Effects of trichloroethylene inhalation on proteins of the gerbil brain

Effect of trichloroethylene on spatiotemporal pattern of LTP in mouse hippocampal slices

The effect of trichloroethylene (TCE) on long-term potentiation (LTP) was studied using both electrical and optical recording. The hippocampi from mice injected with 300 mg/kg or 1000 mg/kg TCE were sliced 24 h after administration. The field potential from the CAI was recorded. After the application of tetanus, population spikes (PS) were potentiated in all groups, but the post-per-pre ratio of PS was smaller in TCE groups than in the control. Optical recording was also carried out in 1000 mg/kg TCE-injected mice and a new analytical method using a high speed camera was employed. After the induction of tetanus, the optical signal was potentiated in both TCE and control groups. However, the post-per-pre ratio of the optical signals and response area were smaller in the TCE groups than in the control. It was suggested that the impairment of LTP is one of the mechanisms of the impairment of immediate memory after acute exposure to TCE in humans.

Presence of sst2(a) receptor immunoreactivity in rat ependyma and tanycytes

Somatostatin sst2(a) receptor was observed, by immunofluorescence, in ependymal cells and in tanycytes of the wall of the ventricle and the hypothalamic recess of the male rat median eminence. Strong immunoreactivity for the receptor protein was observed in lateral tanycytes (alpha-type) while a moderate signal was seen in medial tanycytes (beta-type). In high magnification the immunoreactive material, of moderate intensity, had a coarse granular appearance. Only few of the alpha-tanycytes also displayed immunoreactive GFAP. The apical portion of the ependymal cells as well as of tanycytes contained immunoreactive S-100 (alphabeta). Since rather high levels of somatostatin are demonstrated to occur in the cerebrospinal fluid of the third ventricle, it is suggested that somatostatin via the sst2(a) receptor may regulate the physiology of tanycytes.

Antiserum against S-100 protein prevents long term potentiation through a cAMP-related mechanism

Long term potentiation (LTP) was induced in the CA1 region of rat hippocampal slices by tetanization of the Schaffer collaterals. Local pretreatment of CA1 with serum of rabbits immunized against S-100 prevented the potentiation. However, treatment of the slices with a membrane permeant cAMP analogue, such as 8-Br-cAMP, could protect against the blocking effect of anti S-100 serum. We suggest that in the rat endogenous S-100b is involved in transduction mechanisms during LTP induction, via its ability to stimulate adenylate cyclase. Possible mechanisms of this action are discussed.

Involvement of S-100 protein in anoxic long-term potentiation

In in vitro rat hippocampal slices a short period (2 min) of hypoxia resulted in lasting potentiation of the population spike transynaptically evoked in CA1 by stimulation of Schaffer collaterals ("anoxic LTP"). Pretreatment of slices with antiserum against S-100 protein fully prevented this anoxic LTP. Since also "classical" (i.e., induced by high-frequency electrical stimulation) long-term potentiation is prevented by anti S-100 serum, this represents one more important similarity between these events.

S-100 beta has a neuronal localisation in the rat hindbrain revealed by an antigen retrieval method

The localisation of S-100 in mammalian CNS neurons has been under debate for more than two decades. We address the question with two polyclonal and two new monoclonal antibodies. The specificity and the distribution in rat brain is based on an antigen retrieval method. We present evidence that aldehyde fixatives mask S-100 beta in neurons, and that the immunoreactivity is retrieved after trypsinisation. Neuronal S-100 beta is also detected in unfixed and ethanol fixed sections. The neuronal immunoreactivity is partly solubilised from unfixed tissue sections with 2.5 mM EDTA and is completely extracted with 2.5 mM EDTA and 1% Triton X-100. Most of the glial S-100 beta is washed out from unfixed tissue sections with saline. S-100 beta has distinct distribution in neurons of the hindbrain, i.e., the brainstem and cerebellum, but is not observed in the forebrain. One of the monoclonal antibodies immunostained neither neurons nor glia when it had been absorbed with S-100 crosslinked to nitrocellulose membranes. The distribution of neuronal S-100 beta differed from that of other neuronal calcium binding proteins, such as calbindin and parvalbumin. It was confined mainly to cholinergic neurons of the hindbrain. The presence of S-100 beta in distinct neuronal populations may indicate neurotrophic effects of S-100 beta. The notion is supported by the capability of S-100 to cause neurite outgrowth in vitro.

