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多氯联苯鸡胚肝细胞生物活性非单调剂量-响应关系的QSARs研究 被引量:1

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摘要 毒理学研究发现,环境内分泌干扰物(EDCs)在低于无可见效应浓度(NOAEL)时可诱发更强的生物学效应,导致剂量效应曲线背离了经典毒理学理论而呈现U型或倒U型.在此种情况下,毒理研究中普遍采用的半数效应质量/浓度等活性指标不再唯一,给定量结构活性相关(QSARs)方法的应用造成困难.多氯联苯(PCBs)作为典型环境内分泌干扰物,在诱导鸡胚肝细胞EROD酶活性中呈现特殊非单调剂量-响应关系,在高低剂量范围内毒理机制存在差异,因此如何应用QSARs方法研究不同剂量段的毒性效应是本文主要解决的问题.为探索其可能的生化机制,本文利用Chemoffice软件内置的AM1半经验量子化学方法对多氯联苯化合物进行能量优化,建立结构描述符库;并在DELLPrecision370工作站上,采用SYBYL7.0(Tripos,Inc.Co)中的FlexX模块分别对39种PCBs和芳烃受体相似蛋白FixL进行分子对接,成功模拟不同结构类型PCBs的结合模式并获得PCBs和芳烃受体相互作用结合能.基于多元线性回归分析分别建立了高低剂量下PCBs对鸡胚肝细胞EROD活性影响的QSAR模型,在此基础上推测低剂量下11种PCBs主要通过芳烃受体介导发挥其对鸡胚肝细胞细胞色素P4501A正常生理功能的干扰效应,而高剂量下PCBs对鸡胚肝细胞产生急性毒性.究其可能的原因是处于低剂量的PCBs与特定受体结合作用起到主导地位;随剂量增加,细胞内的反馈调节作用使得EROD趋势减缓;而在剂量升高到一定程度,表现出一定反应性急性毒性机制,从而对鸡胚肝细胞的结构与功能产生损伤.
出处 《中国科学(B辑)》 CSCD 北大核心 2008年第12期1105-1112,共8页 Science in China(Series B)
基金 国家自然科学基金(批准号:20777035,20737001) 国家高技术研究发展计划(编号:2007AA06Z416,2006AA06Z424,2007AA06A405)资助项目
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  • 1Saal F S, Timms B G, Montano M M, Palanza P, Thayer K A, Nagel S C, Dhar M D, Ganjam V K, Parmigiani S, Welshons W S Prostate enlargement in mice due to fetal exposure to low doses of estradiol or diethylstilbestrol and opposite effects at high doses Proc Nad Acad Sci USA, 1997, 94:2056-2061.
  • 2Wetherill Y B, Petre C E, Monk K R, Puga A, Knudsen K E. The xenoestrogen bisphenol A induces inappropriate androgen receptor activation and mitogenesis in prostatic adenocarcinoma cells. Mol Cancer Ther, 2002, 1:515-524.
  • 3Saal F S, Nagel S C, Palanza P, Boechler M, Parmigiani S, Welshons W S. Estrogenic pesticides: binding relative to estradiol in MCF-7 cells and effects of exposure during fetal life on subsequent territorial behaviour in male mice. Toxicol Lett, 1995, 77:343-350.
  • 4Zala S M, Penn D J. Abnormal behaviours induced by chemical pollution: a review of the evidence and new challenges. Anim Behav, 2004, 68:649-664.
  • 5Miao X S, Chu S G, Xu X B. Advances in the research of structure-activity relation ships for polychlorinated biphenyls. Prog Chem, 1996, 8(4): 293-300.
  • 6Welshons W V, Thayer K A, Judy B M, Taylor J A, Curran E M, Saal F S. Large effects from small exposures. I. Mechanisms for en- docrine-disrupting chemicals with estrogenic activity. Environ Health Perspect, 2003, 111(8): 994-1006.
  • 7Kennedy S W, Lorenzen A, Norstrom R J. Chicken embryo hepatocyte bioasay for measuring cytochrome P4501A-based 2,3,7,8-tetrachloro dibenzopdioxin equivalent concentrations in environmental samples. Environ Sci Technol, 1996, 30:706-715.
  • 8Safe S, Bandiera S, Sawyer T, Zmudzka B, Mason G, Romkes M. Effects of structure on binding to the 2,3,7,8-TCDD receptor protein and AHH induction-halogenated biphenyls. Environ Health Perspect, 1985, 61:21-23.
  • 9Safe S. Polychlorinated biphenyls (PCBs), dibenzo-p-dioxins (PCDDs), dibenzofurans (PCDFs), and related compounds: environmental and mechanistic considerations which support the development of toxic equivalency factors (TEFs). Crit Rev Toxicol, 1990, 21:51-88.
  • 10Bandiera S, Sawyer T W, Campbell M A, Fujita T, Safe S. Competitive binding to the cytosolic 2,3,7,8-tetrachlorodibenzo-p-dioxin receptor: effects of structure on the affinities of substituted halogenated biphenyls a QSAR analysis. Biochem Pharmacol, 1983, 32: 3803-3813.

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