Developmental Exposure to 4-hydroxy-2,3,3',4',5-pentachlorobiphenyl (4-OH-CB107): Long-Term Effects on Brain Development, Behavior, and Brain Stem Auditory Evoked Potentials in Rats

In the present study the developmental neurotoxic effects ofthe PCB metabolite 4-OH-2,3,3',4',5-pentachlorobiphenyl (4-OH-CB107)were compared with effects caused by a mixture of parent polychlorinatedbiphenyl (PCB) congeners (Aroclor 1254). Pregnant female Wistarrats were exposed to 0.5 or 5 mg 4-OH-CB107, or 25 mg Aroclor1254 per kg body weight from gestation days 10 to 16. Plasmathyroid hormone levels were significantly decreased in the offspringof all treatment groups at postnatal day 4 (PND 4). Behavioralexperiments using an open field paradigm revealed an impairedhabituation in male offspring of all treatment groups at PND130. Passive avoidance experiments indicated significant influenceson the time course of step-down latencies across trials in exposedmale rats. Catalepsy induced by haloperidol showed increasesin latencies to movement onset in female offspring exposed to0.5 mg 4-OH-CB107 compared to Aroclor 1254 treated offspringat PND 168–175. Male offspring exposed to 4-OH-CB107 orAroclor 1254 showed decreases in latencies compared to controlanimals. Brain stem auditory evoked potentials (BAEPs) measuredat PND 300–310 showed significant increases in auditorythresholds in the low frequency range between Aroclor 1254 and4-OH-CB107 (5 mg/kg bw) treated animals. Measurements of neurotransmitterlevels revealed effects of Aroclor 154 exposure on both thedopaminergic and the serotonergic systems, whereas 4-OH-CB107exposure affected dopaminergic and noradrenergic systems, withslight but not significant effects on the serotonergic system.These results indicate that 4-OH-CB107 is able to induce long-termeffects on behavior and neurodevelopment. The observed effectsfor 4-OH-CB107 are similar to, but in some aspects differentfrom, the effects observed after Aroclor 1254 exposure.     

Tissue distribution and half-lives of individual polychlorinated biphenyls and serum levels of 4-hydroxy-2,3,3',4',5-pentachlorobiphenyl in the rat.

This study was done to generate kinetic data on individual congeners of chlorinated biphenyls in the low dose range, which could be of value in the risk assessment procedure. Male Sprague-Dawley rats were given a single oral dose of a mixture of polychlorinated biphenyls (CBs) containing either CBs 105, 118, 138, 153, 156, 157, 170, and 180 (A-mix) or CBs 28, 52, 77, 87, and 101 (B-mix). Liver, serum, and adipose tissue were collected after 6 h up to 135 days, from rats given the A-mix, and after 6 h up to 4 days from rats given the B-mix. CB concentrations were measured in liver, serum, and adipose tissue. In addition, this study provides kinetic data of one of the major CB metabolites, 4-hydroxy-2,3,3',4',5-pentachlorobiphenyl (4-OH-CB107). The low doses used resulted in serum CB concentrations similar to human background serum concentrations. In the A-mix experiment all CBs show high initial liver and serum concentrations followed by redistribution into adipose tissue. Differences between congeners were correlated to molecular weight. High molecular weight correlated to lower uptake and slower redistribution. During dynamic steady-state the tissue concentrations decreased with a calculated first order rate between 54-129 days for halving the concentrations (half-life). Most of the decrease in concentration was explained by the growth-related increase of tissue masses in general and adipose tissue in particular. In the B-mix experiment, the concentrations of CBs in adipose tissue decreased with between 25 and 59% from day 1 to day 4. These results show that the B-mix congeners, given at low dose, have longer half-lives than previously reported in high dose studies. Partition coefficients between body compartments are reported and for the first time a high and congener specific liver-to-serum ratio of CB 77 is observed.     

Effects of in utero exposure to the organophosphate insecticide fenitrothion on androgen-dependent reproductive development in the Crl:CD(SD)BR rat.

