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加速溶剂萃取-硅胶柱净化-碱性氧化铝柱分离-气相色谱三重四极杆质谱法测定土壤中的二噁英类化合物
引用本文:邬静,胡吉成,马玉龙,王世杰,王英,金军. 加速溶剂萃取-硅胶柱净化-碱性氧化铝柱分离-气相色谱三重四极杆质谱法测定土壤中的二噁英类化合物[J]. 分析化学, 2017, 45(6). DOI: 10.11895/j.issn.0253-3820.170017
作者姓名:邬静  胡吉成  马玉龙  王世杰  王英  金军
作者单位:1. 中央民族大学生命与环境科学学院,北京,100081;2. 中央民族大学生命与环境科学学院, 北京 100081;北京市食品环境与健康工程中心, 北京 100081
基金项目:国家自然科学基金,中央高校基本科研业务费专项资金,高等学校学科创新引智计划,国家大学生创新训练计划(No.GCCX2016110042)资助项目.This work was supported by the National Natural Science Foundation of China,the Fundamental Research Funds for the Central Universities,the Institution of Higher Education Innovation Talent Recruitment Program,the National College Students' Innovative Training Program
摘    要:建立了加速溶剂萃取(ASE),酸性硅胶柱、复合硅胶柱及碱性氧化铝柱纯化分离,气相色谱-三重四极杆质谱测定土壤中二噁英/呋喃(PCDD/Fs)、多氯联苯(PCBs)、多氯萘(PCNs)的分析方法.选用正己烷-二氯甲烷(50∶50, V/V)作为ASE的提取溶剂,设定提取温度为120℃,加标回收实验表明本方法可行.用100 mL正己烷-二氯甲烷(95∶5, V/V)及50 mL正己烷-二氯甲烷(50∶50, V/V)依次淋洗碱性氧化铝柱,得到组分A(PCBs及PCNs)与组分B(PCDD/Fs),实现了PCDD/Fs与另外两种化合物的分离,排除了同系物间及其它杂质的干扰.使用同位素稀释-气相色谱三重四极杆质谱法(GC-MS/MS), 在选择反应监测(Selected reaction monitoring, SRM)模式下测定PCDD/Fs、PCBs和PCNs,3种化合物的仪器检出限(LOD)范围分别为0.04~0.25 μg/L, 0.10~0.20 μg/L和0.01~0.05 μg/L,目标物平均相对响应因子(RRF)的相对标准偏差(RSD)均小于13%.基质土加标实验中,3种化合物13C标记的同位素内标回收率的范围分别为50%~95%,51%~103%, 49%~74%.实际样品的分析结果表明,PCDD/Fs、PCBs及PCNs在土壤样品中的总含量范围分别为16.1~1148 pg/g、6.6~152.6 pg/g及10.9~99.5 pg/g,且样品测定结果与高分辨质谱测定结果相吻合.

关 键 词:二噁英/呋喃  多氯联苯  多氯萘  前处理方法  三重四极杆质谱

Determination of Dioxin-like Compounds in Soil byAccelerated Solvent Extraction-Silica Gel Column Cleanup-BasicAlumina Column Separation Coupled with Gas Chromatography-Triple Quadrupole Mass Spectrometry
WU Jing,HU Ji-Cheng,MA Yu-Long,WANG Shi-Jie,WANG Ying,JIN Jun. Determination of Dioxin-like Compounds in Soil byAccelerated Solvent Extraction-Silica Gel Column Cleanup-BasicAlumina Column Separation Coupled with Gas Chromatography-Triple Quadrupole Mass Spectrometry[J]. Chinese Journal of Analytical Chemistry, 2017, 45(6). DOI: 10.11895/j.issn.0253-3820.170017
Authors:WU Jing  HU Ji-Cheng  MA Yu-Long  WANG Shi-Jie  WANG Ying  JIN Jun
Abstract:A method for determination of PCDD/Fs, PCBs and PCNs in soil sample was developed by using accelerated solvent extraction (ASE)-silica gel column cleanup-basic alumina column separation coupled with GC-MS/MS.The sample was extracted by ASE with Hexane-methylene chloride (Hex-DCM, 50∶50, V/V) at 120℃.The basic alumina column was used to separate PCDD/Fs, PCBs and PCNs.The extracts were eluted with Hex-DCM (95∶5, V/V) to obtain PCBs and PCNs, followed by Hex-DCM (50∶50, V/V) to obtain PCDD/Fs.The limits of detection (LOD) were in the range of 0.04-0.25 μg/L, 0.10-0.20 μg/L and 0.01-0.05 μg/L for PCDD/Fs, PCBs, PCNs, respectively.The relative standard deviations (RSDs) of average relative response factors (RRF) were below 13%.The recoveries of 13C-labeled internal standards of the three classes of analytes were 50%-95%, 51%-103% and 49%-74%, respectively.Concentrations of ∑PCDD/Fs, ∑PCBs and ∑PCNs in soil samples were 16.1-1148 pg/g, 6.6-152.6 pg/g and 10.9-99.5 pg/g, respectively.The results were consistent with that of high resolution mass spectrometer.
Keywords:Polychlorinated dibenzo-p-dioxins and furans  Polychlorinated biphenyls  Polychlorinated naphthalenes  Pretreatment methods  Triple quadrupole mass spectrometry
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