindol was unchanged in heptachlor-exposed striata. In vitro binding studies indicated that heptachlor (> or =10 microM) displaced mazindol binding. Thus, gestational, perinatal, and/or adolescent exposure to heptachlor produced an increase in DAT binding as early as PND 10, and this change persisted into adulthood.

Animals↗

The functional observational battery in adult and developing rats.

Neurobehavioral screening methods, such as the functional observational battery (FOB), are now widely used to identify potential neurotoxicity of new and existing chemicals. These methods have been validated and a large database now exists for the effects of a wide range of chemicals. Since most of the observations recorded are subjective, the quality of the test data depends largely on the observer's ability to detect and describe changes in the animal's behavior and neurologic function. Efforts are underway to aid in the training of observers and to achieve consistency across laboratories in the use of these methods. With the increasing concern over potential neurotoxicological consequences of chemical exposure in the developing organism, there is growing interest in testing laboratory animals at very young ages. We present here an initial report of the development of an FOB suitable for young rats, using some modifications of the individual adult FOB test measures to make them age-appropriate. We have evaluated pre- and postweanling rats to determine the range of behaviors (as evaluated with the FOB) displayed at each age, develop appropriate scoring criteria, and collect control data to document the ontogeny of each of the endpoints in the FOB. This revised FOB protocol may be useful for assessing behavioral or neurological changes due to acute chemical exposure in young rats, or following gestational/lactational exposures typical of developmental neurotoxicity studies.

Aging↗

Comparison of aldicarb and methamidophos neurotoxicity at different ages in the rat: behavioral and biochemical parameters.

Young organisms are often more sensitive to the toxic effects of pesticides, and this finding has spurred research on further characterization of this susceptibility. The neurotoxic effects of cholinesterase (ChE)-inhibiting pesticides are of particular concern for human health risk assessment due to the widespread exposure potential in children. This study evaluated age-related differences in susceptibility for a carbamate (aldicarb) and an organophosphorus pesticide (methamidophos). Comparisons were made between preweanling (Postnatal Day 17, PND17), postweanling (PND27), and adult (approximately PND70) male and female rats. All were acute studies using oral administration. Sensitivity was quantified by (1) determination of maximally-tolerated doses (MTDs); (2) measurement of brain and blood ChE inhibition; and (3) neurobehavioral evaluation using end points known to be sensitive indicators of exposure to anticholinesterases. MTD data showed that preweanling rats were twice as sensitive as adults to aldicarb, but there was no differential sensitivity to methamidophos. The dose-response data for brain ChE inhibition followed a similar pattern of age-related differences, and similar levels of inhibition were measured at the MTD regardless of age. Dose-response and time course studies of neurobehavioral end points indicated that differential effects due to age depend on the behavioral end point examined. Following aldicarb administration, the dose-response curves for a few end points overlapped; however, the young rats otherwise showed fewer signs of toxicity than did the adults despite similar levels of brain ChE inhibition. Motor activity assessment showed that aldicarb did not produce any activity depression in PND17 rats, whereas the data for the PND27 and adult rats overlapped. With methamidophos, the dose-response curves for most end points for preweanling and adult rats were quite similar. Aldicarb-induced ChE inhibition was readily reversible in all age groups, whereas with methamidophos, enzyme activity recovered more rapidly in the young. Most behavioral alterations had recovered by 24 h with either pesticide. The results of these studies indicate that (1) ChE-inhibiting pesticides are not all the same regarding relative sensitivity of the young; (2) age-related differences were reflected in both the MTDs and degree of ChE inhibition; and (3) age-related differences in neurobehavioral measures depended on the pesticide and on the end points examined.

Aging↗

Gestational exposure to chlorpyrifos: dose response profiles for cholinesterase and carboxylesterase activity.