Trichloroethylene--a review of the literature from a health effects perspective

This report reviews the literature on the impact of exposure to trichloroethylene (TCE) on human health. Special emphasis is given to the health effects reported in excess of national norms by participants in the TCE Subregistry of the Volatile Organic Compounds Registry of the National Exposure Registries--persons with documented exposure to TCE through drinking and use of contaminated water. The health effects reported in excess by some or all of the sex and age groups studied were speech and hearing impairments, effects of stroke, liver problems, anemia and other blood disorders, diabetes, kidney disease, urinary tract disorders, and skin rashes.

Fatty acid composition in liver, serum and brain of rat inhalated with trichloroethylene

Temporal variations in chronic effects of inhalated 300 ppm trichloroethylene (TCE) on the fatty acid composition in rats were investigated to clarify influences of TCE on the fatty acid metabolism of serum, liver and brain, including synaptosome, myelin and mitochondria fractions on weeks 0, 4, 8, 12 after exposure and on week 4 after rehabilitation started following 12 weeks exposure. On week 4, rats exposed to TCE had significantly lighter body weight, lighter epididymal fat pads weight and heavier liver weight compared with controls. In liver and serum, increases in 16:0, 18:0, 18:1n-9, 20:2n-6, 20:3n-6 and 20:4n-6 and decreases in 18:2n-6, 18:3n-6, 18:3n-3, 20:5n-3, 22:5n-3 and 22:6n-3 were also observed. The differences between the exposure and the control groups in the fatty acid composition in liver and serum, except for 18:1n-9 and 18:2n-6, did not enhance from week 4 after TCE exposure. In brain, significant changes of fatty acid composition caused by TCE appeared as decreases in 18:2n-6 and 22:5n-3, and increases in 20:4n-6 and 22:4n-6 during the whole exposure period. Changes of fatty acid composition in brain occurred in the same manner as in serum and liver phospholipids, except that 18:1n-9 was elevated in mitochondria. Changes in brain were slighter and appeared later than those in liver and serum. TCE had a strong effect on the fatty acid composition of mitochondria in neural cells.(ABSTRACT TRUNCATED AT 250 WORDS)

Acute effects of trichloroethylene on blood concentrations and performance decrements in rats and their relevance to humans

This study was designed to clarify the nature of effects of trichloroethylene (TCE) on the central nervous system, and to determine the critical concentrations in blood associated with specific behavioural changes. This was achieved by a follow up of the whole time course of TCE intoxication during and after exposure. The effects of a single four hour exposure to TCE on signalled bar press shock avoidance in rats were tested by methods previously applied to investigate the acute neurobehavioural effects of exposure to toluene. Even low exposure to TCE induced shock avoidance performance decrements in rats. Rats exposed to 250 ppm TCE showed a significant decrease both in the total number of lever presses and in avoidance responses at 140 minutes of exposure compared with controls. The rats did not recover their pre-exposure performance until 140 minutes after the exhaustion of TCE vapour. Exposures in the range 250 ppm to 2000 ppm TCE for four hours produced concentration related decreases in the avoidance response rate. No apparent acceleration of the reaction time was seen during exposure to 1000 or 2000 ppm TCE. The latency to a light signal was somewhat prolonged during the exposure to 2000 to 4000 ppm TCE. It is estimated that there was depression of the central nervous system with slight performance decrements and the corresponding blood concentration was 40 micrograms/ml during exposure. Depression of the central nervous system with anaesthetic performance decrements was produced by a blood TCE concentration of about 100 micrograms/ml. These results showed effects of TCE on the central nervous system that were considered to be a function of both the exposure concentration and the duration of exposure, which are closely related to the TCE concentration in blood.

Perchloroethylene-induced reduction in glial and neuronal cell marker proteins in rat brain

Rats were exposed to continuous inhalation of 300 and 600 p.p.m. of perchloroethylene for 4 and 12 weeks. Exposure to 600 p.p.m. for 4 to 12 weeks resulted in a slower increase in brain weight. Brain region weights, total proteins and DNA were decreased in frontal cerebral cortex and brain stem but not in hippocampus after exposure to 600 p.p.m. for 12 weeks. Four marker proteins were measured to monitor the specific neurotoxic effects of perchloroethylene: S-100 protein and glial fibrillary acidic protein as glial cell markers and neurone specific enolase and neurofilament 68 kD polypeptide as neuronal markers. The concentrations of glial and neuronal cytoskeletal proteins (glial fibrillary acidic protein and neurofilament 68 kD polypeptide) were reduced in frontal cerebral cortex. The total tissue contents of glial proteins (S-100 protein and glial fibrillary acidic protein) were decreased in all 3 brain regions investigated (frontal cerebral cortex, hippocampus and brain stem). Neurone specific enolase was unchanged by perchloroethylene exposure. These results indicate that exposure to perchloroethylene reduces the number of brain cells, possibly glial cells, and interferes with the metabolism of cytoskeletal elements in both glial and neuronal cells.