Fenitrothion [0,0-dimethyl-O-(4-nitro-m-tolyl) phosphorothioate] is an organophosphate insecticide that has been shown to have antiandrogenic activity using in vitro and in vivo screening assays. Studies were performed to evaluate the ability of fenitrothion to disrupt androgen-dependent sexual differentiation in the male rat. Pregnant Crl:CD(SD)BR rats were administered fenitrothion by gavage at 0, 5, 10, 15, 20, or 25 mg/kg/day ( n = 6-11/group) from gestation day (GD) 12 to 21. Maternal toxicity was observed in the dams treated with 20 and 25 mg fenitrothion/kg/day based on muscle tremors and decreases in body weight gain from GD 12 to 21. Fetal death was increased in the 20 and 25 mg/kg/day exposure groups, as evidenced by a decrease in the proportion of pups born alive. Androgen-mediated development of the reproductive tract was altered in male offspring exposed in utero to maternally toxic levels of fenitrothion (25 mg/kg/day), as evidenced by reduction in anogenital distance on postnatal day (PND) 1 and retention of areolae on PND 13. However, these effects were only transient, and there were no indications of abnormal phenotypes or development of androgen-dependent tissues on PND 100. At the dose levels evaluated in this study, fenitrothion was only weakly antiandrogenic in vivo compared with other androgen receptor antagonists such as flutamide, linuron, and vinclozolin. Based on observed fetotoxicity at 20 mg/kg/day, the lowest observed adverse effect level (LOAEL) for developmental effects can be lowered from 25 to 20 mg/kg/day.     

The dioxin-like pollutant PCB 126 (3,3',4,4',5-pentachlorobiphenyl) affects risk factors for cardiovascular disease in female rats

Epidemiological studies suggest that exposure to persistent organic pollutants such as organochlorines might induce cardiovascular disorders and diabetes. Some of these organochlorines, such as dioxins and some dioxin-like PCBs, have been characterised as anti-estrogenic due to their inhibition of estrogenic-induced responses. In the present pilot study, 40 female rats were subjected to either exposure to the dioxin-like 3,3′,4,4′,5-pentachlorobiphenyl (PCB 126) or vehicle, as well as ovariectomy (OVX) or sham operation in a 2×2 factorial design over 12 weeks to explore potential interactions between estrogen status and PCB 126 exposure on cardiovascular risk factors.

PCB 126 increased heart weight and serum cholesterol levels in both groups. PCB 126 increased blood pressure in the sham-operated animals only.

In conclusion, PCB 126 exposure in female rats resulted in effects on cardiovascular risk factors, such as serum cholesterol, blood pressure, and heart weight. Of these effects of PCB 126, the increase in blood pressure was dependent on estrogen status.     

Effects of exposure to 3,3',4,4',5-pentachlorobiphenyl (PCB 126) throughout gestation and lactation on behavior (concurrent random interval-random interval and progressive ratio performance) in rats

There is evidence that polychlorinated biphenyl (PCB) congeners have differential effects on endpoints of neurotoxicity depending on their chemical structure: specifically, that ortho-substituted congeners are neurotoxic while coplanar (dioxin-like) congeners are relatively inactive in producing neurotoxic effects. This study extends research on the effects of developmental exposure to the coplanar congener 3,3′,4,4′,5-pentachlorobiphenyl (PCB 126) in Long-Evans rats. Dams were dosed with 0, 0.25, or 1 μg/kg/day Monday to Friday beginning 5 weeks before and continuing through gestation and lactation. The first 2-week breeding period produced 10, 7, and 13 litters in the three dose groups, respectively, used in behavioral assessment. Breeding females from the control and low-dose group that did not conceive were rebred after 76 days of dosing, producing six and six litters used in behavioral testing. This regimen of PCB exposure produced reduced weight gain between birth and weaning in cohort 1, and decreased thyroxine levels and changes in hematology and serum biochemistry parameters in both cohorts. One female and male from each litter were tested under a series of three concurrent random interval–random interval (RI-RI) schedules of reinforcement beginning at about 400 days of age, followed immediately by assessment under a progressive ratio (PR) schedule. The concurrent RI-RI allows assessment of performance during steady state and during behavior in transition (learning). The PR schedule provides the opportunity to assess the strength of the reinforcing event independent of response rate. During the first RI-RI schedule, the high-dose group apportioned responses less accurately than controls with respect to the scheduled relative reinforcement density on the two levers. There was also some evidence for differences in performance between treated and control groups on the third RI-RI schedule of reinforcement. There was no evidence for differences in the relative strength of the reinforcing event as assessed by PR performance. These same rats failed to exhibit PCB-induced impairment on a spatial delayed alternation task or under multiple fixed interval–fixed ratio or DRL schedules of reinforcement, performed prior to the current experiments. These data extend previous findings concerning the pattern of behavioral effects as a consequence of gestational and lactational exposure to a dioxin-like PCB congener.     

