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      Effect of Exposure to 3,3′,4,4′,5-Pentachlorobiphenyl (PCB 126) Throughout Gestation and Lactation on Development and Spatial Delayed Alternation Performance in Rats

      Neurotoxicology and Teratology
      Elsevier BV

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          Developmental exposure to polychlorinated biphenyls (Aroclor 1254) reduces circulating thyroid hormone concentrations and causes hearing deficits in rats.

          Developmental hypothyroidism causes growth deficits, motor dysfunction, and hearing disorders in humans and animals. Therefore, environmental toxicants, such as polychlorinated biphenyls (PCBs), may secondarily affect these endpoints via thyrotoxicity. In this study, Long-Evans rats were given Aroclor 1254 (po), at 0, 1, 4, or 8 mg/kg from Gestation Day 6 through Postnatal Day (PND) 21. We evaluated the offspring at various age intervals for circulating thyroid hormone concentrations [thyroid-stimulating hormone, and free and total triiodothyronine (T3) and thyroxin (T4)], body weight, eye opening, survival, motor activity development, auditory startle response, and auditory thresholds. Circulating T4 concentrations were sharply reduced in a dose-dependent fashion in PCB-exposed groups at PND 1, 7, 14, 21, and 30 but recovered to control levels by PND 45. Moderate reductions in T3 concentrations were apparent in the 4 and 8 mg/kg groups on PND 21 and 30. Deficits in body weight gain and early eye opening were apparent in the treated pups; by weaning, pup mortality was 20% in the 4 mg/kg group and 50% at the highest dose. Motor activity was also transiently reduced in 15 day old offspring from the 8 mg/kg group. At this dose, animals showed reduced auditory startle amplitudes at PND 24, but not when tested as adults. Importantly, Aroclor 1254 caused permanent auditory deficits (20-30 dB threshold shift) at the lowest frequency tested (1 kHz) in both the 4 and 8 mg/kg groups, whereas auditory thresholds were not significantly affected at higher frequencies (4, 16, 32, or 40 kHz). These data indicate that while some effects of Aroclor 1254 exposure are dissimilar to drug-induced hypothyroidism (e.g., age of eye opening), effects on hormone levels and body weight are comparable. Detection of auditory deficits in PCB-treated animals is a novel finding and may reflect the effects of thyroid hormone disruption on the development of the cochlea.
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            Spatial learning deficits in adult rats exposed to ortho-substituted PCB congeners during gestation and lactation.

            Spatial learning and memory was assessed in rats following gestational and lactational exposure to specific ortho-substituted PCBs. Time-mated Sprague-Dawley rats were exposed to PCB 28 (2,4,4'-trichlorobiphenyl), 8 or 32 mg/kg/day, PCB 118 (2,3',4,4',5-pentachlorobiphenyl), 4 or 16 mg/kg/day, PCB 153 (2,2',4,4',5,5'-hexachlorobiphenyl), 16 or 64 mg/kg/day, or corn oil vehicle via gavage on Gestation Days 10-16. Litters were culled to eight on Day 2 and weaned on Day 21. Beginning on Day 90, one male and one female from each litter were tested on a working/reference memory task on an eight-arm maze. For each rat, the same four arms were baited throughout training. Animals were tested Monday-Friday, for seven consecutive weeks. No differences in working or reference memory errors were observed. The same animals were later tested on a T-maze delayed spatial alternation task. On each trial, the reinforcer was placed in the arm opposite that chosen by the rat on the previous trial. Intertrial delays of 15, 25, or 40 sec appeared in counterbalanced order. Rats were tested Monday-Friday for three consecutive weeks. The higher doses of all three congeners resulted in slower acquisition by female rats. Males were not affected. PCB-exposed females were impaired at all delays and were not differentially more impaired at longer delays, suggesting a learning or attentional deficit, rather than a mnemonic deficit. These findings demonstrate that perinatal exposure to ortho-substituted PCBs can result in long-lasting deficits in learning and suggest that the effects of PCBs on learning may be sex specific.
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              Alterations in rat brain thyroid hormone status following pre- and postnatal exposure to polychlorinated biphenyls (Aroclor 1254).