Glial and neuronal marker proteins in the silicone chamber model for nerve regeneration

In the present study, neuronal and Schwann cell marker proteins were used to biochemically characterize the spatiotemporal progress of degeneration/regeneration in the silicone chamber model for nerve regeneration. Rat sciatic nerves were transected and the proximal and distal stumps were inserted into a bridging silicone chamber with a 10-mm interstump gap. Using dot immunobinding assays, S-100 protein and neuronal intermediate filament polypeptides were measured in different parts of the nerve 0-30 days after transection. In the most proximal nerve segment, all the measured proteins were transiently increased. In the proximal and distal stumps adjacent to the transection, the studied proteins were decreased indicating degeneration of the nerve. Within the silicone chamber, the regenerating nerve expressed the Schwann cell S-100 protein already at 7 days, whereas the neurofilament polypeptides appeared later. These observations are corroborated by previous morphological studies. The biochemical method described provides a new and fast approach to the study of nerve regeneration.

Quantitative alterations of S-100 protein and neuron specific enolase in the rat nervous system after chronic 2,5-hexanedione exposure

The regional changes in quantities of the glial S-100 protein and the neuron specific enolase in the rat nervous system have been studied after long-term exposure to 2,5-hexanedione. The wet weights of most of the examined nervous tissues were found to be reduced, with an extensive effect seen in the brain stem. Using dot immunobinding assays, the concentrations of S-100 were found to be increased in most of the examined tissues, but unaffected in the brain stem. The total amount of S-100 per tissue was markedly reduced in the brain stem. The content of neuron specific enolase was reduced only in the brain stem. Thus the effects of 2,5-hexanedione on the nervous system varied regionally. The brain stem was severely atrophied with a reduction of neuronal as well as of glial marker proteins. Other brain regions contained increased glial cell marker proteins as signs of progressive astroglial reactions.

Neuronal and glial marker proteins in the evaluation of the protective action of MK 801

A quantitative dot immunobinding procedure was used to quantify glial [the S-100 protein and the glial fibrillary acidic (GFA) protein] and neuronal (the 68- and 200-kDa neurofilament polypeptides, neuron-specific enolase, and neuronal cell adhesion molecule) markers. A single intraperitoneal administration of 10 mg/kg of MK 801 blocked the increase of glial parameters and the decrease in content of neuronal marker proteins that occurred as the response to an N-methyl-D-aspartate (NMDA) lesion in the rat hippocampus. The degradation products of GFA protein and the 68-kDa neurofilament polypeptide that were induced by the NMDA lesion did not appear after MK 801 treatment. This study shows that brain-specific proteins are a set of precise tools for the evaluation of neuroprotective effects of antagonists to excitatory amino acids.

The effect of an N-methyl-D-aspartate lesion in the hippocampus on glial and neuronal marker proteins

The study employed an immunochemical quantification of brain cell marker proteins in addition to quantitative morphology in order to provide a more multifacetted and characterized model for an excitotoxic CNS lesion. The importance of the approach in the evaluation of the potential of neuroprotective agents is emphasized. The S-100 protein, the glial fibrillary acidic (GFA) protein, neuron specific enolase (NSE) and neuronal intermediary filament polypeptides (NF 68 and NF 200) were measured with a dot-immunobinding assay, 3-30 days after a unilateral injection of N-methyl-D-aspartate (NMDA) in the left dorsal hippocampus of the rat. After 3 days, the neuronal cell loss averaged 80% in the hippocampus. The S-100 content was reduced 3 days after injection, but was 150% of control at 30 days. GFA increased constantly from days 3 to 30. The neuronal marker proteins were all markedly reduced 7 days after injection. However, at 30 days, NF 68 and NF 200 were close to control (80%). Increasing content would reflect regeneration and sprouting of neurites. The content of the neuronal cytoplasmic marker, NSE, was significantly lower than control also at 10 and 30 days, although a gradual recovery could be traced.

