马杰, 石矛, 王辉龙, 王蕴馨. GC-MS测定生活饮用水及水源水中6种酰胺类除草剂[J]. 环境卫生学杂志, 2021, 11(6): 537-541. DOI: 10.13421/j.cnki.hjwsxzz.2021.06.010
    引用本文: 马杰, 石矛, 王辉龙, 王蕴馨. GC-MS测定生活饮用水及水源水中6种酰胺类除草剂[J]. 环境卫生学杂志, 2021, 11(6): 537-541. DOI: 10.13421/j.cnki.hjwsxzz.2021.06.010
    MA Jie, SHI Mao, WANG Huilong, WANG Yunxin. Determination of Six Amide Herbicides in Drinking Water and Source Water by GC-MS[J]. Journal of Environmental Hygiene, 2021, 11(6): 537-541. DOI: 10.13421/j.cnki.hjwsxzz.2021.06.010
    Citation: MA Jie, SHI Mao, WANG Huilong, WANG Yunxin. Determination of Six Amide Herbicides in Drinking Water and Source Water by GC-MS[J]. Journal of Environmental Hygiene, 2021, 11(6): 537-541. DOI: 10.13421/j.cnki.hjwsxzz.2021.06.010

    GC-MS测定生活饮用水及水源水中6种酰胺类除草剂

    Determination of Six Amide Herbicides in Drinking Water and Source Water by GC-MS

    • 摘要:
      目的 建立生活饮用水及水源水中甲草胺、乙草胺、丙草胺、丁草胺、异丙草胺、异丙甲草胺的气相色谱—质谱联用(GC-MS)测定方法。
      方法 水样中6种酰胺类除草剂通过C18固相萃取柱吸附萃取, 用乙酸乙酯洗脱, 洗脱液经脱水、浓缩定容后, 用GC-MS分析测定。根据待测物的保留时间和质谱图定性, 再通过待测物的定量离子外标法定量。
      结果 本法分离效果好, 测定曲线浓度范围(5.0 ~ 250)μg/L, 若取水样500 mL浓缩至1.0 mL测定, 样品测定的最低检测质量浓度为0.01 μg/L。当样品加标浓度为0.02、0.20和0.50 μg/L时, 方法的加标回收率范围为78.6% ~ 106.4%, 连续测定6次, 相对标准偏差(RSD)为1.7% ~ 6.8%。对待测组分在水中的稳定性进行研究表明, 样品于4 ℃保存24 h后仍可获得较稳定的结果。
      结论 该方法操作简便, 灵敏度高, 可用于生活饮用水及水源水中6种酰胺类除草剂的测定。

       

      Abstract:
      Objective To establish a method for the determination of alachlor, acetochlor, pretilachlor, butachlor, propisochlor and metolachlor in drinking water and source water by gas chromatography-mass spectrometry (GC-MS).
      Methods Six amide herbicides in water samples were extracted by a C18 solid-phase extraction column and eluted with ethyl acetate. The eluent was dehydrated, concentrated to a fixed volume, and then separated and determined by GC-MS. A qualitative analysis was performed based on the retention time and mass spectrum of the substance to be determined, and a quantitative analysis was performed by the quantitative ion external standard method.
      Results This method had a good separation effect, and the concentration range was 5.0-250 μg/L on the determination curve, if 500 mL water sample was concentrated to 1.0 mL, the limit of detemination was 0.01 μg/L. When the spiked concentrations of the samples were 0.02, 0.20 and 0.50 μg/L, respectively, the recoveries of the method ranged from 78.6% to 106.4%, and the relative standard deviations were between 1.7% and 6.8% for six consecutive measurements. The stability of the components to be determined in water was studied, and the results showed that accurate results were obtained after the samples were stored at 4 ℃ for 24 hours.
      Conclusion The method is simple and highly sensitive and can be used for the determination of six amide herbicides in drinking water and source water.

       

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