Neurotoxicology Research Group, Toxicology Division, Institute for Risk Assessment Sciences, Utrecht University, Utrecht, The Netherlands.
Environ Health Perspect. 2011 Jul;119(7):900-7. doi: 10.1289/ehp.1003035. Epub 2011 Feb 4.
BACKGROUND/OBJECTIVE: Polybrominated diphenyl ethers (PBDEs) and their hydroxylated (OH-) or methoxylated forms have been detected in humans. Because this raises concern about adverse effects on the developing brain, we reviewed the scientific literature on these mechanisms.
DATA SYNTHESIS: Many rodent studies reported behavioral changes after developmental, neonatal, or adult exposure to PBDEs, and other studies documented subtle structural and functional alterations in brains of PBDE-exposed animals. Functional effects have been observed on synaptic plasticity and the glutamate-nitric oxide-cyclic guanosine monophosphate pathway. In the brain, changes have been observed in the expression of genes and proteins involved in synapse and axon formation, neuronal morphology, cell migration, synaptic plasticity, ion channels, and vesicular neurotransmitter release. Cellular and molecular mechanisms include effects on neuronal viability (via apoptosis and oxidative stress), neuronal differentiation and migration, neurotransmitter release/uptake, neurotransmitter receptors and ion channels, calcium (Ca²⁺) homeostasis, and intracellular signaling pathways.
Bioactivation of PBDEs by hydroxylation has been observed for several endocrine end points. This has also been observed for mechanisms related to neurodevelopment, including binding to thyroid hormone receptors and transport proteins, disruption of Ca²⁺ homeostasis, and modulation of GABA and nicotinic acetylcholine receptor function.
The increased hazard for developmental neurotoxicity by hydroxylated (OH-)PBDEs compared with their parent congeners via direct neurotoxicity and thyroid disruption clearly warrants further investigation into a) the role of oxidative metabolism in producing active metabolites of PBDEs and their impact on brain development; b) concentrations of parent and OH-PBDEs in the brain; and c) interactions between different environmental contaminants during exposure to mixtures, which may increase neurotoxicity.
背景/目的:多溴二苯醚(PBDEs)及其羟基化(OH-)或甲氧基化形式已在人体中被检测到。由于这引起了对发育中大脑的不良影响的担忧,我们综述了关于这些机制的科学文献。
许多啮齿动物研究报告称,在发育、新生或成年期暴露于 PBDE 后会发生行为变化,其他研究记录了暴露于 PBDE 的动物大脑中的细微结构和功能改变。功能影响已在突触可塑性和谷氨酸-一氧化氮-环鸟苷单磷酸途径中观察到。在大脑中,已观察到参与突触和轴突形成、神经元形态、细胞迁移、突触可塑性、离子通道和囊泡神经递质释放的基因和蛋白质的表达发生变化。细胞和分子机制包括对神经元存活的影响(通过细胞凋亡和氧化应激)、神经元分化和迁移、神经递质释放/摄取、神经递质受体和离子通道、钙(Ca²⁺)稳态和细胞内信号转导途径。
PBDEs 的羟化生物活化已在几个内分泌终点观察到。这也在与神经发育相关的机制中观察到,包括与甲状腺激素受体和转运蛋白结合、破坏 Ca²⁺稳态以及调节 GABA 和烟碱型乙酰胆碱受体功能。
与母体同系物相比,羟基化(OH-)PBDEs 通过直接神经毒性和甲状腺破坏对发育性神经毒性的增加危害显然需要进一步研究:a)氧化代谢在产生 PBDEs 的活性代谢物及其对大脑发育的影响中的作用;b)母体和 OH-PBDEs 在大脑中的浓度;c)在暴露于混合物时不同环境污染物之间的相互作用,这可能会增加神经毒性。