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Biomedical subjects

R F Seegal

Publications and source records attributed to R F Seegal.

At least 19 recordsLinked to original sources

Spatial reversal learning in Aroclor 1254-exposed rats: sex-specific deficits in associative ability and inhibitory control.

Polychlorinated biphenyls (PCBs) are ubiquitous environmental contaminants that have been associated with cognitive deficits in children exposed in utero. Cognitive deficits due to PCB exposure have also been documented in animal models, but the underlying behavioral mechanisms responsible for those deficits remain to be elucidated. The current study examined the effects of gestational and lactational exposure to PCBs on spatial discrimination-reversal learning (spatial RL) in rats using standard two-lever operant testing chambers. Pregnant Long-Evans rats (10/dose) received either 0 or 6 mg/kg Aroclor 1254 (A1254) po in corn oil from gestational day 6 to postnatal day 21. One male and one female from each litter were tested on spatial RL beginning at 190-220 days of age. Animals were reinforced with a 45-mg food pellet for pressing the lever associated with the correct spatial location (either left or right). After reaching 85% correct performance for 2 consecutive days, the opposite spatial location was reinforced. Five of these position reversals were given. Male rats exposed to A1254 made significantly more total errors (121.6 +/- 12.5) on the first reversal than controls (90.7 +/- 5.8). In contrast, female rats exposed to A1254 exhibited deficits on the fourth and fifth reversals (23.6 +/- 4.2, 17.0 +/- 2.8 and 36.7 +/- 4.7, 26.8 +/- 2.5 for control and exposed animals, respectively). Response-pattern analyses in the A1254-exposed male and female rats revealed fundamental differences in the underlying behavioral mechanisms responsible for the deficits. A1254-exposed males exhibited an increased tendency to incorrectly respond to the previously correct stimulus (i.e., perseverate) following a reversal while A1254-exposed females exhibited impairments in their ability to make new associations with a reinforced spatial location (i.e., associative deficit). These data provide new insights into the underlying behavioral mechanisms that may be responsible for the spatial learning deficits observed in PCB-exposed rodents and monkeys.

Analysis of Variance↗

Early development of the serotonergic and dopaminergic nervous system in Spisula solidissima (surf clam) larvae.

We have defined the development of the serotonergic and dopaminergic components of the central nervous system in the early Spisula solidissima (surf clam) embryo using HPLC and immunocytochemistry. HPLC analysis reveals norepinephrine, dopamine, and serotonin are present at 24 h post-fertilization. Immunocytochemistry shows that the serotonergic nervous system emerges during the late trochophore stage with the development of a single serotonergic cell, C/A1, in the cerebral/apical ganglion. After 48 h, a second serotonergic cell forms, C/A2, which is connected to C/A1 by two serotonergic processes, and a single serotonergic cell emerges in the visceral ganglion, V1. At 72 h, a new serotonergic cell body develops in the cerebral/apical ganglion, C/A3. After 96 h, the cerebral/apical ganglion and visceral ganglion are connected by a serotonergic process. Expression of the dopamine receptor, D2, begins by 24 h with a generalized expression in the region of the developing gut. D2 expression in the gut ceases by 48 h. At 48 h, a network of fibers forms dorsolateral to the mouth. By 72 h, D2 expressing projections emerge from this network.

Animals↗

Polychlorinated biphenyls and methylmercury alter intracellular calcium concentrations in rat cerebellar granule cells.

