Biomedical subjects

H A Tilson

Publications and source records attributed to H A Tilson.

At least 19 recordsLinked to original sources

PubMed2001

Differential patterns of nerve growth factor, brain-derived neurotrophic factor and neurotrophin-3 mRNA and protein levels in developing regions of rat brain.

The present studies were undertaken to characterize the regional and temporal patterns of neurotrophin messenger RNA and protein levels for beta-nerve growth factor, brain-derived neurotrophic factor and neurotrophin-3 in the developing CNS. We have examined the levels of these neurotrophin messenger RNAs with ribonuclease protection assays and corresponding protein levels with enzyme-linked immunosorbent assays in the developing Long-Evans rat hippocampus, neocortex and cerebellum on postnatal days 1, 7, 14, 21, and 92. In addition, immunohistochemistry was used to localize the neurotrophins in these developing brain regions. Results indicated that in neocortex and hippocampus, messenger RNA for both nerve growth factor and brain-derived neurotrophic factor increased in an age-dependent manner, reaching a plateau by postnatal day 14. In the neocortex, nerve growth factor and brain-derived neurotrophic factor protein levels both peaked at postnatal day 14. In hippocampus, nerve growth factor protein peaked at postnatal day 7 while brain-derived neurotrophic factor peaked at postnatal day 14. In cerebellum, nerve growth factor messenger RNA levels were flat, while nerve growth factor protein peaked at postnatal day 7. Brain-derived neurotrophic factor messenger RNA increased in an age-dependent manner while the pattern for its protein levels was mixed. Neurotrophin-3 messeger RNA levels increased in an age-dependent manner in hippocampus, peaked at postnatal day14 in cerebellum, and no changes occurred in neocortex. Neurotrophin-3 protein was at its peak at postnatal day 1 and thereafter decreased at other postnatal days in all three brain regions. Results of neurotrophin immunohistochemistry often paralleled and complemented enzyme-linked immunosorbent assay data, demonstrating specific cell groups containing neurotrophin proteins in these regions. Within each region, patterns with regard to messenger RNA and respective protein levels for each neurotrophin were unique. No consistent relationship between patterns of neurotrophin messenger RNAs and their cognate proteins was observed between regions. The different regional patterns for neurotrophin messengerRNA and protein levels in each brain region indicate that messenger RNA studies of neurotrophin messenger RNA must be augmented by protein determination to fully characterize spatial and temporal neurotrophin distribution.

Aging↗

PubMed2001

Differential effects of two lots of aroclor 1254: congener-specific analysis and neurochemical end points.

Aroclor 1254 is a widely studied commercial polychlorinated biphenyl (PCB) mixture which, by definition, contains 54% chlorine by weight. Recent reports indicate substantial differences in the congener composition among Aroclor lots and hence their biologic effects. We designed the current study to compare the effects of two lots of Aroclor 1254 (lots 6024 and 124-191). We analyzed these two lots for PCB congeners, polychlorinated dibenzofurans (PCDFs), polychlorinated naphthalenes (PCNs), and polychlorinated dibenzodioxins (PCDDs). We used previously established techniques for analyzing intracellular Ca(2+) buffering and protein kinase C (PKC) translocation to test their biologic activity in neuronal preparations. PCB congener-specific analysis indicated that ortho and non-ortho congeners in these two lots varied in their percent contribution. Among all congeners, the percentages of non-ortho congeners (PCBs 77, 81, 126, and 169) were higher in lot 6024 (2.9% of total) than in lot 124-191 (0.02% of total). We detected no dioxins in these two lots (< 2 ppb). Although there are some differences in the congener composition, total PCNs were similar in both lots: 171 ppm in lot 6024 and 155 ppm in lot 124-191. However, total PCDFs were higher in lot 6024 (38.7 ppm) than in lot 124-191 (11.3 ppm). When we tested these two Aroclors on Ca(2+) buffering and PKC translocation in brain preparations, the effects were significantly different. Although lot 124-191 was more potent on PKC translocation than lot 6024, lot 6024 was slightly more active on Ca(2+) buffering than lot 124-191. These effects could not be attributed to the differences in the percentage of non-ortho congeners or PCDFs because they were inactive on these two parameters. The effects could not be attributed to PCNs because the levels were almost similar. The effects seen with two lots of Aroclor 1254 in neuronal cells were also not predicted based on the TCDD toxic equivalents (TEQs), although TEQs predicted the effects on ethoxyresorufin-O-deethylase (EROD) or methoxyresorufin-O-deethylase (MROD) activities. It is possible that the differential effects seen in neuronal cells could be caused by differences in the composition of ortho-congeners in these two mixtures, because PCBs with ortho-lateral substitutions can exhibit different activities on the selected neurochemical end points. Because of these differential effects with different lot numbers, the composition of Aroclor mixtures used in investigations should be disclosed.

