Laws Susan C, Yavanhxay S, Cooper Ralph L, Eldridge J Charles
Reproductive Toxicology Division, National Health and Environmental Effects Research Laboratory, Office of Research and Development, U.S. Environmental Protection Agency, Mail-drop 72, Research Triangle Park, North Carolina 27711, USA.
Toxicol Sci. 2006 Nov;94(1):46-56. doi: 10.1093/toxsci/kfl092. Epub 2006 Aug 29.
This study was conducted to characterize the estrogen receptor (ER)-binding affinities of 50 chemicals selected from among the high production volume chemicals under the U.S. EPA's (U.S. Environmental Protection Agency's) Toxic Substances Control Act inventory. The chemicals were evaluated using the rat uterine cytosolic (RUC) ER-competitive binding assay, with secondary analysis using Lineweaver-Burk plots and slope replots to confirm true competitive inhibition and to determine an experimental K(i). Data from these ER-competitive binding assays represent the types of competitive binding curves that can be obtained when screening chemicals with broad structural diversity. True competitive inhibition was observed in 17 of 50 chemicals. Binding affinities were much lower than that of estradiol (E(2)) with K(i) concentrations ranging from 0.6 to 373 microM as compared with that of E(2) (0.77 nM). Other chemicals that appeared to displace radiolabeled E(2) binding to ER were, in fact, found not to be competitive inhibitors in the secondary K(i) experiments. These seven chemicals likely altered the stability of the assay by changing the buffer pH, denaturing ER, or disrupting the ER-binding kinetics. Thus, several conditions that may confound interpretation of RUC ER-binding assay data are illustrated. For another group of eight chemicals, neither an IC(50) nor K(i) could be determined due to solubility constraints. These chemicals exhibited slight (20-40%) inhibition at concentrations of 10-100 microM, suggesting that they could be competitors at very high concentrations, yet K(i) experiments were not possible as the limit of chemical solubility in the aqueous assay buffer was well above the IC(50). An additional 18 of the 50 chemicals were classified as nonbinders because in concentrations up to 100 microM they produced essentially no displacement of radiolabeled E(2). These results show that although the ER-competitive binding assay is a valuable tool for screening chemicals, secondary tests such as a double reciprocal Lineweaver-Burk experiment with slope replot should be used to confirm true competitive inhibition. This information will be useful for the ongoing validation of the RUC ER-competitive binding assay under the U.S. EPA's Endocrine Disruptor Screening Program, as well as to support research efforts to develop computational models designed to identify chemicals with the ability to bind to ER.
本研究旨在表征从美国环境保护局(EPA)《有毒物质控制法》清单中的高产量化学品中选出的50种化学品与雌激素受体(ER)的结合亲和力。使用大鼠子宫胞质(RUC)ER竞争性结合试验对这些化学品进行评估,并通过Lineweaver-Burk图和斜率重绘图进行二次分析,以确认真正的竞争性抑制并确定实验性抑制常数(K(i))。这些ER竞争性结合试验的数据代表了在筛选具有广泛结构多样性的化学品时可获得的竞争性结合曲线类型。在50种化学品中有17种观察到真正的竞争性抑制。与雌二醇(E(2))(0.77 nM)相比,结合亲和力远低于E(2),K(i)浓度范围为0.6至373 microM。实际上,在二次K(i)实验中发现,其他看似能取代放射性标记的E(2)与ER结合的化学品并非竞争性抑制剂。这七种化学品可能通过改变缓冲液pH值、使ER变性或破坏ER结合动力学而改变了试验的稳定性。因此,说明了几种可能混淆RUC ER结合试验数据解释的情况。对于另一组八种化学品,由于溶解度限制,既无法确定半数抑制浓度(IC(50))也无法确定K(i)。这些化学品在10至100 microM浓度下表现出轻微(20 - 40%)的抑制作用,表明它们在非常高的浓度下可能是竞争者,但由于水性试验缓冲液中化学品的溶解度极限远高于IC(50),因此无法进行K(i)实验。在50种化学品中,另有18种被归类为非结合剂,因为在高达100 microM的浓度下,它们基本上不会使放射性标记的E(2)发生位移。这些结果表明,尽管ER竞争性结合试验是筛选化学品的有价值工具,但应使用诸如双倒数Lineweaver-Burk实验及斜率重绘图等二次试验来确认真正的竞争性抑制。这些信息对于美国EPA内分泌干扰物筛选计划下正在进行的RUC ER竞争性结合试验的验证,以及支持旨在开发识别具有与ER结合能力化学品的计算模型的研究工作将是有用的。