Hornung Michael W, Tapper Mark A, Denny Jeffrey S, Sheedy Barbara R, Erickson Raymond, Sulerud Taylor J, Kolanczyk Richard C, Schmieder Patricia K
US Environmental Protection Agency, Office of Research and Development, National Health and Environmental Effects Research Laboratory, Mid-Continent Ecology Division, Duluth, MN.
Appl In Vitro Toxicol. 2017 Jun 1;3(2):163-181. doi: 10.1089/aivt.2016.0021.
The potential for chemicals to affect endocrine signaling is commonly evaluated via receptor binding and gene activation, but these assays, especially antagonism assays, have potential artifacts that must be addressed for accurate interpretation. Results are presented from screening 94 chemicals from 54 chemical groups for estrogen receptor (ER) activation in a competitive rainbow trout ER (rtER) binding assay and a trout liver slice vitellogenin mRNA expression assay. Results from true competitive agonists and antagonists, and inactive chemicals with little or no indication of ER binding or gene activation were easily interpreted. However, results for numerous industrial chemicals were more challenging to interpret, including chemicals with: (1) apparent competitive binding curves but no gene activation, (2) apparent binding and gene inhibition with evidence of either cytotoxicity or changes in assay media pH, (3) apparent binding but non-competitive gene inhibition of unknown cause, or (4) no rtER binding and gene inhibition not due to competitive ER interaction but due to toxicity, pH change, or some unknown cause. The use of endpoints such as toxicity, pH, precipitate formation, and determination of inhibitor dissociation constants (Ki) for interpreting the results of antagonism and binding assays for diverse chemicals is presented. Of the 94 chemicals tested for antagonism only two, tamoxifen and ICI-182780, were found to be true competitive antagonists. This report highlights the use of two different concentrations of estradiol tested in combination with graded concentrations of test chemical to provide the confirmatory evidence to distinguish true competitive antagonism from apparent antagonism.
通常通过受体结合和基因激活来评估化学物质影响内分泌信号传导的潜力,但这些检测方法,尤其是拮抗检测方法,存在一些潜在的假象,为了准确解读结果必须加以解决。本文展示了在竞争性虹鳟雌激素受体(rtER)结合试验和鳟鱼肝切片卵黄蛋白原mRNA表达试验中,对来自54个化学组的94种化学物质进行雌激素受体(ER)激活筛选的结果。真正的竞争性激动剂和拮抗剂以及几乎没有或没有ER结合或基因激活迹象的无活性化学物质的结果很容易解读。然而,许多工业化学品的结果更具挑战性,包括以下几种化学品:(1)具有明显的竞争性结合曲线但无基因激活;(2)具有明显的结合和基因抑制,同时有细胞毒性或检测介质pH值变化的证据;(3)具有明显的结合但原因不明的非竞争性基因抑制;(4)无rtER结合且基因抑制并非由于竞争性ER相互作用,而是由于毒性、pH值变化或某些未知原因。本文介绍了使用毒性、pH值、沉淀形成等终点指标以及抑制剂解离常数(Ki)的测定来解读不同化学品的拮抗和结合试验结果。在测试的94种用于拮抗作用的化学品中,仅发现他莫昔芬和ICI - 182780这两种是真正的竞争性拮抗剂。本报告强调了使用两种不同浓度的雌二醇与分级浓度的测试化学品联合测试,以提供确证证据来区分真正的竞争性拮抗作用和表观拮抗作用。