Low-frequency hearing loss following perinatal exposure to 3,3',4,4',5-pentachlorobiphenyl (PCB 126) in rats.

Previous research has demonstrated the sensitivity of the developing rat to the ototoxic effects of exposure to Aroclor 1254. In this study we assessed the effects of developmental exposure to an individual PCB congener (3,3',4,4',5-pentachlorobiphenyl; PCB 126) on auditory function. Nulliparous Long Evans rats received either 0, 0.25, or 1.0 microg/kg/day (5 days/week) for 35 days prior to breeding and throughout gestation and lactation. Auditory thresholds for 0.5-, 1-, 4-, 8-, 16-, 32-, and 40-kHz tones were assessed in offspring on postnatal days (PND) 76-90. Perinatal maternal PCB 126 exposure caused low-frequency hearing deficits. Elevated auditory thresholds occurred in the 1.0 microg/kg/day treated group for 0.5- and 1-kHz tones, whereas thresholds were not significantly affected at any higher frequencies. These results are important in that the data implicate, at least partially, the coplanar PCBs in the developmental ototoxicity induced by Aroclor 1254.     

Change of bone tissue composition and impaired bone strength in rats exposed to 3,3',4,4',5-pentachlorobiphenyl (PCB126)

The aim of this study was to compare effects of estrogen depletion (ovariectomy) and exposure to 3,3′,4,4′,5-pentachlorobiphenyl (PCB126) on bone strength and bone tissue composition in the rat. Half of the rats were ovariectomized (n=20) and the remainder were sham-operated. Ten of the ovariectomized rats and ten of the sham operated were exposed to PCB126 (ip injections) for 3 months (total dose, 384 μg/kg bodyweight), while those remaining received the vehicle. The humerus and femur were used for analysis of torsional strength and biochemical studies, respectively. Both sham-operated and ovariectomized animals showed a significantly shorter bone length, lower water content and a decreased torsional stiffness when exposed to PCB126. Sham-operated rats exposed to PCB126 had lower maximum torque when compared with sham operated controls. The PCB126-exposed rats also exhibited a significantly lower collagen concentration, but showed a higher pyridinoline concentration of cortical bone. PCB126 exposure decreased the hepatic level of vitamin A but increased vitamin A levels in serum and kidneys. Ovariectomy per se increased bone length and organic content and decreased the inorganic content significantly, but did not affect any of the tested biomechanical parameters. In conclusion, this study showed that the common environmental pollutant PCB126 impaired bone strength and altered bone composition. It is hypothesized that these effects might partly be explained by PCB-induced retinoid disturbances.     

Adverse effects of neonatal exposure to 3,3',4,4',5,5'-hexachlorobiphenyl on hormone levels and testicular function in male Sprague-Dawley rats