Animals↗

PubMed2000

Neurochemical effects of environmental chemicals: in vitro and in vivo correlations on second messenger pathways.

Polychlorinated biphenyls (PCBs) are persistent, bioaccumulative, toxic, and widely distributed environmental chemicals. There is now both epidemiological and experimental evidence that PCBs cause cognitive deficits; however, the underlying cellular or molecular mechanism(s) is not known. We have hypothesized that altered signal transduction/second messenger homeostasis by PCBs may be associated with these effects since second messengers in signal transduction pathways, such as calcium, inositol phosphates (IP), and protein kinase C (PKC), play key roles in neuronal development and their function. In vitro studies using cerebellar granule neurons and isolated organelle preparations indicate that ortho-PCBs increase intracellular free Ca2+ levels by inhibiting microsomal and mitochondrial Ca2+ buffering and the Ca2+ extrusion process. Ortho-PCBs also increase agonist-stimulated IP accumulation and cause PKC translocation at low micromolar concentrations where no cytotoxicity is observed. On the other hand, non-ortho-PCBs are not effective in altering these events. Further SAR studies indicate that congeners with chlorine substitutions favoring non-coplanarity are active in vitro, while congeners favoring coplanarity are relatively inactive. Subsequent in vivo studies have shown that repeated exposure to a PCB mixture, Aroclor 1254, increases PKC translocation and decreases Ca2+ buffering in the brain, similar to in vitro studies. These changes in vivo are associated with elevated levels of non-coplanar ortho-PCB congeners at levels equivalent to 40-50 microM in brain, the concentrations that significantly inhibited second messenger systems in neuronal cultures in vitro. Current research is focusing on PCB-induced alterations in second messenger systems following developmental exposure.

Animals↗

PubMed2000

New horizons: future directions in neurotoxicology.

Neurotoxicology is a relatively young discipline that has undergone significant growth during the last 25 years. During the late 1970s and 1980s, numerous national and international conferences and meetings were devoted to the topic of neurotoxicology, the formation of societies or specialty sections related to neurotoxicology, and the establishment of two independent peer-reviewed journals devoted to neurotoxicology. This decade was also associated with a rapid increase in our knowledge of chemical effects on the structure and function of the nervous system. During the 1990s, regulatory agencies such as the U.S. Environmental Protection Agency accepted neurotoxicology as a crucial end point and neurotoxicity testing and risk assessment guidelines were published. Neurotoxicology has also been accepted at the international level as evidenced by environmental criteria documents published by the International Programme on Chemical Safety and testing guidelines by the Organization of Economic Cooperation and Development. In recent years, there has been increased concern that the etiology of some neurodegenerative diseases may be associated with exposure to neurotoxic agents and that subpopulations of humans such as children and the elderly may be differentially sensitive to neurotoxic exposure. In the future, mechanistic information derived from basic research will be used in the identification and characterization of chemicals with neurotoxic potential.

Environmental Health↗

PubMed1999

Extracellular calcium is required for the polychlorinated biphenyl-induced increase of intracellular free calcium levels in cerebellar granule cell culture.

Recent studies from the laboratory indicate that polychlorinated biphenyl (PCB) congeners can alter signal transduction and calcium homeostasis in neuronal preparations. These effects were more pronounced for the ortho-substituted, non-coplanar congeners, although the mechanisms underlying these effects are not clear. In the present study the time-course and concentration-dependent effects of coplanar and non-coplanar PCBs on intracellular free calcium concentration ([Ca2+]i) in cerebellar granule cell cultures were compared using the fluorescent probe fura-2. The ortho-substituted congeners 2,2'-dichlorobiphenyl (DCB) and 2,2',4,6,6'-pentachlorobiphenyl (PeCB) caused a gradual increase of [Ca2+]i while the non-ortho-substituted congeners 4,4'-DCB and 3,3',4,4',5-PeCB had no effect. The increase of [Ca2+]i produced by 2,2'-DCB was time- and concentration-dependent. Further studies examined possible mechanisms for this rise in [Ca2+]i. In contrast to the muscarinic agonist carbachol, the effects of 2,2'-DCB on [Ca2+]i were not blocked by thapsigargin and required the presence of extracellular calcium. The effects of ortho-substituted PCBs may depend on their ability to inhibit calcium sequestration as 2,2'-DCB significantly inhibited 45Ca2+-uptake by microsomes and mitochondria while 3,3',4,4',5-PeCB had no effect. In addition, 2,2'-DCB significantly increased the binding of [3H]inositol 1,4,5-trisphosphate to receptors on cerebellar microsomes, suggesting another possible mechanism by which ortho-substituted PCBs can mobilize [Ca2+]i. These results show that PCBs increase [Ca2+]i in vitro via a mechanism that requires extracelluar calcium, and support previous structure-activity studies indicating that ortho-substituted PCBs are more potent than non-ortho-substituted PCBs.

