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Polychlorinated biphenyls (PCBs) and polybrominated diphenyl ethers (PBDEs) are widespread environmental contaminants found in seafood and dairy products. PCBs and PBDEs are structurally similar chemicals and affect thyroid hormone function and behavior in children and laboratory rodents. Although coexposure frequently exists, the in vivo developmental effects of combined exposure to PCBs and PBDEs on thyroxine (T4) levels are unknown. We examined the effects of PCB and PBDE coexposure from gestational day 6 through postnatal day (p) 21, alone and in combination, on T4 levels in rat offspring. In males, exposure to PCBs and PBDEs at 1.7, 5, 10, 20, 40, and 60 μmol/kg/day induced equivalent and dose-dependent reductions in T4 from p 7 to p 21. Exposure to equimolar mixtures of PCBs and PBDEs at 3.4, 10, 20, 40, and 80 μmol/kg/day additively reduced T4 from p 7 to p 21 in males. In a second series of experiments, we determined sex effects on the mixture exposures and found that coexposure to PCBs and PBDEs had similar additive effects on T4 levels in male and female offspring. This study demonstrates that equimolar exposure to PCBs and PBDEs induces similar reductions in T4 levels and that coexposure to a mixture of PCBs and PBDEs has additive effects on T4 levels. These thyroid hormone effects of coexposure to PCBs and PBDEs are important when considering the cumulative effects of coexposure to multiple environmental thyroid hormone–disrupting agents in risk assessment for developmental disorders. [ABSTRACT FROM PUBLISHER]

Polychlorinated biphenyls (PCBs) and polybrominated diphenyl ethers (PBDEs) are widespread environmental contaminants associated with changes in behavior and neurochemical function in laboratory animals and behavioral deficits in children. PCBs and PBDEs are found in food, especially in seafood and dairy products, and coexposure to these contaminants is likely. We examined the effects of an environmentally relevant mixture of PCBs (Fox River Mix [FRM]) and a PBDE mixture (DE-71) alone and in combination on synaptosomal and medium dopamine (DA) levels and the levels of the DA metabolite 3,4-dihydroxyphenylacetic acid (DOPAC) in striatal synaptosomes derived from postnatal days (PND) 7, PND14, or PND21 rats. FRM elevated medium DA and reduced synaptosomal DA concentrations with greater potency than equimolar concentrations of DE-71. The effects of FRM, but not DE-71, were dependent on the age of the animals from which the synaptosomes were derived, with greater effects observed in synaptosomes from the youngest animals. We used Bliss’ model of independence to assess the possible interaction(s) of a 1:1 mixture of FRM and DE-71 on synaptosomal DA function and found that the effects of the FRM/DE-71 mixture were additive. Furthermore, as for FRM alone, the effects of the FRM/DE71 mixture were greater in synaptosomes prepared from PND7 rats than in synaptosomes from PND14 and PND21 rats. Because the effects of these contaminants are additive, it is necessary to take into account the cumulative exposure to organohalogen contaminants such as PCBs and PBDEs during risk assessment. [ABSTRACT FROM AUTHOR]

Polybrominated diphenyl ethers (PBDEs), a group of flame retardants comprising 209 congeners, have become widespread environmental pollutants. High levels of PBDEs have been detected in human tissues, particularly in North America, and body burden is especially high in infants and toddlers because of exposure through breast milk and house dust. Increasing evidence, provided by animal studies, suggests that PBDEs are developmental neurotoxicants, although the underlying mechanisms are still unknown. Various PBDEs have been reported to cause oxidative stress and to induce apoptotic cell death in several cell types. In the present study, we investigated the comparative neurotoxicity in mouse cerebellar granule neurons of five brominated diphenyl ether (BDE) congeners, chosen among the most commonly found at the highest levels in human tissues. All BDE congener tested (BDE-47, BDE-99, BDE-100, BDE-153, and BDE-209) decreased cell viability and induced apoptotic cell death, which was prevented by antioxidants. They also caused oxidative stress, as indicated by an increase in reactive oxygen species and in lipid peroxidation. For all end points measured, the potency ranking of the congeners was BDE-100 > BDE-47 > BDE-99 > BDE-153 >> BDE-209. Measurement of BDE congener levels in neurons after exposure to different concentrations showed a significant accumulation in cells, which followed the same relative ranking. The findings suggest that all BDE congeners tested exhibit the same general mode of action (induction of oxidative stress–mediated apoptosis) and that the ability of each isomer to elicit such effects is dependent upon their accumulation in neurons, particularly in the microsomal fraction and the mitochondria. [ABSTRACT FROM PUBLISHER]

Polybrominated diphenylethers (PBDEs) are used as additive flame-retardants in consumer products to reduce the chances of ignition and burning. Levels of certain PBDE congeners have been increasing in fish, wildlife, and human tissues during the last decades. Some PBDEs are lipophilic and persistent, resulting in bioaccumulation in the environment. The structural similarity of PBDEs to other polyhalogenated aromatic hydrocarbons such as PCBs, has raised concerns that PBDEs might act as agonists for the aryl hydrocarbon receptor (AhR). To study the possible AhR-mediated effects of the environmentally relevant PBDEs (BDE47, 77, 99, 100, 153, 154, 183, 209), the induction of cytochrome P450-1A1 (CYP1A1) was studied in human breast carcinoma (MCF-7), human hepatocellular carcinoma (HepG2), and rat hepatoma (H4IIE) cells. 7-Ethoxyresorufin-O-deethylase (EROD) was used as a marker for CYP1A1 activity. Cells were exposed for 72 h to various PBDE concentrations (0.01–10 μM). Positive controls were 2,3,7,8-TCDD (0.001–2.5 nM) and PCB126 (0.01–10 nM). None of these PBDEs was capable of inducing EROD activity; this was confirmed by real time RT-PCR for CYP1A1 mRNA. However, in cells exposed to PBDEs in combination with TCDD, a concentration-dependent decrease in TCDD-induced EROD activity occurred. Co-exposure of BDE153 (10 μM) and a maximally inducing concentration of TCDD (1 nM) reduced EROD activity to 49% of the maximum induction by TCDD alone. All tested PBDEs showed similar effects in each cell line, though quantitative differences were observed. The observed decrease in CYP1A1 activity was not due to PBDE-dependent catalytic inhibition of EROD activity or cytotoxicity, nor were decreased CYP1A1 mRNA levels observed. However, inhibition of luciferase induction in mouse (Hepa) and rat (H4IIE) hepatoma cells containing a stably transfected AhR-responsive luciferase reporter gene, suggests that BDE77 is a weak AhR antagonist or partial agonist. [ABSTRACT FROM AUTHOR]