Assessments of the effects of exposure of human populations to complex environmental contaminants, such as those found in contaminated fish, necessitate the investigation of contaminant interactions. We have recently demonstrated that polychlorinated biphenyls (PCBs) and methylmercury (MeHg) synergistically reduce rat brain striatal slice dopamine (DA) and increase media DA concentrations in vitro. To better understand the mechanism(s) by which these effects occur we examined the effects of these two contaminants, either alone or in combination, on intracellular calcium concentrations ([Ca2+]) in rat cerebellar granule cells using flow cytometry. Exposure of granule cells to either 2,2'-dichlorobiphenyl (2,2'-DCB) or MeHg dose-dependently increased [Ca2+]i. Granule cells exposed to 1.5 microM MeHg and 2.5 or 5.0 microM 2,2'-DCB showed synergistic increases in [Ca2+]i which were greatest at exposure times of 5 and 10 min. Higher dose combinations, including 2.0 microM MeHg and 10 or 20 microM 2,2'-DCB, or longer duration of exposure to lower concentrations of contaminant mixtures, reduced [Ca2+]i in the granule cells compared to elevations seen following exposure to MeHg only, suggesting a dose-dependent antagonism between PCBs and MeHg. These data provide evidence for the synergistic and antagonistic interactions of PCBs and MeHg at the level of [Ca2+]i regulation that may ultimately lead to alterations in cellular function, including changes in dopamine regulation.

Animals↗

Differential immune responses in mice with left- and right-turning preference.

Humoral and cell-mediated immune responses of inbred BALB/c male mice were assayed for differential reactivities associated with behavioral sidedness, which was evaluated by spontaneous rotational behavior in a circular cage model system. Mice with left-turning preference had lower in vivo primary IgM and IgG anti-Keyhole Limpet Hemocyanin (KLH) antibody responses, delayed-type hypersensitivity (DTH) responses, and host-resistance against the intracellular bacteria, Listeria monocytogenes, than mice with right-turning preference. The only immune parameter not shown to be associated with turning preference was the secondary humoral immune response to KLH. The weak innate immune response of left-turners for clearance of Listeria showed close intercorrelation with elevated serum IL-6 levels. Serum corticosterone and splenic norepinephrine levels were differentially increased and decreased by infection, respectively. We suggest that the observed differential immune reactivities of individual animals with same age, gender, and genetic background are associated with functional asymmetries within the brain, that the hypothalamic-pituitary-adrenal (HPA) axis and sympathetic innervation are involved in the regulatory brain: immune interconnection after infection, and that the HPA axis and sympathetic nervous system are involved in the brain laterality effects on immune responses.

Adjuvants, Immunologic↗

2,2',6,6'-Tetrachlorobiphenyl is estrogenic in vitro and in vivo.

Polychlorinated biphenyls (PCBs) are ubiquitous environmental contaminants whose effects on biological systems depend on the number of and the positions of the chlorine substitutions. In the present study we examined the estrogenicity of the fully ortho-substituted PCB, 2,2',6,6'-tetrachlorobiphenyl (2,2',6,6'-TeCB). This PCB was chosen as the prototypical ortho-substituted PCB to test the hypothesis that ortho-substitution of a PCB with no para- or meta-chlorine-substitutions results in enhanced estrogenic activity. The results indicate that 2,2',6,6'-TeCB is estrogenic both in vitro, in the MCF-7 cell focus assay, and in vivo, in the rat uterotropic assay. The estrogenic activity elicited by the addition of 5 microM 2,2',6,6'-TeCB to the medium of MCF-7 cultures was inhibited by the estrogen receptor (ER) antagonist, LY156758, suggesting that 2,2',6,6'-TeCB or a metabolite is acting through an ER-dependent mechanism. Results from competitive binding assays using recombinant human (rh) ER indicate that 2,2',6,6'-TeCB does not bind rhERalpha or rhERbeta. A metabolite of 2,2',6,6'-TeCB, 2,2',6,6'-tetrachloro-4-biphenylol (4-OH-2,6,2',6'-TCB), does bind rhERalpha and rhERbeta and is also 10-fold more estrogenic than 2,2',6,6'-TeCB in the MCF-7 focus assay; however, this metabolite is not detected in the medium of MCF-7 cultures exposed to 2,2',6,6'-TeCB. Taken together, the results suggest that the estrogenicity observed in human breast cancer cells and the rat uterus may be due to 1) an undetected metabolite of 2,2',6,6'-TeCB binding to the ER, 2) 2,2',6,6'-TeCB binding directly to a novel form of the ER, or 3) an unknown mechanism involving the ER.