Animals↗

PubMed1998

Neurotoxicity of environmental chemicals and their mechanism of action.

Despite a ban on their manufacture in 1977, polychlorinated biphenyls (PCBs) are still found in significant quantities in the environment. Developmental exposure to PCBs and related compounds has been reported to be neurotoxic in human and animals. Research in our laboratory has focused on the possible site(s) and mechanism(s) of PCB-induced developmental neurotoxicity. Recent experiments with rats found that developmental exposure to Aroclor-1254 (ARC) affects the acquisition of a lever press response and produces long-term changes in calcium buffering and protein kinase C (PKC) activity in the brain. In vitro studies in our laboratory have found that ARC increases [3H]phorbol ester binding, an indirect measure of PKC translocation, and inhibits calcium buffering in microsomes and mitochondria. Other experiments indicate that PCB congeners with chlorine substitutions at ortho- or low lateral substitutions are active in vitro, while non-ortho-substituted congeners are less active or inactive. Other research suggests that the lack of coplanarity of the PCB molecule is related to in vitro activity of PCB congeners. These studies indicate that in vivo developmental exposure to PCBs alters behavior and second messenger systems during adulthood, while in vitro experiments indicate that nervous system activity is related to ortho-substituted congeners that tend to be non-coplanar in configuration. Our results are consistent with the hypothesis that developmental neurotoxicity of ARC is due, in part, to the presence of ortho-substituted PCB congeners.

Animals↗

PubMed1998

Gestational exposure to methylmercury alters the developmental pattern of trk-like immunoreactivity in the rat brain and results in cortical dysmorphology.

Nerve growth factor signal transduction mediated through the trk receptor has been implicated in neuronal growth, differentiation, and survival. In this study, we examined the effects of gestational exposure to the developmental neurotoxicant methylmercury (CH3Hg) on the ontogeny of trk-immunoreactivity (IR). Long-Evans dams were dosed on gestational days 6-15 (p.o.) with 0, 1, or 2 mg/kg CH3Hg dissolved in saline. Pups were sacrificed and perfused with buffered paraformaldehyde on postnatal days (PND) 1, 4, 10, 21 and 85. The brains were sectioned sagitally, Nissl-stained or stained immunohistochemically for trk receptors or glial fibrillary acidic protein (GFAP), and examined throughout the medial to lateral extent of the brain. The greatest density of IR in neural cell bodies was seen in the olfactory bulb, hippocampus, cerebral, and cerebellar cortex, striatum, septum, nucleus basalis, inferior colliculus, pons, and brain stem nuclei. trk IR was not limited to nerve cell bodies, with prominent axonal and dendritic staining in the brainstem, neocortex, hippocampus, cerebellum, and olfactory tract. The regional pattern of trk IR varied in an age-dependent manner. In controls, trk-like IR appeared to peak in most regions between PND4-10 and decreased dramatically after PND21. This age-related difference in trk IR was supported by western blot analysis of PND10 and adult neocortex. This reduced and more adult-like pattern of trk IR was apparent on PND21 with some persistent trk-like IR in the olfactory bulb, hippocampus, neocortex, cerebellum and basal forebrain. In contrast to the normal regional patterns of trk IR, CH3Hg produced a dose-related decrease in trk-like IR in the absence of overt maternal toxicity or neonatal toxicity. CH3Hg-induced decreases in trk-like IR were especially apparent during the early postnatal period when trk IR was the greatest. The effects of CH3Hg exposure were restricted regionally, with the largest decrease in trk-like IR apparent in cortical regions, basal forebrain nuclei, and brain stem nuclei. Subsequent to the effects of CH3Hg on cortical trk-like IR were alterations in the development of cortical laminae on PND10 and 21 of neocortex. These alterations were characterized by quantifiable decreases in cell density, cell size and the widths of the layers of posterior neocortex. Not all of the CH3Hg-induced effects were characterized by decreased trk-like IR. Robust increases in trk IR in glial cells in the corpus callosum and brain stem were observed coincident with increased GFAP IR in cells of similar morphology. The present results localize the cellular and regional ontogeny of trk and suggest that developmental exposure to CH3Hg alters the normal ontogeny of this trophic factor receptor which may be associated with the developmental neurotoxicity of this chemical.

