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气相色谱-质谱法分段测定土壤中的可提取总石油烃
引用本文:杨慧娟,刘五星,骆永明,黄玉娟,孙剑英,徐旭士. 气相色谱-质谱法分段测定土壤中的可提取总石油烃[J]. 土壤, 2014, 46(1): 134-138
作者姓名:杨慧娟  刘五星  骆永明  黄玉娟  孙剑英  徐旭士
作者单位:南京师范大学生命科学学院,江苏省生物多样性与生物技术重点实验室,江苏省微生物资源产业化工程技术研究中心
基金项目:国家自然科学基金项目(41001182)、江苏省自然科学基金项目(BK2012891)和环境保护公益性行业科研专项基金项目(201009015)资助
摘    要:
本文建立了用气相色谱-质谱法分段分析土壤中可提取总石油烃的检测方法,并对该方法进行了质量控制研究。土壤中的总石油烃的检测范围是C8(C7.6)~C34(C34.01)。用索氏提取,柱层析分离方法进行前处理,用C8(C7.6),C10(C10.1),C12(C11.7),C16(C15.5),C21(C20.8),C34(C34.01)标准品分别作为C8~C10(C7.6~C10.1),C10~C12(C10.1~C11.7),C12~C16(C11.7~C15.5),C16~C21(C15.5~C20.8),C21~C34(C20.8~C34.01)每段馏分的"替代物"定量,将C8~C34之间所有波峰面积分段积分,以"替代物"的线性关系计算每段馏分的浓度。该方法的质控结果:脂肪烃:相关系数为0.990 3~0.999 8;最低检出限为0.011~0.373 ng/μl;回收率为50.3%~109.3%;相对标准偏差为1.5%~11.3%;芳香烃:相关系数为0.991 3~0.997 6;最低检出限为0.004~0.047 ng/μl;回收率为53.6%~107.7%;相对标准偏差为3.2%~12.2%。本方法检测结果能准确反映土壤的污染程度并有助于生物毒性计算。

关 键 词:GC-MS;石油污染土壤;可提取总石油烃;分段积分

The Sectional Determination of Extractable Total Petroleum Hydrocarbons in Soil by Gas Chromatography-Mass Spectrometry
YANG Hui-juan,LIU Wu-xing,LUO Yong-ming,HUANG Yu-juan,SUN Jian-ying,XU Xu-shi. The Sectional Determination of Extractable Total Petroleum Hydrocarbons in Soil by Gas Chromatography-Mass Spectrometry[J]. Soils, 2014, 46(1): 134-138
Authors:YANG Hui-juan  LIU Wu-xing  LUO Yong-ming  HUANG Yu-juan  SUN Jian-ying  XU Xu-shi
Affiliation:Jiangsu Engineering and Technology Research Center for Industrialization of Microbial Resources, Jiangsu Key Laboratory for Biodiversity and Biotechnology, College of Life Science, Nanjing Normal University
Abstract:
A testing method by using gas chromatograph-mass spectrometry has been established, which might be employed to carry out simultaneous analyses of total petroleum hydrocarbons. In addition, quality assurance and quality control (QA/QC) of the analysis method have also been performed. The range of petroleum hydrocarbons determined in the soil by this method covers the range from C8 (C7.6) to C34 (C34.01) for aliphatics (aromatics). Soxhlet extraction and column chromat-ography separation had been taken as the pretreatment. C8 (C7.6), C10 (C10.1), C12 (C11.7), C16 (C15.5), C21 (C20.8) and C34 (C34.01) substitute C8–C10 (C7.6–C10.1), >C10–C12 (>C10.1–C11.7), >C12–C16 (>C11.7–C15.5), >C16–C21 (>C15.5– C20.8) and >C21–C34 (>C20.8–C34.01) , respectively for quantitative determination. Using the“substitute”linear relationship calculate each segment fractions’ concentration,then integrate all the peak areas from C8 to C34. The results of linear relationship and precision test of aliphatic petroleum hydrocarbon in this method demonstrate the correlation coefficient (0.990 3 to 0.999 8), the method detection limits (MDLs) (0.011 to 0.373 ng/μl), recovery rates (50.3% to 109.3%) and relative standard deviation (1.5% to 11.3%); and those of aromatic petroleum hydrocarbon in this method are the correlation coefficient (0.991 3 to 0.997 6), the method detection limits (MDLs) (0.004 to 0.048 ng/μl), recovery rates (53.6% to 107.7%) and relative standard deviation (3.2% to 12.2%). The test results of the method could accurately reflect the degree of soil contamination and toxicity.
Keywords:GC-MS   Petroleum contaminated soil   Extractable total petroleum hydrocarbons   Section integral
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