              The effect of daily oral maternal exposure to 0, 5, or 25 mg/kg body wt of a polychlorinated biphenyl (PCB) mixture (Aroclor 1254) on Days 10 to 16 of gestation on plasma and brain thyroid hormone concentrations and peripheral thyroid hormone concentrations and peripheral thyroid hormone metabolism were examined in fetal and weanling rats. Plasma thyroid hormone levels and hepatic microsomal thyroid hormone glucuronidation were also examined in pregnant rats and the adult offspring. Plasma and brain levels of PCBs and hydroxylated PCB metabolites were analyzed in fetal, weanling, and adult offspring. Maternal exposure to Aroclor 1254 significantly decreased fetal (Gestation Day 20) and neonatal (Postnatal Day 4) plasma total thyroxine (T4) and free T4 levels in a dose-dependent manner. Effects of maternal Aroclor 1254 exposure on plasma total and free T4 concentrations were less pronounced in offspring at 21 days of age and absent 90 days after birth. Plasma concentrations of thyroid-stimulating hormone were unaltered in fetuses, neonates, weanling rats, and adult offspring following maternal treatment with Aroclor 1254. the concentration of T4 was severely depressed in the forebrain and cerebellum of fetal rats on Day 20 of gestation following maternal Aroclor 1254 exposure. Brain triiodothyronine (T3) concentrations in the Aroclor-exposed fetuses were significantly decreased relative to control values only in the low-dose group. On Day 21 postpartum T4 concentrations were significantly decreased in the forebrains of female weanling rats from the 25 mg Aroclor 1254/kg dose group, and no reductions were observed in forebrain T3 concentrations in male or female neonates. The deiodination of T4 to T3 was significantly increased in fetal forebrain homogenates by both PCB treatments. In female weanling brain homogenates the deiodination of T4 to T3 was significantly decreased in the low-dose group and unaltered in the high-dose group. No alterations in brain thyroid hormone metabolism were observed in forebrain homogenates from adult offspring exposed pre- and postnatally to Aroclor 1254. Hepatic microsomal T4 glucuronidation was significantly decreased in fetal microsomes following perinatal PCB exposure and significantly increased in weanling hepatic microsomes in a dose-dependent manner. An accumulation of mainly one PCB metabolite, 2,3,3',4',5-pentachloro-4-biphenylol was observed in fetal plasma and forebrain on Gestation Day 20 and in neonatal and weanling rat plasma on Postnatal Days 4, 21, and 90. The plasma level of 2,3,3',4',5-pentachloro-4-biphenylol was higher than that of the persistent PCB congener 2,2',4,4',5,5'-hexachlorobiphenyl in the control and PCB-exposed offspring up to Postnatal Day 21, and even after 90 days, the 2,3,3',4',5-pentachloro-4-biphenylol was present in amounts approximately equal to those of CB 153. Although PCB levels were relatively high in the weanling rat forebrain, no hydroxylated PCB metabolites were detected. On Day 90 postpartum, plasma levels of PCBs and 2,3,3',4',5-pentachloro-4-biphenylol were still elevated in the offspring of PCB-treated dams relative to controls. These results suggest that the accumulation of hydroxylated PCB metabolites in fetal plasma can reduce fetal plasma T4 levels and accordingly fetal brain T4 levels. However, in late gestational fetuses, the induction of brain type II thyroxine 5'-deiodinase activity compensates for decreases in brain T4 levels, so that brain T3 levels are maintained.
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                Author and article information

                Journal
                Neurotoxicology and Teratology
                Neurotoxicology and Teratology
                Elsevier BV
                08920362
                January 1999
                January 1999
                : 21
                : 1
                : 59-69
                Article
                10.1016/S0892-0362(98)00031-2
                e3fdcc52-dc9a-4676-8b40-9aed16215665
                © 1999

                http://www.elsevier.com/tdm/userlicense/1.0/

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