In this study, we investigated the time-course changes of hormone levels and sperm numbers in male Sprague-Dawley (SD) rats after neonatal exposure to 3,3',4,4',5,5'-hexachlorobiphenyl (PCB169). Neonatal rats were given (through oral gavages) doses of 0, 0.025, 0.25, or 0.5 mg/kg-day of PCB169 in corn oil from postnatal day 1 (PND1) to PND7. The rats were sacrificed at PND8, PND21, and PND90. PCB169 exposure was confirmed by the marked induction of liver CYP1A1 mRNA expression at these three time points. The testicular daily sperm production and the sperm counts of the epididymis cauda significantly decreased at PND90 compared to that of control. Although reductions in serum thyroxine and triiodothyronine levels occurred at all these three time points and at both PND21 and PND90, respectively, the mRNA expression of testicular thyroid hormone receptor α1 was suppressed significantly only at PND8. The serum and testicular testosterone (T) levels declined markedly at PND90 compared to the controls, but there was no effect at PND21. The mRNA expression of testicular steroidogenic factor 1 was inhibited markedly at the three time points, whereas those of StAR, P450c17, P450scc, and 3β-HSD were suppressed significantly only at PND90 relative to the controls. PCB169 treatment had no effects on pituitary follicle-stimulating hormone and luteinizing hormone levels and on their receptors' expression in the testes. These results indicate that neonatal exposure to PCB169 damages hormone levels and testicular function in the long-term, resulting in persistent hypothyroidism and decreases in adult T levels and sperm counts.     

Effects of maternal exposure to aflatoxin B1 during pregnancy on fertility output of dams and developmental,behavioral and reproductive consequences in female offspring using a rat model

A suboptimal in utero environment can have detrimental effects on the pregnancy and long-term adverse “programing” effects on the offspring. Aflatoxin B1 is one of the potent reproductive toxicants and currently detected in both milk and tissues. This article focuses on the effects of prenatal exposure to graded doses of aflatoxin B1 on the pregnancy outcomes of dams and postnatal developments of the female offspring, since these issues have ethological relevance in both animals and humans. Pregnant Wistar rats were injected intramuscularly with vehicle or aflatoxin B1 (10, 20, 50 or 100?μg/kg body weight/day) on days 12–19 of gestation. At parturition, newborns were observed for clinical signs of toxicity and survival. The female offspring were examined through a battery of tests in order to evaluate their developmental, behavioral and reproductive end points. All animals were born alive. The litter size of the aflatoxin B1 treated rats was comparable to the controls. However, the birth weight of the pups in the experimental group was significantly lower when compared to controls. Significant and persistent lags in cliff avoidance, negative geotaxis, surface rightening activity and ascending wire mesh, with a delay in elapsed time for vaginal opening were detected in the female progeny exposed to aflatoxin B1 during embryonic development. The locomotor activity and exploratory behavior in experimental females were significantly decreased than that of controls. Embryonic exposure to aflatoxin B1 also resulted in prolonged stress response, irregular estrus and suppressed fertility output in the progeny at their adulthood. These results indicate that in utero exposure to aflatoxin B1 severely compromised postnatal development of neonatal rats and caused irregular estrus that was accompanied by suppressed fertility output.     

A dose-response study following in utero and lactational exposure to di-(2-ethylhexyl) phthalate (DEHP): effects on androgenic status, developmental landmarks and testicular histology in male offspring rats

An extensive dose-response study following in utero and lactational exposure to di-(2-ethylhexyl) phthalate (DEHP) was conducted. A wide range of low and high DEHP doses were tested. Reproductive effects were evaluated on male offspring rats. Female Wistar rats were treated daily with DEHP and peanut oil by gavage from gestation day 6 to lactation day 21 at doses of 0.015, 0.045, 0.135, 0.405 and 1.215 mg DEHP/kg body weight (bw)/day (low doses) and at 5, 15, 45, 135 and 405 mg DEHP/kg bw/day (high doses). Nipple retention and reduced anogenital distance, both sensitive markers of anti-androgenic effects during development, were only seen in males exposed to the highest dose (405 mg/kg/day). Delayed preputial separation was observed in animals exposed to 15 mg DEHP/kg/day and higher doses. Histopathological examination of the testis on postnatal days (PNDs) 1 and 22 revealed changes at 135 and 405 mg DEHP/kg/day. The most prominent finding on PND 1 was the presence of bi- and multinucleated gonocytes. On PND 22 signs of reduced germ cell differentiation in seminiferous tubules of exposed animals were observed. Testis weight on PND 22 was significantly increased at 5, 15, 45 and 135 mg/kg/day, an effect that qualitatively differs from exposure to higher doses. The current results show that DEHP acts as an anti-androgen at a high dose exposure (405 mg/kg/day). However, these results also indicate that other subtle developmental effects occur at lower DEHP doses.     