Animals↗

PubMed1998

Time course of changes in cholinergic and neurotrophin-related markers after infusion of colchicine into the basal forebrain.

After bilateral infusions of colchicine or vehicle in the rat nucleus basalis magnocellularis, the time course of changes in several cholinergic and neurotrophin-related markers were assessed. Animals were sacrificed at 3, 7, 14, 28, 35 and 84 days post-lesion, and both the NBM and cortical areas were assessed. Sections were stained immunohistochemically for choline acetyltransferase (ChAT) or p140trk (trk) or histochemically for acetylcholinesterase (AChE). ChAT activity and neurotrophin protein levels were assessed regionally. The number of ChAT immunoreactive NBM neuronal profiles decreased beginning 3 days post-lesion and reach maximal loss by 28 days post-lesion, with no recovery. Examination of trk-IR around the NBM revealed a time-dependent decrease in trk-IR of magnocellular neuron and an increase in trk-IR of astrocytes at 14 and 28 days post-lesion. The density of AChE-stained cortical fibers was maximally decreased 3 days post-lesion followed by an increase in fiber staining across the remaining time points. Cortical ChAT activity showed the largest decrease at 7 days followed by recovery 84 days after colchicine infusion. There was an increase in NGF in the parietal cortex after colchicine infusion but no change in BDNF level. These patterns of changes in the cholinergic and neurotrophin-related markers suggest an association between NGF and lesion-induced compensatory responses in the basal forebrain cholinergic system.

Acetylcholinesterase↗

PubMed1998

Repeated exposure of adult rats to Aroclor 1254 causes brain region-specific changes in intracellular Ca2+ buffering and protein kinase C activity in the absence of changes in tyrosine hydroxylase.

Polychlorinated biphenyls (PCBs) are ubiquitous environmental contaminants, some of which may be neurotoxic. In vitro studies from this laboratory indicated that noncoplanar PCBs perturbed intracellular signal transduction mechanisms including Ca2+ homeostasis, receptor-mediated inositol phosphate production, and translocation of protein kinase C (PKC). In the present study, we examined the effects of PCBs in vivo by dosing adult male Long-Evans rats orally with Aroclor 1254 (0, 10, or 30 mg/kg/day; 5 days/week for 4 weeks) in corn oil. At 24 h after the last dose, rats were tested for motor activity in a photocell device for 30 min. Immediately, the rats were euthanized, blood was collected for thyroid hormone analysis, and brains were removed, dissected into regions (cerebellum, frontal cortex, and striatum), and subcellular fractions were obtained for neurochemical analysis. Following Aroclor 1254 treatment, body weight gain in the high-dose group was significantly lower than the control and low-dose groups. Horizontal motor activity was significantly lower in rats dosed with 30 mg/kg Aroclor 1254. Ca2+ buffering by microsomes was significantly lower in all three brain regions from the 30 mg/kg group. In the same dose group, mitochondrial Ca2+ buffering was affected in cerebellum but not in cortex or striatum. Similarly, total cerebellar PKC activity was decreased significantly while membrane-bound PKC activity was significantly elevated at 10 and 30 mg/kg. PKC activity was not altered either in cortex or the striatum. Neurotransmitter levels in striatum or cortex were slightly altered in PCB-exposed rats compared to controls. Furthermore, repeated oral administration of Aroclor 1254 to rats did not significantly alter forebrain tyrosine hydroxylase immunoreactivity or enzymatic activity. Circulating T4 (total and free) concentrations were severely depressed at both doses in Aroclor 1254-exposed rats compared to control rats, suggesting a severe hypothyroid state. These results indicate that (1) in vivo exposure to a PCB mixture can produce changes in second messenger systems that are similar to those observed after in vitro exposure of neuronal cell cultures; (2) second messenger systems seem to be more sensitive than alterations in neurotransmitter levels or tyrosine hydroxylase involved in dopamine synthesis during repeated exposure to PCBs; and (3) the observed motor activity changes were independent of changes in striatal dopamine levels.

Animals↗

PubMed1998

Congener-specific distribution of polychlorinated biphenyls in brain regions, blood, liver, and fat of adult rats following repeated exposure to Aroclor 1254.