Animals↗

Are PCBs the major neurotoxicant in Great Lakes salmon?

Epidemiological studies have demonstrated an association between consumption, by women, of contaminated Great Lakes salmon and deficits in cognitive performance in the children of these women. Although significant statistical associations between polychlorinated biphenyl (PCB) body burdens and these negative outcomes suggest that PCBs may be responsible, the fetus and neonate are also exposed to other fish-borne neurotoxicants. In this manuscript we present data from two developmental studies that support the hypothesis that PCBs may serve either as a marker for other contaminants that are responsible for the observed effects, or that other contaminants present in the fish interact synergistically with the PCBs to produce the observed neurotoxicity. In the first study we demonstrated that exposure of rats to diets containing lyophilized Great Lakes salmon, resulting in exposure to as little as 13.9 micrograms/(kg small middle dotday) of total PCBs, induced significant reductions in regional brain dopamine (DA) concentrations. In the second study, we demonstrated that exposure of rats to the ortho-substituted PCB congener (2,4,2', 4'-tetrachloro- biphenyl) at 1, 10 or 20 mg/(kg small middle dotday) also induced significant reductions in DA concentrations in the same brain regions although only at the two highest doses-levels at least 100-fold higher than seen in the first study. On the basis of these developmental neurochemical studies we suggest that the reported cognitive deficits in children exposed in utero and during lactation to fish-borne contaminants may be due either to contaminants other than PCBs or to complex interactions between PCBs and other neurotoxicants present in the fish.

Animals↗

Polychlorinated biphenyls and methylmercury act synergistically to reduce rat brain dopamine content in vitro.

Consumption of contaminated Great Lakes fish by pregnant women is associated with decreased birth weight and deficits in cognitive function in their infants and children. These fish contain many known and suspected anthropogenic neurotoxicants, making it difficult to determine which contaminant(s) are responsible for the observed deficits. We have undertaken a series of experiments to determine the relevant toxicants by comparing the neurotoxic effects of two of these contaminants--polychlorinated biphenyls (PCBs) and methylmercury (MeHg)--both of which are recognized neurotoxicants. Striatal punches obtained from adult rat brain were exposed to PCBs only, MeHg only, or the two in combination, and tissue and media concentrations of dopamine (DA) and its metabolites were determined by high performance liquid chromatography. Exposure to PCBs only reduced tissue DA and elevated media DA in a dose-dependent fashion. Exposure to MeHg only did not significantly affect either measure. However, when striatal punches were simultaneously exposed to PCBs and MeHg, there were significantly greater decreases in tissue DA concentrations and elevations in media DA than those caused by PCBs only, in the absence of changes in media lactate dehydrogenase concentrations. Elevations in both tissue and media 3, 4-dihydroxyphenylacetic acid concentrations were also observed. We suggest that the significant interactions between these two toxicants may be due to a common site of action (i.e., toxicant-induced increases in intracellular calcium and changes in second messenger systems) that influences DA function. The synergism between these contaminants suggests that future revisions of fish-consumption guidelines should consider contaminant interactions.

Animals↗

Neurobehavioral effects of chronic ingestion of Great Lakes chinook salmon.

Cross-generational chronic feeding of either a 5 or a 20% lyophilized Lake Huron (LH) or Lake Ontario (LO) chinook salmon diet to rats caused no observable effects on many behavioral dimensions including activity, exploration, sensorimotor function, and stereotypy. As assessed by the Morris water maze and the radial arm maze, there was no diet-induced impairment of spatial learning or long-term memory. There was no evidence that the fish diets caused an exaggerated response to food reward reduction as had been observed previously for rats fed Oswego area Lake Ontario salmon. Effects of the fish diets with the exception of one statistically significant but probably meaningless effect on the Morris water maze for females were found only for male rats and only for males who ate the 20% diet. F1 male rats were reluctant to traverse a runway for a single pellet reward. Performance of the reference/working memory version of the radial arm maze was affected for the F1 LO-20 rats and for the F2 LH-20 rats. Until further research is conducted it would be unwise to ignore indications that male rats may show some effect of chronic consumption of the highest concentration of these diets, particularly on tasks that require intact frontocortical dopamine function.

