Ellington J Jackson, Washington John W, Evans John J, Jenkins Thomas M, Hafner Sarah C, Neill Michael P
US Environmental Protection Agency, National Exposure Research Laboratory, 960 College Station Road, Athens, GA 30605, USA.
J Chromatogr A. 2009 Jul 10;1216(28):5347-54. doi: 10.1016/j.chroma.2009.05.035. Epub 2009 May 21.
This article describes the development of an analytical method for the determination of fluorotelomer alcohols (FTOHs) in soil. The sensitive and selective determination of the telomer alcohols was performed by extraction with methyl tert-butyl ether (MTBE) and analysis of the extract using gas chromatography with detection and quantification by mass spectrometry operated in the positive chemical ionization mode. The protonated molecular ion, M+H and a fragment ion (loss of HF+H(2)O) m/z 38 less than the molecular ion were monitored to identify tentatively FTOHs in MTBE extracts of contaminated soils. The FTOHs were confirmed by treatment of the extract with a silylation reagent and observing the disappearance of the FTOH response and the appearance of peaks attributable to the M+H ions of the trimethylsilyl derivatives. Mass-labeled FTOHs were used as recovery and matrix internal standards. Recovery experiments on soils shown to be free of endogenous FTOHs at instrument detection limits (IDL) of 16 fg/microL for 6:2 FTOH, 10 fg/microL for 8:2 FTOH and 14 fg/microL for 10:2 FTOH yielded a limit of quantitation (LOQ) of 190, 100, and 160 fg/microL for 6:2 FTOH, 8:2 FTOH, and 10:2 FTOH, respectively when 3 g samples of soil were extracted with 1 mL MTBE. The levels of the 6:2 FTOH, 8:2 FTOH, and 10:2 FTOH in five soils contaminated with FTOHs by exposure to the laboratory atmosphere during air drying were determined. In these air-dried soils, concentrations of FTOHs ranged from non-detectable to 3600 fg/microL (0.6 ng/g) of the 6:2 FTOH in the extract of a commercial topsoil. This method was used to determine even and odd numbered FTOHs from 6:2 through 14:2 in soils from fields that had received applications of sewage sludge. Concentrations of FTOHs in these sludge-applied soils ranged as high as 820 ng/g of dry soil for the 10:2 FTOH.
本文介绍了一种测定土壤中氟调聚物醇(FTOHs)的分析方法。通过用甲基叔丁基醚(MTBE)萃取并使用气相色谱对萃取物进行分析,以正化学电离模式进行质谱检测和定量,从而对端粒醇进行灵敏且选择性的测定。监测质子化分子离子M+H和比分子离子小38 m/z的碎片离子(损失HF + H₂O),以初步鉴定受污染土壤的MTBE萃取物中的FTOHs。通过用硅烷化试剂处理萃取物,并观察FTOH响应的消失以及归因于三甲基硅基衍生物的M+H离子的峰的出现,来确认FTOHs。使用质量标记的FTOHs作为回收率和基质内标。对在仪器检测限(IDL)下显示不含内源性FTOHs的土壤进行回收率实验,6:2 FTOH的IDL为16 fg/μL,8:2 FTOH为10 fg/μL,10:2 FTOH为14 fg/μL,当用1 mL MTBE萃取3 g土壤样品时,6:2 FTOH、8:2 FTOH和10:2 FTOH的定量限(LOQ)分别为190、100和160 fg/μL。测定了五种在空气干燥过程中因暴露于实验室大气而被FTOHs污染的土壤中6:2 FTOH、8:2 FTOH和10:2 FTOH的含量。在这些风干土壤中,FTOHs的浓度范围从不可检测到商业表土萃取物中6:2 FTOH的3600 fg/μL(0.6 ng/g)。该方法用于测定来自施用污水污泥田地的土壤中从6:2到14:2的偶数和奇数编号的FTOHs。在这些施用污泥的土壤中,10:2 FTOH的浓度高达820 ng/g干土。