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固相萃取-气相色谱-串联质谱联用技术测定水中16种多环芳烃

Determination of 16 polycyclic aromatic hydrocarbons in water by solid phase extraction-gas chromatography-tandem mass spectrometry combination technique

  • 摘要: 水中多环芳烃(PAHs)可致癌、致畸、致突变,危害生态系统,威胁人体健康,准确、便捷测定水中多环芳烃的含量具有重要意义。本文采用固相萃取(SPE)富集水样,氮吹浓缩,采用气相色谱-串联质谱法(GC-MS/MS)多反应监测模式(MRM)完成样品定性定量分析。实验对不同萃取方式、不同萃取柱类型、萃取溶液pH值、基体改进剂类型、余氯含量及去除方法、萃取水样体积、色谱与质谱条件进行优化,选择1 000 mL水样用0.1 g抗坏血酸去除余氯,用磷酸调节pH≤2,加25 g氯化钠、10 mL异丙醇-10 mL正己烷作为基体改进剂后以多环芳烃专用(MIP-PAHs)固相萃取柱为载体全自动固相萃取的方法富集水中的16种PAHs。16种PAHs在5.0~250μg/L线性范围内校准曲线的线性相关系数均不小于0.999 5;方法中16种PAHs的检出限为0.89~1.97 ng/L,定量限为3.56~7.88 ng/L。按照实验方法测定地下水、地表水、饮用水、自来水4个水质类型的实际样品,平行样品的相对偏差为0.11%~11.5%,加标回收率为79.0%~123%;对某焦化厂地周边的有潜在污染风险的地下水、地表水、饮用水及流经的自来水进行测定,结果的相对标准偏差(RSD,n=7)为1.9%~12%,加标回收率为71.5%~119%。

     

    Abstract: Polycyclic aromatic hydrocarbons(PAHs) in water can cause cancer, teratogenesis and mutagenesis, which are harmful to ecosystems and human health. Therefore, the accurate and convenient determination of PAHs content in water is of great significance. In this study, the water samples were enriched by solid-phase extraction(SPE). After concentration by nitrogen blowing, the qualitative and quantitative analysis of samples was conducted by gas chromatography-tandem mass spectrometry(GC-MS/MS) in multiple reaction monitoring(MRM) mode. The experimental parameters were optimized, including different extraction methods, types of extraction columns, pH of extraction solution, types of matrix modifiers, residual chlorine content and removal methods, volume of extracted water samples, and chromatographic and mass spectrometric conditions. 0.1 g of ascorbic acid was added into 1 000 mL of water sample to remove the residual chlorine followed by adjusting pH ≤ 2 with phosphoric acid. Then 25 g of sodium chloride, 10 mL of isopropanol and 10 mL of n-hexane were added as the matrix modifiers. Finally, 16 kinds of PAHs in water were enriched by automatic solid-phase extraction using MIP-PAHs solid-phase extraction column as the carrier. The linear correlation coefficients of calibration curves for 16 PAHs in the linear range of 5.0-250 μg/L were all not less than 0.999 5. The limits of detection in this method for 16 PAHs were 0.89-1.97 ng/L, and the limits of quantification were 3.56-7.88 ng/L. Four actual water samples, including underground water, surface water, drinking water, and tap water, were determined according to the experimental method. The relative deviations of parallel samples were 0.11%-11.5%, and the spiked recoveries were 79.0%-123%. Samples of groundwater, surface water, drinking water, and tap water from the supply network with potential pollution risks around a coking plant were quantitatively analyzed.The relative standard deviations(RSD, n=7) of determination results were 1.9%-12%, and the spiked recoveries were between 71.5% and 119%.

     

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