Analysis of Variance↗

Neurochemical effects of consumption of Great Lakes salmon by rats.

This study, part of a larger project to determine the health consequences of both perinatal and adult exposure to contaminated salmon from the Great Lakes, determined the neurochemical effects of exposure of rats to chow adulterated with lyophilized salmon fillets. Concentrations of biogenic amines, their metabolites, and choline acetyltransferase (ChAT) were determined in the frontal cortex (FC), nucleus accumbens, caudate nucleus (CN), hippocampus (HC), and substantia nigra (SN) of adult rats who had been exposed, both perinatally and as adults, to standard rat chow adulterated with either 5 or 20% (w/w) lyophilized fillets from either Lake Huron (LH) or Lake Ontario (LO) salmon. Dopamine (DA) concentrations in the FC were significantly decreased following exposure to both 20% fish diets. CN DA concentrations were significantly reduced in rats exposed to all diets, while SN DA was decreased only in the LO20-fed animals. SN norepinephrine concentrations were reduced in all groups except for the LO5-fed rats. 3,4-Dihydroxyphenylacetic acid (DOPAC) concentrations in the FC were significantly increased in the LH20 and LO5 groups, while CN DOPAC concentrations were reduced in LH20, LO5, and LO20 animals. 5-Hydroxyindoleacetic acid concentrations were reduced in the FC and CN of all animals exposed to diets adulterated with Great Lakes salmon. ChAT concentrations were unaffected in rats exposed to any of the adulterated diets. The significant reductions in DA, particularly in the FC and CN, suggest that either fish-borne contaminants or consumption of fish, per se, may affect behaviors that require inhibition of normal responding. We conclude that consumption of contaminated fish from the Great Lakes may result in sufficient reductions in biogenic amine function to result in significant deficits in important behavioral functions in the rat and, by inference, in the perinatally exposed human.

Animal Feed↗

Symposium overview: toxicity of non-coplanar PCBs.

Research into the mechanism of toxicity of PCBs has focused on the Ah receptor. However, it is becoming increasingly clear that certain ortho-chlorine-substituted, non-coplanar PCB congeners having low affinity for the Ah receptor exhibit important biological activities. Actions of non-coplanar PCB congeners in a variety of biological systems have been discovered and the mechanisms for these effects are being elucidated. The objectives of this symposium are to examine the state of knowledge concerning the mechanisms of toxic action of non-coplanar PCBs and to identify similarities and differences using a variety of biological systems. Effects to be considered will include: neurotoxicity, estrogenicity, insulin release, neutrophil function, calcium regulation, and relevant signal transduction systems. Finally, the symposium addresses the need to consider non-coplanar congeners within the context of risk assessment. The use of Ah-receptor binding and its associated biological effects to assess the total toxicity of PCBs may no longer be defensible because of the actions produced by non-coplanar congeners. This symposium provides documentation for that conclusion and focuses attention on emerging mechanisms of PCB action that have received relatively little attention to date. The topics presented should be of interest to toxicologists interested in mechanisms of action, in PCB risk assessment, and in regulatory toxicology.

Animals↗

Subchronic toxicity of 2,2',3,3',4,4'-hexachlorobiphenyl in rats.

The subchronic toxicity of 2,2',3,3',4,4'-hexachlorobiphenyl (PCB 128) was investigated in rats following dietary exposure at 0, 0.05, 0.5, 5, or 50 ppm for 13 wk. The growth rate was not affected by treatment and no apparent clinical signs of toxicity were observed. There was a significant increase in liver weight in the 50 ppm females. The liver ethoxyresorufin deethylase (EROD) activity was increased by five- and fourfold in the highest dose males and females, respectively, while aminopyrine demethylase (ADPM) activity was significantly increased only in the highest dose females. Liver vitamin A was significantly reduced in the highest dose females. No other biochemical or hematological effects were observed. Treatment-related histopathological changes were seen in the thyroid and liver, and to a lesser extent in the bone marrow and thymus. Residue data showed a dose-dependent accumulation of PCB 128 in the following tissues: fat, liver, kidney, brain, spleen, and serum, with the highest concentration being found in fat followed by liver and kidney. Based on these data, the no-observable-adverse-effect level of PCB 128 was judged to be 0.5 ppm in diet or 42 micrograms/kg body weight.