Trichloroethylene affects learning and decreases myelin in the rat hippocampus

The goal of the present study was to relate previously observed behavioral effects with changes in myelin in the hippocampus following exposure to the industrial solvent 1,1,2-trichloroethylene (TCE). Young adult rats exposed to TCE via their drinking water underwent tests to evaluate their ability to perform spatial navigational tasks, and their brains were examined for changes in myelin in the hippocampus. Exposure to an average daily load of 5.5 mg TCE first for 4 weeks and then to 8.5 mg for an additional 2 weeks (separated by a 2-week interval) resulted in an increased level of performance in spatial navigational tasks. Examination of the brains from these animals revealed a significant decrease in the amount of myelin in one layer of the hippocampus, the stratum lacunosum-moleculare. No increase in performance was observed in rats exposed to an average daily load of 5.5 mg TCE for 4 weeks only. A reduction in myelin was observed, however, in the stratum lacunosum-moleculare of these animals. This decrease was not as severe as that seen in the twice-exposed animals. The results of this study suggest that exposure to TCE results in a reduction of hippocampal myelin, and that this reduction may be related to the increased level of performance observed following a second exposure to TCE.

Effects of subacute toluene exposure on neuronal and glial marker proteins in rat brain

The behavior of marker proteins of neurons (gamma-enolase) and glial cells (alpha-enolase, beta-S100 protein and creatine kinase-B) was investigated quantitatively by using enzyme immunoassay systems in toluene-exposed rat brains. Three groups of animals were exposed to toluene vapor at 300 ppm, 1000 ppm, and 3000 ppm, respectively, 8 h/day, 6 days/week, for 2 weeks. After subacute repeated solvent exposure, both neuron-specific gamma-enolase and glial marker proteins displayed an overall concentration-dependent increase tendency in separate brain regions. In cerebrum, only the 3000 ppm group showed a significant increase in alpha-enolase by 27% and creatine kinase-B (CK-B) by 26%. alpha-Enolase and gamma-enolase exhibited a pronounced elevation in cerebellum relative to other brain regions, while beta-S100 protein appeared to be the most markedly altered marker in brainstem. The development of gliosis, which is a frequent phenomenon following CNS damage, is presumed to be responsible for the elevation of glial marker content. Energy metabolism disruption in brain tissues may also bring about the compensatory oversynthesis of glycolytic enzymes such as gamma-enolase, alpha-enolase and CK-B. The dose-dependent alteration patterns following toluene exposure suggest the feasibility of using these brain specific markers to evaluate solvent-induced CNS effects.

Effects of chronic n-hexane exposure on nervous system-specific and muscle-specific proteins

Two kinds of nervous system-specific and muscle-specific proteins, enolase and S-100 protein, were quantitatively determined in peripheral nerves and skeletal muscles of rats chronically exposed to a neurotoxic solvent - n-hexane. Three groups of animals were exposed to n-hexane vapor at three different solvent concentrations (500 ppm, 1200 ppm, 3000 ppm) for 12 h/day, 7 days/week for 16 weeks. The body weight gain and motor nerve conduction velocity (MCV) in exposure groups show progressively concentration-dependent decreases compared to control values. Histopathological examination also demonstrates the degeneration of peripheral nerves in 3000 ppm- and 1200 ppm-exposed rats. The significant decrease in the amount of S-100 protein in peripheral nerves was observed not only in the high level exposure groups (3000 ppm and 1200 ppm), but also in the lowest level group (500 ppm), although the MCV and morphological examination remained unchanged at this level. In addition, the muscle-specific S-100 protein in 3000 ppm exposed rats' soleus also displayed a significant reduction. In contrast to this, however, enolase isozymes were not significantly changed by either dosage level in both nervous tissue and skeletal muscle. The experiment suggests that beta- and alpha-S-100 proteins which are specifically localized in nervous system and muscles, respectively, are more vulnerable than enolase isozymes under treatment with n-hexane, and may possibly serve as a specific indicator to evaluate the neurotoxic effects. Further research would be worthwhile to elucidate the role of the specific S-100 protein in evaluating the neurologic damage induced by various industrial chemicals.

