Department of Analytical Chemistry, Nutrition and Food Sciences, Institute for Food Analysis and Research-IIAA, University of Santiago de Compostela, 15782 Santiago de Compostela, Spain.
Anal Chim Acta. 2011 Jan 17;684(1-2):50-7. doi: 10.1016/j.aca.2010.10.049. Epub 2010 Nov 9.
A fully automated method for the determination of triclosan (TCS), its derivative methyl triclosan (MeTCS) and six parabens (esters of 4-hydroxybenzoic acid) including branched and linear isomers of propyl (i-PrP and n-PrP) and butyl paraben (i-BuP and n-BuP) in sewage water samples is presented. The procedure includes analytes enrichment by microextraction by packed sorbent (MEPS) coupled at-line to large volume injection-gas chromatography-mass spectrometry (LVI-GC-MS). Under optimised conditions, compounds were extracted from 2 mL samples, adjusted at pH 3, using a C18 MEPS-sorbent. Adsorbed analytes were eluted directly into the Programmable Temperature Vaporizer (PTV) injector of the chromatograph with 2×25 μL of ethyl acetate. They were quantified using standard solutions in ultrapure water submitted to the same sample enrichment process as real sewage water samples. After signal normalisation using isotopic labelled species as internal surrogates, no differences were noticed among the extraction efficiency for sewage and ultrapure water; moreover, the proposed method reported lineal calibration curves from 0.1 to 10 ng mL(-1), relative standard deviations (%RSD) between 2 and 7.1% and limits of detection (LODs) varying from 0.001 to 0.015 ng mL(-1) in ultrapure water and from 0.02 to 0.59 ng mL(-1) in the most complex sample (raw wastewater).
一种全自动方法用于测定三氯生(TCS)、其衍生物甲基三氯生(MeTCS)和六种对羟基苯甲酸酯(对羟基苯甲酸的酯),包括丙基(异丙基和正丙基)和丁基对羟基苯甲酸酯(异丁基和正丁基)的支链和直链异构体,该方法应用于污水水样中。该程序包括通过微萃取填充吸附剂(MEPS)与大体积进样-气相色谱-质谱联用(LVI-GC-MS)在线联用进行分析物富集。在优化条件下,使用 C18 MEPS 吸附剂,将 pH 值调整为 3 的 2 mL 样品进行萃取。吸附的分析物直接用 2×25 μL 乙酸乙酯洗脱到色谱仪的可编程温度汽化器(PTV)进样器中。使用与真实污水水样相同的样品富集过程的超纯水标准溶液进行定量分析。在用同位素标记的物质作为内标进行信号归一化后,发现污水和超纯水的萃取效率没有差异;此外,该方法在超纯水中报告了 0.1 到 10 ng mL(-1)的线性校准曲线,相对标准偏差(%RSD)在 2 到 7.1%之间,在超纯水中的检测限(LOD)从 0.001 到 0.015 ng mL(-1)变化,在最复杂的样品(原废水)中从 0.02 到 0.59 ng mL(-1)变化。