Bone tissue composition, dimensions and strength in female rats given an increased dietary level of vitamin A or exposed to 3,3',4, 4',5-pentachlorobiphenyl (PCB126) alone or in combination with vitamin C

In previous studies we have described structural and functional changes in rat bone tissue caused by 3,3',4,4',5-pentachlorobiphenyl (PCB126). Some of the effects caused by PCB126 resemble those found in vitamin C-deficient rats, as well as those found in rats with a high dietary intake of vitamin A. The present investigation was designed to determine if these PCB126-induced changes could be inhibited by addition of vitamin C to the drinking water and if they could be evoked by vitamin A administration. Five groups of female rats were used in this study, which lasted for 12 weeks. Three of the groups were exposed to PCB126 (total dose 320 microgram/kg, bw), either alone or in combination with vitamin C added to the drinking water (1 and 10 g/l, respectively). One group was given feed with increased level of vitamin A (600000 U/kg pellet) and the fifth group served as controls. Using peripheral quantitative computed tomography (pQCT), it was found that PCB126 increased trabecular density and cortical thickness, but reduced the trabecular area. Furthermore, maximum torque and stiffness of the humerus during torsional testing and serum osteocalcin levels were reduced by PCB126. Of the PCB126 induced effects observed, addition of vitamin C only inhibited the reduction of serum osteocalcin. Like PCB126 vitamin A supplementation increased the inorganic content and the bone density and also reduced the trabecular area and polar moment of inertia but did not increase the cortical thickness or reduce maximum torque, stiffness or serum osteocalcin level. Apparently, the effects induced by PCB126 are not mediated either via decreased vitamin C level or increased vitamin A level.     

Effects of subchronic exposure to complex mixtures of dioxin-like and non-dioxin-like polyhalogenated aromatic compounds on thyroid hormone and vitamin A levels in female Sprague-Dawley rats.

The aim of this study was to determine the effects of subchronic exposure to complex mixtures of polyhalogenated aromatic hydrocarbons (PHAHs) on the thyroid hormone and retinoid status in female Sprague-Dawley rats and to investigate the predictability of these effects by the toxic equivalency factor (TEF) concept. In the first experiment, the focus was on a complex dioxin-like PHAH mixture, which covered > 90% of the total toxic equivalents (TEQ) present in Baltic herring. In the second experiment, the contribution of non-dioxin-like polychlorinated biphenyls (PCBs) was investigated by testing the commercial PCB mixture Aroclor 1260, its 0-1 ortho and 2-4 ortho fractions and the reconstituted 0-4 ortho fraction. Hepatic retinoid levels were severely decreased ( approximately 70%) after treatment with the dioxin-like PHAH mixture, similar to the effect of a TEQ equivalent dose of 1 microg 2,3,7,8-TCDD/kg bw/week. However, the TEF concept failed to predict the effect on plasma retinol; a decrease (21%) was observed after treatment with the PHAH mixture, whereas an increase (21%) was found after treatment with TCDD. A more severe decrease of total thyroid hormone in plasma was observed after exposure to the PHAH mixture compared to treatment with TCDD ( approximately 60% vs. 38%). The discrepancy found between the predicted and observed effects for plasma retinol and thyroid hormone is possibly due to an additional effect of hydroxylated PCBs, formed from metabolizable PCBs present in the PHAH mixture. Aroclor 1260 and its fractions did not significantly alter the retinoid and thyroid hormone status at the dose levels tested, indicating that in case of exposure to complex PCB mixtures at environmental levels, no effects, or at best, only marginal effects can be expected on the retinoid and thyroid hormone status.     

Effects of subchronic exposure to a complex mixture of persistent contaminants in male rats: systemic, immune, and reproductive effects.