Our previous in vitro studies with both isolated organelles and primary neuronal cell cultures found that intracellular signal transduction can be perturbed by some noncoplanar PCBs at exposure levels of </=10 microM. However, it is not clear whether such concentrations are achievable in brain in vivo. Also, the pattern of congener disposition and quantities of the PCB accumulation in tissues of animals exposed to commercial PCB mixtures is not well studied. In the present study, we have conducted PCB congener-specific analysis in different brain regions, liver, blood, and fat of adult male Long-Evans rats dosed orally with Aroclor 1254 (0 or 30 mg/kg/day; once per day, 5 days/week for 4 weeks) in corn oil. Twenty-four hours after the last dose, rats were euthanized, and the brains were removed and dissected to obtain cerebellum, frontal cortex, and striatum. Liver, blood, and fat samples were also collected at the same time. Congener-specific analysis of PCBs was performed by high-resolution gas chromatography with electron capture detection. While PCB concentrations in control rat brain regions were less than 0.02 ppm, total PCB congeners in treated animals accumulated to much higher levels. Total levels in the frontal cortex, cerebellum, and striatum were 15.1 +/- 0.3, 13.1 +/- 1.7, and 8.2 +/- 2.6 ppm, respectively. The levels of PCBs in the fat, liver, and blood were 0.041, 0.002, and 0.001 ppm in control rats and 552, 38.3, and 1.6 ppm in treated rats, respectively. In addition to the differential total uptake between tissues, there was differential accumulation of PCBs with respect to the number of chlorines. In all the tissues, the more lightly chlorinated (tetra- and penta-) congeners accumulated less than their respective proportions in the parent Aroclor 1254 mixture. On the other hand, heavily chlorinated (hexa- to nona-) congeners accumulated more than the proportion of these congeners found in Aroclor 1254 mixture. This shift toward accumulation of heavily chlorinated congeners seems to be more pronounced in the brain than liver and fat. Predominant congeners (5-32% of total PCBs) detected in different brain regions, blood, liver, and fat are: 2,3,3',4',5,6- (no. 163) + 2,2',3,4,4',5- (no. 138) (coeluted); 2,2',4,4',5,5'- (no. 153) + 2, 2',3,3',4,6'- (no. 132) (coeluted); 2,3,3',4,4',5- (no. 156) + 2,2', 3,3',4,4',6- (no. 171) (coeluted); 2,3',4,4',5- (no. 118); 2,2',4,4', 5-(no. 99); and 2,3,3',4,4'- (no. 105). These congeners together accounted for about two thirds of the total PCB load in brain. All these predominant congeners are ortho-substituted and therefore are noncoplanar in nature. The total PCB concentrations accumulated in brain were as high as 50 microM (based on average molecular weight of 326.4 for Aroclor 1254) and, at these concentrations, intracellular second messengers were significantly affected in neuronal cultures and brain homogenate preparations in vitro. These results indicate that concentrations that altered Ca2+ disposition and second messenger systems in vitro are achievable in brain in vivo following repeated exposure.

Adipose Tissue↗

PubMed1998

Developmental neurotoxicology of endocrine disruptors and pesticides: identification of information gaps and research needs.

There is increasing evidence that some environmental chemicals can interrupt neurodevelopmental processes during critical periods of development, resulting in effects on sensory, motor, and cognitive function. It is now generally accepted that developing organisms are differentially sensitive to chemical exposure because of toxicokinetic and/or toxicodynamic factors. Regulatory mechanisms have been implemented to protect humans from over- or inappropriate exposures to environmental chemicals. Current regulatory practices, however, may be insufficient because of the possibility that some environmental chemicals interfere with endocrine function at key periods of neurodevelopment. In addition, a recent National Research Council (NRC) report on pesticide contamination in the diets of infants and children concluded that current regulatory practices may not sufficiently protect infants and children from the risk of pesticide exposure. The NRC report indicates that regulatory agencies might underestimate the actual exposure of infants and children to pesticides and rely too heavily on data from adults in the risk assessment of pesticides. Consideration of endocrine-disrupting chemicals and the differential susceptibility of infants and children has led to identification of a number of information gaps and research needs that should be addressed in order to improve future risk assessments for these chemicals.

Adult↗

PubMed1998

In vitro techniques for the assessment of neurotoxicity.