Adipose Tissue↗

Effects of in utero and lactational exposure of the laboratory rat to 2,4,2',4'- and 3,4,3',4'-tetrachlorobiphenyl on dopamine function.

Offspring of Sprague-Dawley derived dams were exposed to either 2,4, 2',4'-tetrachlorobiphenyl (TCB) (1, 10, or 20 mg/(kg.day)) or 3,4,3', 4'-TCB (0.1 or 1 mg/(kg.day)) from gestational Day 6 through weaning by providing the dams with cookies adulterated with the appropriate amount and type of PCB. Male and female offspring were sacrificed on postnatal Days 35, 60, and 90, and brain concentrations of dopamine and its metabolites, 3,4-dihydroxyphenylacetic acid and homovanillic acid, were determined in the frontal cortex, caudate nucleus and substantia nigra by high-performance liquid chromatography with electrochemical detection. In utero and lactational exposure to 3,4,3',4'-TCB resulted in significant elevations in concentrations of dopamine in the frontal cortex, and of dopamine and its metabolites in the substantia nigra that persisted into adulthood. In contrast, in utero and lactational exposure to 2,4,2',4'-TCB resulted in significant decreases in concentrations of dopamine in the frontal cortex and caudate nucleus that also persisted into adulthood. We suggest that the reductions in brain dopamine concentrations are a consequence of ortho-substituted PCB congener-induced inhibition of the synthesis of dopamine during critical periods of development acting, perhaps, in concert with PCB-induced changes in cholinergic receptor function. On the other hand, the persistent elevations in brain dopamine and metabolite concentrations following perinatal exposure to 3,4,3',4'-TCB may be mediated by alterations in steroid hormone function during key developmental periods.

3,4-Dihydroxyphenylacetic Acid↗

Toxicity of 2,4,4'-trichlorobiphenyl in rats following 90-day dietary exposure.

The toxicity of 2,4,4'-trichlorobiphenyl (PCB 28) was investigated in rats after a 90-d dietary exposure. Groups of 10 male and 10 female weanling Sprague-Dawley rats were administered PCB 28 in the diet at 0, 0.05, 0.50, 5.0, or 50.0 ppm for 13 wk. Growth rate and food consumption were not affected by treatment, and no clinical signs of toxicity were observed. Mottled liver was noted in both control and PCB-treated males, but was found with increased incidence in the highest treatment group. Increased urinary ascorbic acid and hepatic microsomal ethoxyresorufin O-deethylase activity were observed in the 50.0 ppm group of both sexes. The vitamin A content in liver, lung, and kidney was not significantly affected by treatment. Analysis of brain biogenic amines showed a decreased dopamine concentration in the substantia nigra region of female rats receiving 0.5 ppm PCB 28 and higher doses. Female rats appeared to be more sensitive than males to the neurochemical effects of PCB 28. Dose-dependent histologic changes were observed in the thyroid and liver, with biologically significant changes occurring at 5.0 ppm and above. Based on these data, the no observable-adverse-effect level (NOAEL) for this PCB congener was considered to be 0.5 ppm in diet or 36 micrograms/kg body weight/d.

Administration, Oral↗

Epidemiological and laboratory evidence of PCB-induced neurotoxicity.

The purpose of this review is to provide a selective, but critical, assessment of important findings derived from both epidemiological and laboratory studies suggesting that: (1) exposure to polychlorinated biphenyls (PCBs) and related halogenated aromatic hydrocarbons induces significant neurological and behavioral dysfunctions in humans and laboratory animals, particularly following exposure during gestation and lactation; (2) the neurochemical actions of PCBs depend on their structure and the developmental status of the animal at the time of exposure; and (3) the mechanisms responsible for these changes may involve alterations in basic cellular signaling processes and endocrine function that influence the synthesis and activity of important central nervous system neurotransmitters, the organization of the developing brain, and the behavioral responses to these environmental contaminants.