Maternal exposure to 1,1,2-trichloroethylene affects myelin in the hippocampal formation of the developing rat

The effect of 1,1,2-trichloroethylene (TCE), an industrial solvent, on myelin in the dorsal hippocampus of the developing rat was investigated. Rat pups were exposed to TCE via their dams' drinking water while in utero and until they were sacrificed at 21 days of age. Frozen coronal sections through the dorsal hippocampus were stained for the presence of myelin using a modification of the Heidenhain procedure developed for frozen sections. A significant decrease in myelinated fibers was found in the stratum lacunosum-moleculare, an area comprised of distal dendritic profiles of CA1 pyramidal neurons which receive input from the entorhinal cortex. These findings suggest that the reduction in myelin in the hippocampus may be responsible, in part, for behavioral effects observed following TCE exposure.

Long term neurotoxicity of styrene. A quantitative study of glial fibrillary acidic protein (GFA) and S-100

Little information exists about the possible neurotoxicity of styrene. The present study was designed to explore whether long term inhalation exposure (three months) to styrene (90 and 320 ppm) could induce long lasting astroglial alterations in Sprague Dawley rats, traceable four months after exposure ceased. Styrene exposure at 320 ppm induced such alterations as shown by raised concentrations of the glial cell marker, glial fibrillary acidic protein (GFA) in the sensory motor cortex and in the hippocampus. GFA is the structural protein of the astroglial filaments and formation of these filaments has been shown after damage to the central nervous system from any cause. It is concluded that exposure to styrene at moderate exposure levels induces regional, long lasting astroglial reactions that serve as an indicator of solvent induced brain damage.

The S-100 protein in cerebrospinal fluid: a simple ELISA method

A simple ELISA method is described for determinations of S-100 protein concentrations in CSF. The assay has a useful range of 200-3200 pmol/l. The precision of the ELISA was estimated using a pool of CSF. The coefficient of variation was 0.18 within assay, 0.17 between assay and 0.17 between day. The S-100 protein is stable in the CSF as no measurable differences in S-100 concentrations were observed in samples stored at room temperature for 2 days. No correlation between age and S-100 concentration was found when determinations were performed in CSF from neurologically healthy males. Furthermore, no changes of S-100 was observed in a lumbocisternal CSF gradient from patients with normal pressure hydrocephalus. Thus, the described ELISA represents an easy to handle and reliable method, well suited for routine determinations of S-100 protein concentration in the CSF.

Detection limits of different approaches in behavioral teratology, and correlation of effects with neurochemical parameters

Five laboratories collaborated in the evaluation of detection limits of different testing concepts in behavioral teratology. In one laboratory, rat dams were treated by gavage with five doses of methylmercury (0.0, 0.25, 0.05, 0.5, and 5.0 mg/kg/day). The treatment period was restricted to days 6 to 9 of gestation. The usual reproduction parameters were assessed in the dams. The offspring (88-99 per group) were subjected to a routine developmental and behavioral testing battery. After completion of these tests, random samples of the animals were further investigated in four other laboratories using the following techniques: auditory startle habituation, visual discrimination and figure-8 activity monitor; wheel-shaped activity monitor and spatial alternation operant conditioning; two-compartment locomotor activity, passive avoidance and male ultrasonic vocalization during sexual behavior; assays of the weight of different brain areas, their glial fibrillary acidic (GFA) protein and S-100 protein concentration. The following dose-dependent effects were noted in ascending dose sensitivity order: delayed vaginal opening; increased and more variable passiveness in spatial alternation; impaired swimming behavior, increased GFA protein concentration in the cerebellar vermis; increased auditory startle amplitude, decreased intertrial interval pokes in the visual discrimination test, increased percentage of visits in passive area of figure-8 activity monitor, increased path iteration frequencies and decreased local activity in the wheel-shaped activity monitor, decreased locomotor activity in the two-compartment monitor, increased cerebellar vermis weight, and decreased S-100 protein in the hippocampus. Therefore, this study showed comparable sensitivities for the behavioral testing battery, for some automated multiparametric test systems and for the neurochemical assays.

