Conley Justin M, Evans Nicola, Cardon Mary C, Rosenblum Laura, Iwanowicz Luke R, Hartig Phillip C, Schenck Kathleen M, Bradley Paul M, Wilson Vickie S
U.S. Environmental Protection Agency/National Health and Environmental Effects Research Laboratory/Toxicity Assessment Division , Research Triangle Park, North Carolina 27711 United States.
CB&I Federal Services , Cincinnati, Ohio 45212 United States.
Environ Sci Technol. 2017 May 2;51(9):4781-4791. doi: 10.1021/acs.est.6b06515. Epub 2017 Apr 12.
In vitro bioassays are sensitive, effect-based tools used to quantitatively screen for chemicals with nuclear receptor activity in environmental samples. We measured in vitro estrogen (ER), androgen (AR), and glucocorticoid receptor (GR) activity, along with a broad suite of chemical analytes, in streamwater from 35 well-characterized sites (3 reference and 32 impacted) across 24 states and Puerto Rico. ER agonism was the most frequently detected with nearly all sites (34/35) displaying activity (range, 0.054-116 ng E2Eq L). There was a strong linear relationship (r = 0.917) between in vitro ER activity and concentrations of steroidal estrogens after correcting for the in vitro potency of each compound. AR agonism was detected in 5/35 samples (range, 1.6-4.8 ng DHTEq L) but concentrations of androgenic compounds were largely unable to account for the in vitro activity. Similarly, GR agonism was detected in 9/35 samples (range, 6.0-43 ng DexEq L); however, none of the recognized GR-active compounds on the target-chemical analyte list were detected. The utility of in vitro assays in water quality monitoring was evident from both the quantitative agreement between ER activity and estrogen concentrations, as well as the detection of AR and GR activity for which there were limited or no corresponding target-chemical detections to explain the bioactivity. Incorporation of in vitro bioassays as complements to chemical analyses in standard water quality monitoring efforts would allow for more complete assessment of the chemical mixtures present in many surface waters.
体外生物测定是一种灵敏的、基于效应的工具,用于对环境样品中具有核受体活性的化学物质进行定量筛选。我们在来自美国24个州和波多黎各的35个特征明确的地点(3个参考点和32个受影响点)的溪水中,测量了体外雌激素(ER)、雄激素(AR)和糖皮质激素受体(GR)活性,以及一系列广泛的化学分析物。几乎所有地点(34/35)都检测到了ER激动作用,活性范围为0.054 - 116 ng E2Eq/L。在校正每种化合物的体外效力后,体外ER活性与甾体雌激素浓度之间存在很强的线性关系(r = 0.917)。在5/35的样品中检测到AR激动作用(范围为1.6 - 4.8 ng DHTEq/L),但雄激素化合物的浓度在很大程度上无法解释体外活性。同样,在9/35的样品中检测到GR激动作用(范围为6.0 - 43 ng DexEq/L);然而,在目标化学分析物列表中未检测到任何公认的GR活性化合物。从ER活性与雌激素浓度之间的定量一致性,以及检测到AR和GR活性(但相应的目标化学物质检测有限或没有,无法解释生物活性)可以明显看出体外测定在水质监测中的作用。在标准水质监测工作中,将体外生物测定作为化学分析的补充,可以更全面地评估许多地表水中存在的化学混合物。