Risk assessment is a process often divided into the following steps: a) hazard identification, b) dose-response assessment, c) exposure assessment, and d) risk characterization. Regulatory toxicity studies usually are aimed at providing data for the first two steps. Human case reports, environmental research, and in vitro studies may also be used to identify or to further characterize a toxic hazard. In this report the strengths and limitations of in vitro techniques are discussed in light of their usefulness to identify neurotoxic hazards, as well as for the subsequent dose-response assessment. Because of the complexity of the nervous system, multiple functions of individual cells, and our limited knowledge of biochemical processes involved in neurotoxicity, it is not known how well any in vitro system would recapitulate the in vivo system. Thus, it would be difficult to design an in vitro test battery to replace in vivo test systems. In vitro systems are well suited to the study of biological processes in a more isolated context and have been most successfully used to elucidate mechanisms of toxicity, identify target cells of neurotoxicity, and delineate the development and intricate cellular changes induced by neurotoxicants. Both biochemical and morphological end points can be used, but many of the end points used can be altered by pharmacological actions as well as toxicity. Therefore, for many of these end points it is difficult or impossible to set a criterion that allows one to differentiate between a pharmacological and a neurotoxic effect. For the process of risk assessment such a discrimination is central. Therefore, end points used to determine potential neurotoxicity of a compound have to be carefully selected and evaluated with respect to their potential to discriminate between an adverse neurotoxic effect and a pharmacologic effect. It is obvious that for in vitro neurotoxicity studies the primary end points that can be used are those affected through specific mechanisms of neurotoxicity. For example, in vitro systems may be useful for certain structurally defined compounds and mechanisms of toxicity, such as organophosphorus compounds and delayed neuropathy, for which target cells and the biochemical processes involved in the neurotoxicity are well known. For other compounds and the different types of neurotoxicity, a mechanism of toxicity needs to be identified first. Once identified, by either in vivo or in vitro methods, a system can be developed to detect and to evaluate predictive ability for the type of in vivo neurotoxicity produced. Therefore, in vitro tests have their greatest potential in providing information on basic mechanistic processes in order to refine specific experimental questions to be addressed in the whole animal.

Animals↗

PubMed1997

Effects of polychlorinated biphenyls (PCBs) on brain tyrosine hydroxylase activity and dopamine synthesis in rats.

Literature reports suggest that polychlorinated biphenyls (PCBs) may alter dopaminergic neurotransmission in mammalian forebrain. In vitro, PCBs can decrease dopamine levels in PC 12 cells and studies of the structure-activity relationship (SAR) indicate that ortho-substituted (non-coplanar) PCB congeners are more active than para-substituted (coplanar) congeners. This report tested the hypothesis that ortho-substituted PCBs can selectively (vs para-substituted congeners) decrease dopamine synthesis in mammalian forebrain by inhibiting the activity of tyrosine hydroxylase, the rate-limiting enzyme in dopamine biosynthesis. In vitro effects of individual PCB congeners on activity of striatal tyrosine hydroxylase from two different rat strains were assessed. It was found that certain ortho-substituted PCB congeners (e.g., 2,2'-DCB) can inhibit tyrosine hydroxylase activity and dopamine synthesis by nearly 40% in minces of corpus striatum prepared from Sprague-Dawley and Long-Evans hooded rats. Comparatively, the ortho, meta-substituted PCB congener 2,2',5,5'-TeCB inhibited tyrosine hydroxylase activity only in striatal minces obtained from Sprague-Dawley rats, suggesting that genetic factors may influence the susceptibility of mammals to effects of PCBs that compromise brain dopamine synthesis. The PCB-induced inhibition of tyrosine hydroxylase activity in mammalian forebrain observed here appears to occur through indirect and as yet unknown mechanisms.

Animals↗

PubMed1997

Effects of acute and repeated exposures to Aroclor 1254 in adult rats: motor activity and flavor aversion conditioning.

