2,3,7,8- tcdd或多氯联苯对甲状腺激素代谢的亚慢性影响:用于风险评估

Angélique P.J.M. Van Birgelen , Elisabeth A. Smit , Irene M. Kampen , Coralie N. Groeneveld , Kitty M. Fase , Jolanda Van der Kolk , Hermann Poiger , Martin Van den Berg , Jan H. Koeman , Abraham Brouwer
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引用次数: 127

摘要

研究了2,3,7,8-四氯二苯并对二恶英(TCDD)、3,3 '、4,4 '、5-五氯联苯(PCB 126)、2,3,3 '、4,4 '、5-六氯联苯(PCB 156)对雌性Sprague-Dawley大鼠13周喂养后甲状腺激素代谢的影响。在饲粮中分别添加浓度为0.2 ~ 20 μg/kg TCDD、7 ~ 180 μg/kg PCB 126和12 mg/kg PCB 156的试验化合物。血浆总甲状腺素(TT4)水平的降低与微粒体II期酶udp -葡萄糖醛基转移酶(T4UGT)的诱导之间存在显著相关性。此外,这些化合物对某些I期和II期同工酶,如细胞色素P450 1A1 (CYP1A1)和UGT1A1的共诱导,清楚地表明,Ah受体介导的机制参与了这些多卤芳香族化合物对甲状腺激素代谢的干扰。这些结果为利用多卤芳香族化合物对甲状腺激素代谢的某些影响进行风险评估提供了机制基础。通过使用这些效应,PCB 126和PCB 156相对于TCDD的效价分别为0.008至0.1和0.00007至0.004。通过使用其他一些众所周知的Ah受体介导的毒性和生化参数,这些值与PCB 126和PCB 156的相对效价非常吻合。
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Subchronic effects of 2,3,7,8-TCDD or PCBs on thyroid hormone metabolism: use in risk assessment

Effects of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD), 3,3′,4,4′,5-pentachlorobiphenyl (PCB 126), 2,3,3′,4,4′,5-hexachlorobiphenyl (PCB 156) on thyroid hormone metabolism were studied in 13-week feeding studies in female Sprague-Dawley rats. The diets were supplemented with the compounds tested at concentrations ranging from 0.2 to 20 μg/kg diet for TCDD, 7 to 180 μg/kg diet for PCB 126, or 12 mg/kg diet for PCB 156, respectively. Significant correlations were found for all three compounds between reductions in plasma total thyroxine (TT4) levels and inductions of the microsomal phase II enzyme UDP-glucuronosyltransferase by using T4 as a substrate (T4UGT). Furthermore, the coinduction of certain phase I and II isozymes, i.c., cytochrome P450 1A1 (CYP1A1) and UGT1A1, by these compounds, clearly suggests the involvement of an Ah receptor-mediated mechanism in the disturbance of thyroid hormone metabolism by these polyhalogenated aromatic compounds. These results provide a mechanistic base for the use of certain effects on thyroid hormone metabolism by polyhalogenated aromatic compounds in risk assessment. By using these effects, potencies of PCB 126 and PCB 156 relative to TCDD ranged from 0.008 to 0.1 for PCB 126, and from 0.00007 to 0.004 for PCB 156, respectively. These values correspond very well with relative potencies of PCB 126 and PCB 156 by using some other well-known Ah receptor-mediated toxic and biochemical parameters.

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