The effects of chronic trichloroethylene exposure on neurobehavioral functioning in the rat

Groups of rats were exposed by inhalation to either clean air (Controls) or trichloroethylene at 500, 1000 or 1500 ppm TCE for 16 hr/day, 5 days/week for 18 weeks. At preselected intervals, animals were evaluated for changes in: spontaneous activity, gripstrength, coordinated hindlimb movement, performance of a discrete-trial operant two-choice visual discrimination task, and peripheral nerve conduction velocity. Compared to Controls, TCE-treated rats showed no significant differences in open field behavior, fore- and hindlimb gripstrength or coordinated movement throughout the exposure period. Peripheral nerve conduction time was also unaffected. In contrast, TCE produced progressively marked changes in the speed and patterning of responding in the two-choice visual discrimination task. Two-choice response latency, for example, demonstrated an approximately four-fold increase (p less than 0.001) in the highest dose group. In addition, a recurrent within-week functional tolerance developed for all TCE-exposed groups. However, tolerance was lost in the TCE 1500 group as exposure became chronic. Finally, following the termination of exposure, there was no carry-over of TCE-related effects on any of the measures and performance quickly returned to baseline levels. This profile of effects argues for a primary involvement of the CNS with chronic TCE exposure and is quite unlike that seen with, e.g., n-hexane and carbon disulfide. Such findings underscore the differences in the effects which can be produced by long-term exposure to organic solvents and emphasize the need for a battery of tests in the evaluation of neurotoxicant-induced changes in nervous system functioning.

Irreversible effects of dichloromethane on the brain after long term exposure: a quantitative study of DNA and the glial cell marker proteins S-100 and GFA

Two astroglial proteins S-100 and GFA, as well as DNA, were quantitatively determined in different regions of the gerbil brain after continuous long term exposure to moderate concentrations of dichloromethane. The intention of the experiment was to expose three groups of animals at three different solvent concentrations (210, 350, or 700 ppm) for three months. Because of the high mortality rate, however, the 700 ppm experiment was terminated after seven weeks. In the 350 ppm experiment half the exposed animals died and the exposure period was terminated after ten weeks. After the exposure period, the surviving gerbils in the 350 ppm exposure group and those from the 210 ppm group were allowed a postexposure solvent free period of four months. After exposure to 350 ppm, increased concentrations of the two astroglial proteins were found in the frontal and sensory motor cerebral cortex, compatible with astrogliosis in these regions. Exposure to 350 ppm and 210 ppm decreased the concentrations of DNA in the hippocampus. Moreover, after exposure at 350 ppm, DNA concentrations were also decreased in the cerebellar hemispheres. These results indicate a decreased cell density in these brain regions, probably due to cell loss. The neurotoxic effects were not found to correlate with the endogenous formation of carbon monoxide.

Membrane lipid changes in organic solvent tolerant neural cells

Although, organic solvents are known to interact with neural membranes and to possess acute anesthetic properties, very little is known about the chronic effects of organic solvents on neural membranes. In the present study lipid compositional changes were examined after chronic exposure to the chlorinated organic solvents, trichloroethylene (TCE) and perchloroethylene (PCE). Animals were exposed continuously in inhalation chambers. Each experimental group had its own control group exposed simultaneously to air under identical conditions. Exposure to these organic solvents had only minor effects on lipid class composition. A tendency towards a decreased cholesterol to phospholipid ratio was observed, whereas the content of cerebrosides was unaffected. However, the proportions of the polyunsaturated fatty acids of ethanolaminephosphoglyceride (EPG) was consistently changed after exposure to either of these solvents for three months at (320 ppm). After longer exposure periods such alterations were observed at even lower solvent concentrations. This change in fatty acid pattern was characterized by an increase in linolenic acid derived fatty acids, with a concomitant decrease in fatty acids of the linolenic acid family. These changes may be an effort to compensate for the increased hydrophobic volume of membranes induced by dissolved solvent molecules. This compensation could be achieved by insertion of less coned lipid components into the membrane. The observed decrease in cholesterol to phospholipid ratio and the increase in the less saturated linoleic acid derived fatty acids could serve this function. Another possibility could be that chlorinated organic solvents interfere with the protein structure of desaturases, resulting in an alteration in the speed of desaturation and a changed fatty acid composition.

Fatty acid composition of ethanolamine phosphoglycerides in different areas of the gerbil brain after chronic exposure to trichloroethylene

Exposure of Mongolian gerbils to trichloroethylene (TCE) (320 ppm) in an inhalation chamber continuously for 3 mo resulted in an altered fatty acid pattern of phospholipid in discrete areas of the brain. Lipids were extracted from four brain regions: the cerebral cortex, the hippocampus, the cerebellar vermis posterior, and the brain stem. No changes induced by TCE were found in lipid class distribution among the different regions examined. Whole brain weights and weights of the dissected pieces were also unchanged. In ethanolamine phosphoglycerides from the cerebral cortex and the hippocampus, a decrease was found among long-chain fatty acids derived from linolenic acid with a corresponding increase of the linoleic acid family. The cerebellar vermis and the brain stem were less affected. Since areas rich in gray matter were affected more than those with a high proportion of white matter, it seems reasonable to assume that the fatty acid alterations of ethanolamine phosphoglycerides occur mainly in the gray matter. Furthermore, we suggest that the alterations can be a compensatory mechanism for the membrane fluidizing properties of TCE.