This study investigates the in vivo dose response profiles of the target enzyme cholinesterase (ChE) and the detoxifying enzymes carboxylesterase (CaE) in the fetal and maternal compartments of pregnant rats dosed with chlorpyrifos [(O,O'-diethyl O-3,5,6-trichloro-2-pyridyl) phosphorothionate], a commonly used organophosphorus insecticide. Pregnant rats were dosed daily (po) with chlorpyrifos in corn oil (0, 3, 5, 7, or 10 mg/kg) on gestational days (GD) 14-18. Animals were sacrificed 5 h after the last chlorpyrifos dose (time of maximum brain cholinesterase inhibition) for analysis of ChE and CaE activity in maternal blood, liver, brain, placenta, and fetal liver and brain. The in vitro sensitivity (i.e., IC50, 30 min, 26 degrees C) of CaE also was determined by assaying the activity remaining after incubation with a range of chlorpyrifos-oxon concentrations. In vivo exposure to 10 mg/kg chlorpyrifos from GD14-18 caused overt maternal toxicity, with dose-related decreases in ChE activity more notable in maternal brain than fetal brain. Dose-related effects were also seen with chlorpyrifos-induced inhibition of fetal liver ChE and maternal brain CaE activities. Gestational exposure caused no inhibition of placental ChE or CaE, fetal brain CaE, or maternal blood CaE. ChE activities in the maternal blood and liver, as well as fetal and maternal liver CaE, however, were maximally inhibited by even the lowest dosage of chlorpyrifos. The in vitro sensitivity profiles of CaE to chlorpyrifos-oxon inhibition were valuable in predicting and verifying the in vivo CaE response profiles. Both the in vivo and in vitro findings indicated that fetal liver CaE inhibition was an extremely sensitive indicator of fetal chlorpyrifos exposure.

Analysis of Variance↗

Age- and gender-related differences in the time course of behavioral and biochemical effects produced by oral chlorpyrifos in rats.

It is well known that young animals are generally more sensitive to lethal effects of cholinesterase-inhibiting pesticides, but there are sparse data comparing less-than-lethal effects. We compared the behavioral and biochemical toxicity of chlorpyrifos in young (postnatal Day 17; PND17) and adult (about 70 days old) rats. First, we established that the magnitude of the age-related differences decreased as the rat matures. Next, we evaluated the time course of a single oral dose of chlorpyrifos in adult and PND17 male and female rats. Behavioral changes were assessed using a functional observational battery (with age-appropriate modifications for pre-weanling rats) and an evaluation of motor activity. Cholinesterase (ChE) activity was measured in brain and peripheral tissues and muscarinic receptor binding assays were conducted on selected tissues. Rats received either vehicle (corn oil) or chlorpyrifos (adult dose: 80 mg/kg; PND17 dose: 15 mg/kg); these doses were equally effective in inhibiting ChE. The rats were tested, and tissues were then taken at 1, 2, 3.5, 6.5, 24, 72, 168, or 336 h after dosing. In adult rats, peak behavioral changes and ChE inhibition occurred in males at 3.5 h after dosing, while in females the onset of functional changes was sooner, the time course was more protracted and recovery was slower. In PND17 rats, maximal behavioral effects and ChE inhibition occurred at 6.5 h after dosing, and there were no gender-related differences. Behavioral changes showed partial to full recovery at 24 to 72 h, whereas ChE inhibition recovered markedly slower. Blood and brain ChE activity in young rats had nearly recovered by 1 week after dosing, whereas brain ChE in adults had not recovered at 2 weeks. Muscarinic-receptor binding assays revealed apparent down-regulation in some brain areas, mostly at 24 and 72 h. PND17 rats generally showed more receptor down-regulation than adults, whereas only adult female rats showed receptor changes in striatal tissue that persisted for 2 weeks. Thus, compared to adults (1) PND17 rats show similar behavioral changes and ChE inhibition although at a five-fold lower dose; (2) the onset of maximal effects is somewhat delayed in the young rats; (3) ChE activity tended to recover more quickly in the young rats; (4) young rats appear to have more extensive muscarinic receptor down-regulation, and (5) young rats show no gender-related differences.

Age Factors↗

Gestational exposure to chlorpyrifos: apparent protection of the fetus?