Adult↗

Toxicity of PCB 77 (3,3',4,4'-tetrachlorobiphenyl) and PCB 118 (2,3',4,4'5-pentachlorobiphenyl) in the rat following subchronic dietary exposure.

The toxicity of 3,3',4,4'-tetrachlorobiphenyl (PCB 77) and 2,3',4,4',5-pentachlorobiphenyl (PCB 118) was investigated in rats following subchronic dietary exposure. Groups of 10 male and 10 female weanling Sprague-Dawley rats were administered PCB 77 in the diet at 0, 10, 100, 1000, or 10,000 ppb for 13 weeks. PCB 118 was administered to males in the diet at 0, 10, 100, 1000, and 10,000 ppb, while the female groups received 0, 2, 20, 200, or 2000 ppb of the congener for 13 weeks. Growth rate and food consumption were not affected by treatment. No clinical signs of toxicity were observed. Increased spleen weight occurred in male rats fed 1000 or 10,000 ppb PCB 77. Male rats receiving 10,000 ppb PCB 118 had increased liver weight and hepatic ethoxyresorufin O-deethylase (EROD) activity. Increased hepatic EROD activity but not liver weight was observed in female rats given the 2000-ppb PCB 118 diet. Increased EROD activity was also noted in male rats given 10,000 ppb and in female groups receiving 1000 or 10,000 ppb PCB 77. Male rats exposed to 10,000 ppb PCB 77 had decreased vitamin A in the liver and lung and elevated levels in the kidney. Liver vitamin A of both 1000- and 10,000-ppb PCB 77 female groups was decreased. PCB 118 had no effects on tissue vitamin A at the levels studied. No hematological changes or serum biochemical changes were seen in any of PCB 118- and PCB 77-treated groups, nor were liver uroporphyrin levels altered. A reduction in dopamine and homovanillinic acid in substantia nigra region of the brain was observed in female rats fed 2000 ppb PCB 118, while 10,000 ppb PCB 77 was associated with an elevation in 3,4-dihydroxyphenylacetic acid in the nucleus accumbens region of male rat brains. Mild to moderate changes were observed in the liver and thyroid of rats given PCB 77 or PCB 118. PCB 118 accumulated in a dose-dependent manner in fat and to a much lesser extent in liver. In contrast, very low levels of PCB 77 residue were found in the tissues examined. Based on the above data it was concluded that NOAEL of PCB 77 is 100 ppb in diet or 8.7 micrograms/kg and that of PCB 118 is 200 ppb in diet or 17 micrograms/kg body wt/day.

Animal Feed↗

Decreases in dopamine concentrations in adult, non-human primate brain persist following removal from polychlorinated biphenyls.

Adult male non-human primates, Macaca nemestrina, were orally exposed for 20 weeks to 3.2 mg/kg per day of either Aroclor 1016 or Aroclor 1260 made up in corn oil. Following cessation of exposure, the animals were observed for either an additional 24 or 44 weeks. After killing, regional brain concentrations of biogenic amines and polychlorinated biphenyls were determined by high-performance liquid chromatography (HPLC) and gas chromatography (GC), respectively. Brain dopamine (DA) concentrations were significantly decreased, compared to controls, in all polychlorinated biphenyl-exposed animals. Most importantly, in spite of significant decreases in brain polychlorinated biphenyl concentrations observed following removal from exposure (an average decline of 60%), there was no statistically discernible relationship of the changes in brain DA concentrations to either time following removal from polychlorinated biphenyls or brain polychlorinated biphenyl concentrations. These findings demonstrate that sub-chronic exposure of the adult non-human primate to polychlorinated biphenyls results in long-lasting changes in brain DA concentrations.

Animals↗