Human populations throughout the world are exposed daily to low levels of environmental contaminants. The consequences of potential interactions of these compounds to human endocrine, reproductive, and immune function remain unknown. The current study examines the effects of subchronic oral exposure to a complex mixture of ubiquitous persistent environmental contaminants that have been quantified in human reproductive tissues. The dosing solution used in this study contained organochlorines (2,3,7,8-tetrachlorodibenzo-p-dioxin [TCDD], polychlorinated biphenyls [PCBs],p,p'-dichlorodiphenoxydichloroethylene [p,p'-DDE],p,p-dichlorodiphenoxytrichloroethane [p,p'-DDT], dieldrin, endosulfan, methoxychlor, hexachlorobenzene, and other chlorinated benzenes, hexachlorocyclohexane, mirex and heptachlor) as well as metals (lead and cadmium). Each chemical was included in the mixture at the minimum risk level (MRL) or tolerable daily intake (TDI) as determined by the U.S. EPA or ATSDR or, for TCDD, at the no observable effect level (NOEL) used to calculate the TDI. Sexually mature male rats were exposed to this complex mixture at 1, 10, 100, and 1000 times the estimated safe levels daily for 70 days. On day 71, all animals were sacrificed and a variety of physiological systems assessed for toxic effects. Evidence of hepatotoxicity was seen in the significant enlargement of the liver in the 1000x group, reduced serum LDH activity (100x), and increased serum cholesterol and protein levels (both 1000x). Hepatic EROD activities were elevated in animals exposed to10x and above. The mixture caused decreased proliferation of splenic T cells at the highest dose and had a biphasic effect on natural killer cell lytic activity with an initial increase in activity at 1x followed by a decrease to below control levels in response to 1000x. No treatment-related effects were seen on bone marrow micronuclei, daily sperm production, serum LH, FSH, or prolactin levels or weights of most organs of the reproductive tract. The weights of the whole epididymis and of the caput epididymis were significantly decreased at 10x and higher doses, although no effect was seen on cauda epididymal weight. The sperm content of the cauda epididymis was increased at the 1x level but not significantly different from control at higher dose levels. A slight, but significant, increase in the relative numbers of spermatids was seen in the animals from the 1000x group with a trend towards reduced proportion of diploid cells at the same dose. Only minor, nondose related changes were seen in parameters related to condensation of chromatin, as determined by flow cytometry, in epididymal sperm. We conclude that the mixture induced effects on the liver and kidney and on general metabolism at high doses but caused only minor effects on immune function, reproductive hormone levels, or general indices of reproductive function measures. These data suggest that additive or synergistic effects of exposure to contaminants resulting in residue levels representative of contemporary human tissue levels are unlikely to result in adverse effects on immune function or reproductive physiology in male rats.     

Effects of octamethylcyclotetrasiloxane (D4) on the luteinizing hormone (LH) surge and levels of various reproductive hormones in female Sprague-Dawley rats

The objectives of this study were to assess the potential for D₄ to suppress the pre-ovulatory lutenizing hormone (LH) surge, to block or delay ovulation, and to evaluate potential effects on reproductive hormones in rats. Female Sprague–Dawley Crl:CD^® (SD) IGS BR rats received whole-body vapor inhalation exposure to D₄ (0, 700, or 900 ppm) 6 h per day for 3 days. Trunk blood obtained on proestrus at 10 a.m. was evaluated for levels of follicle stimulating hormone (FSH), estradiol (E2), estrone (E1), and progesterone (P4). Other rats had serial blood samples collected via cannula at 2, 4, 6, 8, and 10 p.m. on the day of proestrus and plasma evaluated for LH and prolactin (PRL). Trunk blood was collected at 8 a.m. of estrus and plasma evaluated for FSH, E2, E1, and P4. At 10 a.m. on proestrus, significant increases in E1 levels in the 700 and 900 ppm groups and significant increases in P4 levels in the 900 ppm group were noted. At 8 a.m. on estrus, significant increases in E1, E2, in the E1/E2 ratio and decreases in FSH were noted in the 700 and 900 ppm groups. The major effect on the LH profile was observed most clearly when the rats were grouped by ovulatory status, animals that did or did not ovulate. Regardless of treatment, suppression of the LH surge correlated with blocked ovulation. The percentage of rats that ovulated was (700 ppm, 42%; 900 ppm, 31%) compared to controls (79%). Overall, the data indicate that high exposures to D₄ attenuated the pre-ovulatory LH surge and significantly decreased the portion of female rats that ovulated.