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本文引用的文献

1
Exposure to polychlorinated biphenyls and hearing impairment in children.多氯联苯暴露与儿童听力损伤。
Environ Toxicol Pharmacol. 2008 Mar;25(2):183-7. doi: 10.1016/j.etap.2007.10.030. Epub 2007 Oct 24.
2
Auditory effects of developmental exposure to purity-controlled polychlorinated biphenyls (PCB52 and PCB180) in rats.大鼠发育暴露于高纯多氯联苯(PCB52 和 PCB180)的听觉效应。
Toxicol Sci. 2011 Jul;122(1):100-11. doi: 10.1093/toxsci/kfr077. Epub 2011 Apr 4.
3
Effects of pre and postnatal exposure to low levels of polybromodiphenyl ethers on neurodevelopment and thyroid hormone levels at 4 years of age.出生前后暴露于低水平多溴二苯醚对 4 岁儿童神经发育和甲状腺激素水平的影响。
Environ Int. 2011 Apr;37(3):605-11. doi: 10.1016/j.envint.2010.12.005. Epub 2011 Jan 14.
4
How are the inner hair cells and auditory nerve fibers activated without the mediation of the outer hair cells and the cochlear amplifier?在内耳毛细胞和耳蜗放大器不介导的情况下,内毛细胞和听觉神经纤维是如何被激活的?
J Basic Clin Physiol Pharmacol. 2010;21(3):231-40. doi: 10.1515/jbcpp.2010.21.3.231.
5
Lead and PCBs as risk factors for attention deficit/hyperactivity disorder.铅和多氯联苯作为注意缺陷多动障碍的风险因素。
Environ Health Perspect. 2010 Dec;118(12):1654-67. doi: 10.1289/ehp.0901852. Epub 2010 Sep 9.
6
Serum PCB concentrations and cochlear function in 12-year-old children.血清 PCB 浓度与 12 岁儿童耳蜗功能。
Environ Sci Technol. 2010 Apr 15;44(8):2884-9. doi: 10.1021/es901918h.
7
Developmental exposure to a commercial PBDE mixture, DE-71: neurobehavioral, hormonal, and reproductive effects.发育暴露于一种商用 PBDE 混合物 DE-71 中:神经行为、激素和生殖影响。
Toxicol Sci. 2010 Jul;116(1):297-312. doi: 10.1093/toxsci/kfq105. Epub 2010 Apr 7.
8
Prenatal exposure to PBDEs and neurodevelopment.产前暴露于多溴联苯醚与神经发育。
Environ Health Perspect. 2010 May;118(5):712-9. doi: 10.1289/ehp.0901340. Epub 2010 Jan 4.
9
Developmental exposure to PCBs, MeHg, or both: long-term effects on auditory function.发育过程中接触多氯联苯、甲基汞或两者:对听觉功能的长期影响。
Environ Health Perspect. 2009 Jul;117(7):1101-7. doi: 10.1289/ehp.0800428. Epub 2009 Apr 3.
10
To scale or not to scale: the principles of dose extrapolation.是否需要进行剂量外推:剂量外推的原则。
Br J Pharmacol. 2009 Jul;157(6):907-21. doi: 10.1111/j.1476-5381.2009.00267.x. Epub 2009 Jun 5.

发育暴露于多氯联苯和/或多溴二苯醚对耳蜗功能的影响。

Effects of developmental exposure to polychlorinated biphenyls and/or polybrominated diphenyl ethers on cochlear function.

机构信息

Neuroscience Program, University of Illinois at Urbana-Champaign, Urbana, Illinois 61802, USA.

出版信息

Toxicol Sci. 2011 Nov;124(1):161-8. doi: 10.1093/toxsci/kfr214. Epub 2011 Aug 26.

DOI:10.1093/toxsci/kfr214
PMID:21873374
原文链接:https://pmc.ncbi.nlm.nih.gov/articles/PMC3196655/
Abstract

Developmental exposure to polychlorinated biphenyls (PCBs) causes hearing loss that may be due to reduced thyroxine during cochlear development. Polybrominated diphenyl ethers (PBDEs) are structurally similar to PCBs and reduce thyroxine. This study utilized an environmental PCB mixture and a commercial PBDE mixture, DE-71, that represents the PBDEs found in humans to assess the potential for additive effects of PCBs and PBDEs on cochlear function. Female Long-Evans rats were dosed with corn oil vehicle, PCBs (3 or 6 mg/kg), molar equivalent doses of PBDEs (5.7 or 11.4 mg/kg), 3 mg/kg PCBs + 5.7 mg/kg PBDEs, or 6 mg/kg PCBs + 11.4 mg/kg PBDEs throughout gestation and lactation. At weaning, pup blood was taken to assess thyroxine concentrations. One male and one female from each litter were maintained until adulthood for distortion product otoacoustic emission (DPOAE) measurements of cochlear function. DPOAE amplitudes were decreased and thresholds were elevated in the 6 mg/kg PCB group. Exposure to PBDEs did not cause DPOAE deficits. There was an interactive effect from combined exposure such that the individual low doses of PCBs and PBDEs did not result in DPOAE deficits, but the two combined produced a deficit similar to that in the high-dose PCB group. Serum thyroxine concentrations of all groups were reduced compared with controls, but PBDEs produced a less dramatic reduction than PCBs, which could explain the lack of DPOAE effects. Importantly, there was evidence that the co-exposure to subthreshold doses of PCBs and PBDEs can have an additive effect on cochlear function.

摘要

发育过程中接触多氯联苯(PCBs)会导致听力损失,这可能是由于耳蜗发育过程中甲状腺素减少所致。多溴二苯醚(PBDEs)与 PCB 结构相似,会减少甲状腺素。本研究利用环境 PCB 混合物和商业 PBDE 混合物 DE-71(代表人类体内发现的 PBDE)来评估 PCB 和 PBDE 对耳蜗功能的潜在相加作用。雌性长耳大白鼠在妊娠和哺乳期接受玉米油载体、PCB(3 或 6mg/kg)、PBDE 摩尔当量剂量(5.7 或 11.4mg/kg)、3mg/kg PCB+5.7mg/kg PBDE 或 6mg/kg PCB+11.4mg/kg PBDE 处理。断奶时,取幼仔血液以评估甲状腺素浓度。每个窝中各取一雄一雌幼仔饲养至成年,用于耳蜗功能的畸变产物耳声发射(DPOAE)测量。6mg/kg PCB 组的 DPOAE 幅度降低,阈值升高。暴露于 PBDE 不会导致 DPOAE 缺陷。联合暴露存在交互作用,即单独低剂量的 PCB 和 PBDE 不会导致 DPOAE 缺陷,但两者联合产生的缺陷与高剂量 PCB 组相似。与对照组相比,所有组的血清甲状腺素浓度均降低,但 PBDE 产生的降低幅度小于 PCB,这可以解释 DPOAE 效应缺乏的原因。重要的是,有证据表明,亚阈值剂量的 PCB 和 PBDE 共同暴露会对耳蜗功能产生相加作用。