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超声提取-气相色谱质谱法测定大气PM_(2.5)中正构烷烃

Determination of N-alkanes in Atmospheric Fine Particulate Matter by Gas Chromatography Mass Spectrometry with Ultrasonic Extraction
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摘要 建立了超声提取-气相色谱质谱法测定大气PM2.5中32种正构烷烃方法,经离子温度优化、前处理比较、空白滤膜考察等获得了最佳的实验条件。研究发现,高、中、低3种浓度标准曲线的相关系数均在0.995以上,3种浓度的空白样品加标回收率分别为72.2%~117.8%、73.5%~104.4%、73.8%~109.5%,精密度均小于10%,实际样品加标回收率为75.7%~108.9%。当采样体积为24 m3时,各目标化合物的方法检出限为0.046~2.6 ng/m^3;经正构烷烃浓度范围为0.17~64.3 ng/m^3的1月及浓度范围为0.53~7.67 ng/m^3的6月的实际样品验证,该方法的检出限和测量范围也可较好的满足实际样品的测定。 A method of Gas Chromatography Mass Spectrometry with Ultrasonic Extraction determination of 32 N-alkanes in PM2. 5has been established. In order to acquire the best conditions,various parameters were studied,like as the effect of different ion source temperature,the pretreatment of the method,the selection of blank quartz filter,and investigating the adaptability of this method by detecting the actual samples. Results showed that the correlation coefficient of 32 N-alkanes in PM2. 5detected by Gas Chromatography Mass Spectrometry with Ultrasonic Extraction were all above 0. 995,it has high accuracy and precision. In addition the recovery of 32 N-alkanes of different concentration in blank quartz filters were in the range of 72. 2%-117. 8%,73. 5%-104. 4%,73. 8%-109. 5%,precision is less than 10%,and the recovery of actual sample was in the range of75. 7%-108. 9%. Otherwise,When the sampling volume was 24 m3,the limit detection of 32 N-alkanes was 0. 046-2. 6 ng/m^3.We detected actual samples in in January and June,the concentration of N-alkanes ranged from 0. 53-7. 67 ng / m^3 and 0. 17-64. 3ng / m^3 separately,With this result we can see this method has low detection limit,can completely suitable for determination of N-alkanes in PM_(2. 5).
出处 《中国环境监测》 CAS CSCD 北大核心 2015年第6期109-117,共9页 Environmental Monitoring in China
关键词 超声提取法 气相色谱质谱法 PM2.5 正构烷烃 Ultrasonic Extraction Gas Chromatography Mass Spectrometry PM2.5 N-alkanes
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  • 1胡颖,邵龙义,Schaefer K,王静,Suppan P,王建英.北京市PM2.5对DNA的氧化性损伤规律分析[J].中国环境科学,2013,33(10):1863-1868. 被引量:14
  • 2Hueglin C , Gehrig R,Baltensperger U, et al. Chemicalcharacterisation of PM2 5,PM10 and coarse particles aturban, near-city and rural sites in Switzerland [J].Atmospheric Environment,2005 ,39 : 637-651.
  • 3Cao J,Chow J C , Lee F S C, et al. Evolution of PM2 5Measurements and Standards in the US and futureperspectives for China [ J ]. Aerosol and Air QualityResearch,2013,13:1 197-1 211.
  • 4Sun Y L, Wang Z F, Fu P Q, et al. Aerosolcomposition,sources and processes during wintertimein Beijing, China [J]. Atmospheric Chemistry andPhysics,2013,13:4 577-4 592.
  • 5Dan YANG,Shihua QI,Ningombam Linthoingambi DEVI,Fang TIAN,Ziping HUO,Qingyuan ZHU,Jing WANG.Characterization of polycyclic aromatic hydrocarbons in PM2.s and PMlo in Tanggu District, Tianjin Binhai New Area, China[J].Frontiers of Earth Science,2012,6(3):324-330. 被引量:9
  • 6Sun Z, Mu Y,Liu Y,et al. A comparison study onairborneparticles during haze days and non-haze days inBeijing [ J]. Science of the Total Environment, 2013,456:1-8.
  • 7Cao J, Xu H, Xu Q, et al. Fine particulate matterconstituents and cardiopulmonary mortality in a heavilypolluted Chinese city [ J ]. Environmental healthperspectives,2012,120(3) : 373-378.
  • 8郑永杰,刘佳,田景芝,傅尧.齐齐哈尔市春季大气中PM_(2.5)的污染特征分析[J].中国环境监测,2014,30(4):76-81. 被引量:13
  • 9Chan Y C,Simpson R W, Mctainsh G H, et al.Characterization of chemical species in PM2 5 and PM10aerosols in Brisbane Australia [ J ]. AtmosphericEnvironment, 1997 ,31 :2 061-2 080.
  • 10Chow J C , Watson J G, Lu Z, et al. Descriptive analysisof PM2 5 and PM,0 at regionally representative locationsduring sjvaqs/auspex [ J ]. Atmospheric Environment,1996,30:2 079-2 112.

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