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    柴瑞娜, 陈鹏飞, 成建国, 马力通, 段建国. 超声辅助乳化萃取结合气相色谱-质谱法测定废水中8种酚类污染物的含量[J]. 理化检验-化学分册, 2024, 60(8): 796-801. DOI: 10.11973/lhjy-hx230262
    引用本文: 柴瑞娜, 陈鹏飞, 成建国, 马力通, 段建国. 超声辅助乳化萃取结合气相色谱-质谱法测定废水中8种酚类污染物的含量[J]. 理化检验-化学分册, 2024, 60(8): 796-801. DOI: 10.11973/lhjy-hx230262
    CHAI Ruina, CHEN Pengfei, CHENG Jianguo, MA Litong, DUAN Jianguo. Determination of 8 Phenolic Pollutants in Wastewater by Gas Chromatography-Mass Spectrometry Coupled with Ultrasound-Assisted Emulsion Extraction[J]. PHYSICAL TESTING AND CHEMICAL ANALYSIS PART B:CHEMICAL ANALYSIS, 2024, 60(8): 796-801. DOI: 10.11973/lhjy-hx230262
    Citation: CHAI Ruina, CHEN Pengfei, CHENG Jianguo, MA Litong, DUAN Jianguo. Determination of 8 Phenolic Pollutants in Wastewater by Gas Chromatography-Mass Spectrometry Coupled with Ultrasound-Assisted Emulsion Extraction[J]. PHYSICAL TESTING AND CHEMICAL ANALYSIS PART B:CHEMICAL ANALYSIS, 2024, 60(8): 796-801. DOI: 10.11973/lhjy-hx230262

    超声辅助乳化萃取结合气相色谱-质谱法测定废水中8种酚类污染物的含量

    Determination of 8 Phenolic Pollutants in Wastewater by Gas Chromatography-Mass Spectrometry Coupled with Ultrasound-Assisted Emulsion Extraction

    • 摘要: 通过优化萃取条件和色谱条件,提出题示方法测定废水中苯酚、邻氯苯酚、邻甲酚、对甲酚、2,5-二甲基苯酚、3,5-二甲基苯酚、2,4-二甲基苯酚、喹啉等8种酚类污染物的含量。废水样品经沉淀、过滤后,分取样品20 mL,加入4.0 g氯化钠,振荡2 min。加入20 mL二氯甲烷,超声乳化萃取5 min,置于分液漏斗中静置5 min。分取有机相,于10 ℃浓缩至2~3 mL,用二氯甲烷稀释至5 mL。加入1 g无水硫酸钠,放置10 h,脱去水分,所得溶液进入气相色谱-质谱仪,在Agilent DB-VRX色谱柱(30 m×0.25 mm,1.4 μm)上程序升温分离样品溶液中8种酚类污染物,分别采用全扫描(SCAN)、选择离子监测(SIM)模式进行定性和定量分析。结果表明:8种酚类污染物的质量浓度在0.50~500.00 μg·L−1内和峰面积呈线性关系,检出限(3S/N)为0.02~0.07 μg·L−1。按照标准加入法进行回收试验,回收率为76.8%~114%,测定值的相对标准偏差(n=6)不大于10%。方法用于地表水和煤化工废水样品的分析,地表水中检出了2.40 μg·L−1苯酚和1.3 μg·L−1对甲酚,煤化工废水中检出了8种酚类污染物(检出量1.21~30.63 μg·L−1)。

       

      Abstract: By optimizing extraction and chromatographic conditions, the title method was proposed to determine 8 phenolic pollutants in wastewater, including phenol, o-chlorophenol, o-cresol, p-cresol, 2,5-dimethylphenol, 3,5-dimethylphenol, 2,4-dimethylphenol, and quinoline. After settling and filtering the wastewater sample, 20 mL of the sample was taken. Then 4.0 g of sodium chloride was added, and the mixture was shaken for 2 min. After 20 mL of dichloromethanen was added, ultrasonic emulsification extraction was performed for 5 min. The mixed solution was placed into a separating funnel to settle for 5 min. The organic phase was taken, and concentrated to 2-3 mL at 10 ℃. The concentrated solution was diluted to 5 mL by dichloromethane, and 1 g of anhydrous sodium sulfate was added. The mixture was settled for 10 h to remove the moisture, and the resulting solution was introduced into the gas chromatograph-mass spectrometer. Program temperature separation of 8 phenolic pollutants in the sample solution was conducted on the Agilent DB-VRX chromatographic column (30 mm×0.25 mm, 1.4 μm). Qualitative and quantitative analysis was performed by full scan (SCAN) and selective ion monitoring (SIM) modes, respectively. It was shown that linear relationships between values of the mass concentration and peak area of 8 phenolic pollutants were kept in the range of 0.50-500.00 μg·L−1, with detection limits (3S/N) in the range of 0.02-0.07 μg·L−1. Test for recovery was made according to the standard addition method, giving recoveries in the range of 76.8%-114%, and RSDs (n=6) of the determined values not more than 10%. The proposed method was used for the analysis of surface water and coal chemical wastewater samples, 2.40 μg·L−1 phenol and 1.3 μg·L−1p-cresol were detected in surface water, and 8 phenolic pollutants were detected in coal chemical wastewater with detection amounts in the range of 1.21-30.63 μg·L−1.

       

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