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经优化的 H4IIE-luc 体外生物测定用 PCDDs、PCDFs 和非邻位取代 PCBs 的修订相对效力值。

Revised relative potency values for PCDDs, PCDFs, and non-ortho-substituted PCBs for the optimized H4IIE-luc in vitro bioassay.

机构信息

NeoEnBiz Co, Daewoo Technopark, 1306, Bucheon, Republic of Korea.

出版信息

Environ Sci Pollut Res Int. 2013 Dec;20(12):8590-9. doi: 10.1007/s11356-013-1770-2. Epub 2013 May 21.

Abstract

While the World Health Organization 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) equivalency factors are useful estimates of relative potencies of mixtures when conducting risk assessments, they are not useful when comparing the results of bioassays such as the H4IIE-luc to concentrations of TCDD equivalents calculated from instrumental analyses. Since there are thousands of dioxin-like compounds (DLCs), one use of screening assays is to determine if all of the aryl hydrocarbon receptor (AhR) active DLCs in a mixture have been accounted for in instrumental analyses. For this purpose, bioassay-specific relative potency (ReP) values are needed. RePs of 21 polychlorinated dibenzo-p-dioxins, polychlorinated dibenzofurans, and dioxin-like polychlorinated biphenyls that exhibit effects mediated through the AhR were determined by use of the H4IIE-luc assay. Different values of RePs are derived, depending on the statistical, curve-fitting methods used to derive them from the dose-response relationships. Here, we discuss the various methods for deriving RePs from in vitro data and their assumptions and effects on values of RePs. Full dose-response curves of 2,3,7,8-TCDD and other representative DLCs were used to estimate effective concentrations at multiple points (e.g., EC20-50-80), which were then used to estimate ReP of each DLC to 2,3,7,8-TCDD.

摘要

虽然世界卫生组织(WHO)2,3,7,8-四氯二苯并对二恶英(TCDD)当量因子在进行风险评估时是混合物相对效力的有用估计值,但在比较生物测定(如 H4IIE-luc)的结果与仪器分析计算的 TCDD 当量浓度时,它们并不有用。由于存在数千种二恶英样化合物(DLCs),筛选测定法的一种用途是确定混合物中所有芳基烃受体(AhR)活性 DLCs 是否已在仪器分析中得到说明。为此,需要使用生物测定法特异性相对效力(ReP)值。使用 H4IIE-luc 测定法测定了 21 种多氯二苯并对二恶英、多氯二苯并呋喃和表现出通过 AhR 介导的作用的二恶英样多氯联苯的 ReP。根据从剂量-反应关系推导出它们的统计、曲线拟合方法,得出不同的 ReP 值。在这里,我们讨论了从体外数据推导出 ReP 的各种方法及其假设以及对 ReP 值的影响。使用 2,3,7,8-TCDD 和其他代表性 DLC 的完整剂量-反应曲线来估计多个点的有效浓度(例如,EC20-50-80),然后使用这些浓度来估计每个 DLC 相对于 2,3,7,8-TCDD 的 ReP。

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