While considerable research has focused on the neurotoxicity of developmental exposures to polychlorinated biphenyls, including Aroclor 1254, relatively little is known about exposures in adult animals. This study investigated the behavioral effects of acute and repeated Aroclor 1254 exposures to adult rats on motor activity and flavor aversion conditioning. Male Long-Evans rats (60 days old) were tested for motor activity in a photocell device after acute (0, 100, 300, or 1000 mg/kg, p.o.) or repeated (0, 1, 3, 10, 30 or 100 mg/kg/day, po, 5 days/week for 4 to 6 weeks exposure to Aroclor 1254. Motor activity was decreased dose-dependently at doses of 300 mg/kg or more after acute exposure. Severe body weight loss and deaths occurred at 1000 mg/kg. Recovery of activity occurred over 9 weeks but was incomplete. After repeated exposure, motor activity was decreased dose-dependently at doses of 30 mg/kg or more, and severe weight loss and deaths occurred at 100 mg/kg. In contrast to acute exposure, complete recovery of activity occurred 3 weeks after exposure. Additional rats were water deprived (30 min/day) and received acute po administration of Aroclor 1254 (0, 10, 15, 25, 30, 100, or 300 mg/kg) shortly after consuming a saccharin solution. Three days later they were given the choice between consuming saccharin or water, and saccharin preferences were recorded. Saccharin preference was decreased at doses of 25 mg/kg or more. Additional experiments determined the effect of repeated saccharin-Aroclor 1254 pairings (0, 3.75, 7.5, or 15 mg/kg/day, 14 days) followed by a choice test 1 day after the last dose. Repeated exposure to 15 mg/kg produced robust flavor aversion conditioning. Repeated exposure to 7.5 mg/kg produced flavor aversion conditioning in four of 12 rats. These results demonstrate that Aroclor 1254 causes hypoactivity and flavor aversions in adult rats; the no observable effect level (NOEL) for motor activity was 100 mg/kg for acute exposure and 10 mg/kg for repeated exposure for a period of up to 6 weeks. The acute NOEL for flavor aversion conditioning was 15 mg/kg while the repeated NOEL was 7.5 mg/kg.

Animals↗

PubMed1997

EPA's neurotoxicity risk assessment guidelines.

The proposed Neurotoxicity Risk Assessment Guidelines (U.S. EPA, 1995c Fed. Reg. 60(192), 52032-52056) of the U.S. Environmental Protection Agency (EPA) were the subject of a workshop at the 1997 Meeting of the Society of Toxicology. The workshop considered the role of guidelines in the risk assessment process, the primary features, scientific basis, and implications of the guidelines for EPA program offices, as well as for industrial neurotoxicologists from the perspectives of both pesticides and toxic substances regulation. The U.S. National Academy of Sciences (NAS, 1983, Risk Assessment in the Federal Government: Managing the Process) established a framework for distinguishing risk management from risk assessment, the latter being the result of integrating hazard identification, hazard characterization, and exposure assessment data. The guidelines are intended to establish operating principles that will be used when examining data in a risk assessment context. The proposed neurotoxicity risk assessment guidelines provide a conceptual framework for deciding whether or not a chemically induced effect can be considered to be evidence of neurotoxicity. Topics in the proposed guidelines include structural and functional effects, dose-response and -duration considerations, and relationships between effects. Among the issues that must be considered are the multiplicity of chemical effects, the levels of biological organization in the nervous system, and the tests, measurements, and protocols used. Judgment of the adversity of an effect depends heavily on the amount and types of data available. The attribution of a chemically induced effect to an action on the nervous system depends on several factors such as the quality of the study, the nature of the outcome, dose-response and time-response relationships, and the possible involvement of nonneural factors. The guidelines will also serve as a reference for those conducting neurotoxicity testing, as well as establish a consistent approach to neurotoxicity risk assessment by regulators. Extending this approach through international harmonization would be advantageous to the development of products for a worldwide market. Thus, both risk assessors and regulated industries have a large stake in the guidelines to provide a framework that will lead to accurate risk assessment decisions.

Data Collection↗

PubMed1997

Empirical modeling of an in vitro activity of polychlorinated biphenyl congeners and mixtures.

The goal of this research is to predict an in vitro activity of polychlorinated biphenyl (PCB) congeners and their mixtures and to describe the relationship between this activity and chemical structure. The test system used multiple PCB concentrations on each cell culture plate in a repeated measures design, which improved precision for comparing between concentration levels. A weighted regression that accounted for this experimental design feature was used in fitting a nonlinear dose-response exponential model to the PCB concentration-activity data from an in vitro test system in which 3H-phorbol ester binding was measured in cerebellar granule cells exposed to different PCB congeners to test for their effects on protein kinase C translocation. The model allowed for the minimum level to be less than control, a common slope, and the estimation of the log of the concentration that produces an activity 50% above the control activity (E50) for 36 congeners and 3 commercial mixtures. Next, a weighted logistic regression using a second order response model in the variables Clortho, Clpara, and Clmeta was used to relate the estimated log E50s to indicators of chemical structure. This model was preferred over models that might seem more mechanistically based because in internal validation, it attained a smaller PRESS statistic (the sum of squares between all observed and predicted observations) than other models. Evidently, this second order model makes more efficient use of parameters than other models considered. Plots of the predictions of the logistic second order response model versus log Kow confirm the usual pattern that congeners with intermediate levels of log Kow are the more active. The data of three commercial mixtures were included in this regression by assuming a common combination index (ratio of observed E50 to predicted E50, assuming dose addition). The logistic model suggests that congeners with one, two, or three chlorine substitutions at the ortho position are more active than other congeners. Also, congeners with log Kow between 5.2 and 6.6 are generally more active. The estimated combination index indicated that the joint action of PCB congeners in the three commercial mixtures was less than dose additive. The error sum of squares was significantly large, which may indicate a lack of fit of the logistic model. Empirical Bayes estimates (EBE) are weighted averages of model predictions and observations of E50s and can be better estimates than the fitted model when there is a lack of fit. The PRESS statistic for the EBE indicated larger prediction error than for the logistic model, but the EBE provided better estimates of commercial mixture E50s based on dose addition. This may indicate that the logistic model is not incorporating all the information in the single congener data needed to predict mixtures.