Long lasting changes in gerbil brain after chronic ethanol exposure: a quantitative study of the glial cell marker S-100 and DNA

Glial S-100 protein, soluble protein, and DNA were quantitatively studied in brains of gerbils chronically exposed to ethanol in a nutritionally complete fluid diet. Eight different brain areas were studied. After exposure to ethanol for 3 months followed by a 4-month post-treatment ethanol-free period, increased amounts of S-100 protein per wet weight were found in the frontal cerebral cortex, the sensory-motor cerebral cortex, the posterior cerebellar vermis, and the brainstem. The increase of S-100 in the posterior cerebellar vermis was paralleled by an increase in DNA per wet weight, which was also increased in the anterior cerebellar vermis. However, a decreased content of DNA was observed in the frontal cerebral cortex, despite the increase of S-100 protein, suggesting a cell loss affecting cells other than astroglial in this area. In the cerebellar vermis, elevated concentrations of soluble proteins per wet weight were found, whereas a decreased amount was found in the anterior cerebellar hemispheres. It is suggested that the S-100 protein acts as a marker for astroglial cell volume and that a concomitant increase of S-100 protein and DNA might indicate an increase in the number of astroglial cells. Thus, our results obtained after ethanol exposure and subsequent ethanol abstinence are compatible with changes consisting of astroglial hypertrophy in the cortex areas and brainstem, as well as astroglial hypertrophy and/or proliferation in the posterior cerebellar vermis, a clear sign of the preceding noxae.

Chronic effects of perchloroethylene on the composition of lipid and acyl groups in cerebral cortex and hippocampus of the gerbil

Continuous exposure of Mongolian gerbils to perchloroethylene (PCE) (120 ppm) for 12 months in an inhalation chamber caused no changes in body or brain weights. The protein content, the concentration of lipid phosphorus or cholesterol were unaltered in the cerebral cortex and hippocampus. However, a small change in the fatty acid pattern of phospholipid was observed. In the phosphatidylethanolamine of cerebral cortex and hippocampus a decrease was found among the long-chain, linolenic acid-derived, fatty acids. The ratio 22:4 (N-6)/22:5 (N-3) was increased, indicating a shift towards the corresponding linoleic acid-derived 22-carbon fatty acids. The observed changes among poly-unsaturated fatty acids are similar to those appearing after peroxidation and either protein or essential fatty acid malnutrition. However, an attractive explanation for the changes is that they represent a response to the fluidizing properties of PCE.

Effects of trichloroethylene inhalation on acid phosphatase in rodent brain

Rats, mice and gerbils were continuously exposed to 150 ppm trichloroethylene (TCE) for 30 days. In all three species, there was a marked increase in liver weight. In mice the weight increased more (86%) than in rats and gerbils (20%). After exposure the activity of acid phosphatase, a lysosomal marker enzyme, was tested in different brain areas, using a system which had a limit of detection of +/- 10-15%. In most areas no significant influence was found. However, in the brain stem of mice and gerbils the phosphatase activity increased by approx. 10%.

Trichloroethylene: effects on body and organ weights in mice, rats and gerbils

The influence of continuous inhalation of 150 ppm trichloroethylene (TCE) on body, liver, spleen, and kidney weights in rats, mice, and mongolian gerbils was tested. An age dependent decrease in body weight gain was observed in female rats exposed to TCE. All 3 species showed liver enlargement caused by the exposure. The effect was much more pronounced in mice, in which the increase was 60--80%, than in rats and gerbils where it was only 20--30%. After the end of the TCE-exposure the liver weights of the mice decreased rapidly. After 5 days of rehabilitation the weight was only 10--20% higher than that of the controls. This difference persisted for at least 25 days. The spleen weight appeared unaffected or somewhat smaller in TCE-exposed animals of all species. An increased kidney weight (15%) was observe din TCE-exposed gerbils. This effect was less pronounced in mice and rats. Effects on the liver have earlier been seen only after exposure to concentrations much higher than that used in the present study. This difference in results is proposed to be due to the different schedules used for the exposure.