Previous studies have shown that, in general, young, postnatal animals are more sensitive than adults to the toxic effects of anticholinesterase (antiChE) pesticides. Paradoxically, often fetal brain cholinesterase (ChE) is less inhibited than maternal brain after gestational exposure to an antiChE, presumably due to placental and fetal detoxification of the antiChE. The present investigation was designed to study selected toxicokinetic and toxicodynamic factors surrounding the toxicity of chlorpyrifos (CPF; [O,O'-diethyl O-3,5,6-trichloro-2-pyridyl] phosphorothionate) in pregnant rats dosed repeatedly or singly during late gestation. Dams were dosed daily (po) with CPF in corn oil (0 or 7 mg/kg) on gestational days (GD) 14 to 18. Animals were euthanized at 2 to 120 h after the last dose and tissues were collected for enzyme analysis. Using this dosing regimen, we found that (1) the time of maximal ChE inhibition was the same (i.e., 5-10 h after dosing) for both maternal and fetal brain, (2) the degree of fetal brain ChE inhibition was 4.7 times less than maternal brain inhibition, and (3) the detoxification potential (i.e., carboxylesterase and chlorpyrifos-oxonase) of the fetal tissues was very low compared to the maternal tissues. A separate group of experiments showed that if pregnant dams received only one oral dose of 7 or 10 mg/kg CPF on GD18, the degree of ChE inhibition in the fetal brain was comparable to the maternal brain ChE inhibition. Taking into consideration the net increase (more than fourfold) in fetal brain ChE activity from GD14 to 18 in control animals, and the fact that maternal brain ChE was inhibited more than fetal brain ChE only in a repeated-dosing regimen, we conclude that the fetus is not genuinely protected from the toxic effects of a given dose of CPF. We propose that fetal brain ChE is simply able to recover more fully between each dose as compared to maternal brain ChE, giving the illusion that the fetal compartment is less affected than the maternal compartment.

Animals↗

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.

Age Factors↗

Carbon disulfide neurotoxicity in rats: VII. Behavioral evaluations using a functional observational battery.

The neurobehavioral consequences of inhalational exposure to carbon disulfide (CS2) were evaluated as part of a joint project between the National Institute of Environmental Health Sciences and the U.S. Environmental Protection Agency. Behavioral changes in rats were measured using a functional observational battery (FOB), which is a series of observations and manipulations designed to assess the neuronal integrity of autonomic, motor, sensory, and integrative functions. Young adult male and female Fischer-344 rats were exposed to one of four CS2 concentrations (0, 50, 500, or 800 ppm, six hours/day, five days/week) and tested at the end of one of several exposure durations (two, four, eight, or 13 weeks). All rats were also tested before exposure began to obtain baseline values. Neuromuscular deficits which were more pronounced in the hindlimbs, e.g., decreased strength and gait alterations, were detected in rats of both sexes. These changes were closely related to CS2 concentration and exposure duration, with mild gait changes evident after only two weeks of exposure. Other effects, mostly observed at 13 weeks, included decreased responsiveness to a visual stimulus and mild tremors. Reactivity in response to handling was generally increased, and excitability in the open field was decreased, in rats tested after the shorter exposures (two and four weeks). Thus, the exposure-concentration and -duration characteristics of the neuromotor syndrome produced by CS2 were detected and defined using the FOB. These studies provide a more complete evaluation of rats under these CS2 exposure conditions, which can then be used to compare with other mechanistic-related endpoints from this collaborative study.

Administration, Inhalation↗

The IPCS collaborative study on neurobehavioral screening methods.

The International Programme on Chemical Safety sponsored a collaborative study to evaluate the utility of neurobehavioral test methods for identifying neurotoxic chemicals. The protocol consisted of a functional observational battery and automated assessment of motor activity. The study involved four laboratories in the United States and four in Europe, each of which evaluated the dose- and time-related effects of seven prototypic chemicals following both single and 4-week repeated exposures. The protocol was designed to assess the general utility and reliability of neurobehavioral screening procedures in a diversity of testing situations. The results of chemical testing indicated that all participating laboratories generally could detect and characterize the effects of known neurotoxicants, despite some differences on specific endpoints. These data provide important information regarding the reliability and sensitivity of neurobehavioral screening methods over a range of laboratory conditions. The purpose of this workshop was to describe the background and study design of the collaborative effort, present the data (including comparison of results across laboratories), and discuss issues regarding the conduct and interpretation of these behavioral tests, as well as future directions for neurotoxicity screening.

Animals↗