Department of Chemistry, Université de Montréal, Montreal, QC, Canada; Department of Civil, Geological and Mining Engineering, École Polytechnique de Montréal, Montreal, QC, Canada.
Department of Chemistry, Université de Montréal, Montreal, QC, Canada.
J Chromatogr A. 2019 Apr 26;1591:87-98. doi: 10.1016/j.chroma.2019.01.016. Epub 2019 Jan 8.
The list of endocrine disrupting compounds (EDCs) defined under U.S. EPA Method 539 was recently expanded to include additional hormones and bisphenol A (BPA). Here, we validated a fast and robust alternative method compliant with Method 539.1 requirements in diverse water matrixes (i.e., ultra-pure water, tap water, surface water, and wastewater influent and effluent). Automated large volume injection solid phase extraction (SPE) coupled on-line to ultra-high-performance liquid chromatography tandem mass spectrometry (UHPLC-MS/MS) was investigated for this purpose. The surveyed molecules included 13 EPA-priority hormones (testosterone, progesterone, medroxyprogesterone, levonorgestrel, norethindrone, androstenedione, estrone, β-estradiol, α-estradiol, equilin, equilenin, ethinylestradiol, estriol) and BPA. Combinations of ionization source and mobile phases were optimized for improved sensitivity. Suitable chromatographic performances were obtained and the implementation of an on-line SPE washing step consecutive to sample loading was investigated. On-line SPE extraction efficiencies in acceptable ranges (64-79%) and detection limits in the order of nanogram per liter or sub-nanogram per liter were obtained. The linearity range extended over 2-3 orders of magnitude, with determination coefficients (R) typically > 0.9980. Robust precision and trueness complying with acceptance criteria (70-130%) were obtained for the scope of analytes/matrix combinations. Limited internal standard variations were also observed across samples (±18%), well within the ±50% acceptance criterion. The method was successfully applied to field-collected samples in Canada and summed EDC concentrations were reported in the range of 0.80-2.8 ng L, 6.8-19 ng L, 260-790 ng L, and 37-360 ng L in tap water, surface water, effluent and influent wastewater samples, respectively.
美国环保署方法 539 定义的内分泌干扰化合物 (EDC) 清单最近扩大到包括其他激素和双酚 A (BPA)。在这里,我们验证了一种符合方法 539.1 要求的快速而强大的替代方法,该方法可用于多种水基质(即超纯水、自来水、地表水以及废水进水和出水)。为此,研究了自动化大体积进样固相萃取 (SPE) 与超高效液相色谱串联质谱 (UHPLC-MS/MS) 在线联用。调查的分子包括 13 种美国环保署优先考虑的激素(睾酮、孕酮、甲羟孕酮、左炔诺孕酮、诺孕酯、雄烯二酮、雌酮、β-雌二醇、α-雌二醇、马烯雌酮、马烯雌酮、乙炔雌二醇、雌三醇)和 BPA。优化了离子源和流动相的组合以提高灵敏度。获得了合适的色谱性能,并研究了在样品加载后连续进行在线 SPE 洗涤步骤的可行性。在可接受范围内(64-79%)获得了在线 SPE 提取效率和纳克/升或亚纳克/升级别的检测限。线性范围扩展到 2-3 个数量级,测定系数 (R) 通常大于 0.9980。对于分析物/基质组合的范围,获得了符合接受标准(70-130%)的稳健精密度和准确度。还观察到样品内的内标变化有限(±18%),远在±50%的接受标准范围内。该方法成功应用于在加拿大采集的现场样本,并报告了自来水中 EDC 浓度范围为 0.80-2.8ng/L、地表水为 6.8-19ng/L、废水出水中为 260-790ng/L、废水中为 37-360ng/L。