Animals↗

PubMed1997

The workshop on endocrine disrupter research needs: a report.

On April 10-13, 1995 the US EPA sponsored a workshop to develop research needs for endocrine disrupters. Participants were assigned to discussion groups for health effects issues and risk assessment methodologies. The neurotoxicology workgroup identified several chemicals including the PCBs and dioxins that affect nervous system function possibly by acting on the endocrine system during development. The study of endocrine disrupter is confounded by a number of uncertainties, including the presence of chemical mixtures in the environment unclear exposure parameters, poorly understood mechanisms of action, poor dose-response characterization, and uncertain animal-to-human extrapolation. The working group proposed a research strategy to address these uncertainties, which includes initial identification of effects of concern to human and/or wildlife populations and determining whether those effects can be associated with exposure to specific chemicals in the environment and neuroendocrine disruption. Once a problem chemical has been identified and the exposure conditions established, hypothesis-driven research to determine mechanism of action could proceed.

Endocrine System Diseases↗

PubMed1997

Structure-activity relationships of potentially neurotoxic PCB congeners in the rat.

We have explored the effects of PCBs on Ca(2+)-homeostasis and inositol phosphates in an attempt to understand cellular mechanism(s) for neurotoxicity of PCBs. The selected prototypic congeners have non-dioxin-like (2,2'-dichlorobiphenyl; 2,2'-DCB; IUPAC # 4; ortho-substituted) and dioxin-like (3,3',4,4',5-pentachlorobiphenyl; 3,3',4,4',5-PeCB; IUPAC # 126; non-ortho substituted) properties. The hypothesis is that some PCBs in vitro alter Ca(2+)-homeostasis and interfere with intracellular second messengers. One of the consequences of this perturbation is protein kinase C (PKC) translocation, and these events could lead to cytotoxicity. Our results indicate that the non-dioxin like PCB (ortho-substituted one) is active in vitro and perturbed signal transduction mechanism including Ca(2+)-homeostasis and PKC translocation. The effects were seen at relatively low concentrations (5-50 microM), whereas higher concentrations (> 200 microM) were required to produce cytotoxicity. Results from SAR, in general, indicate that congeners with chlorine substitutions at ortho-position or low lateral substitutions (mostly meta-) are active in vitro where as non-ortho congeners are inactive. In summary, these results indicate that low lateral substitution (especially without para-substitution that favor coplanarity) or high lateral content in the presence of ortho-substitution (to hinder coplanarity) may be the most critical structural requirement underlying the activity of PCB congeners in vitro. Additional experiments with polychlorinated diphenyl ethers (PCDEs) and their analogs, where coplanarity is difficult regardless of degree and pattern of chlorination, provided important information supporting our hypothesis that coplanarity plays a key role in the activity of PCBs in vitro. For example, a PCB congener with 3,3',4,4'-chlorine substitutions is not active whereas a PCDE with the same chlorine substitutions is active. Similarity, 4,4'-DCB is not active whereas PCDE with 4,4'-substitutions is active. One major structural difference in PCDE when compared to the corresponding PCB is non-coplanarity. The PCBs compared here are coplanar and not active, whereas PCDEs are non-coplanar and active in vitro in neuronal preparations. Molecular mechanics calculations and conformational searches confirmed the extent of coplanarity among PCBs and PCDEs. Non-ortho PCBs are more coplanar in nature when compared to ortho-PCBs and PCDEs. These results demonstrate that the extent of coplanarity of certain chlorinated aromatic hydrocarbons can affect their potency in vitro, and ortho-substitutions on the biphenyl, which increase non-coplanarity, are characteristics of the most active PCB congeners.

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