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采用手性液相色谱-四极杆飞行时间质谱法对手表和废水中的药物和非法药物进行对映体水平分析。

Using chiral liquid chromatography quadrupole time-of-flight mass spectrometry for the analysis of pharmaceuticals and illicit drugs in surface and wastewater at the enantiomeric level.

机构信息

University of Bath, Department of Chemistry, Faculty of Science, Bath BA2 7AY, UK.

出版信息

J Chromatogr A. 2012 Aug 3;1249:115-29. doi: 10.1016/j.chroma.2012.06.012. Epub 2012 Jun 12.

DOI:10.1016/j.chroma.2012.06.012
PMID:22749459
Abstract

This paper presents and compares for the first time two chiral LC-QTOF-MS methodologies (utilising CBH and Chirobiotic V columns with cellobiohydrolase and vancomycin as chiral selectors) for the quantification of amphetamine, methamphetamine, MDA (methylenedioxyamphetamine), MDMA (methylenedioxymethamphetamine), propranolol, atenolol, metoprolol, fluoxetine and venlafaxine in river water and sewage effluent. The lowest MDLs (0.3-5.0 ng L(-1) and 1.3-15.1 ng L(-1) for river water and sewage effluent respectively) were observed using the chiral column Chirobiotic V. This is with the exception of methamphetamine and MDMA which had lower MDLs using the CBH column. However, the CBH column resulted in better resolution of enantiomers (R(s)=2.5 for amphetamine compared with R(s)=1.2 with Chirobiotic V). Method recovery rates were typically >80% for both methodologies. Pharmaceuticals and illicit drugs detected and quantified in environmental samples were successfully identified using MS/MS confirmation. In sewage effluent, the total beta-blocker concentrations of propranolol, atenolol and metoprolol were on average 77.0, 1091.0 and 3.6 ng L(-1) thus having EFs (Enantiomeric Fractions) of 0.43, 0.55 and 0.54 respectively. In river water, total propranolol and atenolol was quantified on average at <10.0 ng L(-1). Differences in EF between sewage and river water matrices were evident: venlafaxine was observed with respective EF of 0.43 ± 0.02 and 0.58 ± 0.02.

摘要

本文首次提出并比较了两种手性 LC-QTOF-MS 方法(分别使用 CBH 和 Chirobiotic V 柱,以纤维二糖水解酶和万古霉素作为手性选择剂),用于定量检测河水中的安非他命、甲基苯丙胺、MDA(亚甲二氧基苯丙胺)、MDMA(亚甲二氧基甲基苯丙胺)、普萘洛尔、阿替洛尔、美托洛尔、氟西汀和文拉法辛,以及污水中的上述物质。使用手性柱 Chirobiotic V 时,最低检测限(MDL)为 0.3-5.0ng/L(河水)和 1.3-15.1ng/L(污水)。这一结果与使用 CBH 柱时,仅甲基苯丙胺和 MDMA 的 MDL 较低的情况形成对比。然而,CBH 柱在手性异构体的分离度方面表现更好(安非他命的分离度 R(s)=2.5,而 Chirobiotic V 柱为 R(s)=1.2)。两种方法的药物回收率通常都大于 80%。使用 MS/MS 确证,成功识别了环境样品中检测到的药物和非法药物。在污水中,普萘洛尔、阿替洛尔和美托洛尔的总β-阻断剂浓度平均分别为 77.0、1091.0 和 3.6ng/L,其对映体分数(EF)分别为 0.43、0.55 和 0.54。在河水中,普萘洛尔和阿替洛尔的总浓度平均低于 10.0ng/L。污水和河水基质之间的 EF 差异明显:文拉法辛的 EF 分别为 0.43±0.02 和 0.58±0.02。

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