GC-MS Determination of CS2 in Indoor Air with Separation by Adsorption on Activated Carbon
摘 要
移取2 μL二硫化碳标准储备溶液(二硫化碳的绝对质量小于4 μg)于动态稀释仪中,在选定的最佳条件下(吹扫流量为1 000 mL·min-1,吹扫时间为10 min)操作。仪器的出气口与活性炭吸附管连接,使空气中的二硫化碳被活性炭吸附。吹扫时间结束时,取下吸附管,移置于全自动热脱附仪中,按仪器工作条件操作,使二硫化碳解吸并引入气相色谱仪,在DB-5色谱柱(60 m×0.25 mm,0.25 μm)上按程序升温(温度区间为50~250℃)模式进行分离,按设定条件用质谱法测定二硫化碳的含量。用二硫化碳标准溶液系列绘制标准曲线,其线性范围在0.010~2.0 mg·L-1之间,检出限(3s)为0.007 μg。当采集体积为10 L时,其检出限为0.7 μg·m-3。用标准加入法进行回收试验,测得回收率在105%~110%之间,测定值的相对标准偏差(n=6)均小于4%。为检测吸附管中二硫化碳的稳定保持时间,取2 μL二硫化碳标准储备溶液9份,分别按上述条件吹扫,并吸附于9个吸附管中,在不同的时间测定其二硫化碳的含量。结果表明,吸附管中二硫化碳至少可保存72 h,在室温(23℃)和低温(-18℃)条件下,保存的吸附管中二硫化碳的测定结果之间无明显差异。
Abstract
A dynamic dilution instrument, with its gas outlet connected with an activated carbon adsorption tube, was used for sampling of air and separation of CS2 from air by adsorption on activated carbon. An aliquot of 2 μL of CS2 standard reserve solution (absolute mass of CS2<4 μg) was introduced into the instrument and the air sample was collected under the optimum conditions (i.e., with flow-rate of 1 000 mL·min-1 and time of 10 min in sweeping). At the end of sweeping time, the adsorption tube was dis-connected and transferred to be thermo-desorption device in which the CS2 adsorbed on activated carbon was desorbed under the working condition of the desorption device and transferred to gas chromatograph to be separated on DB-5 chromatographic column (60 m×0.25 mm, 0.25 μm) under the mode of programed temperature elevation in the range between 50℃ to 250℃. Finally, CS2 separated by GC was determined by MS. Standard curve was prepared with standard solution of CS2 and analyzed by the same procedure described above. Linearity range of CS2 was found between 0.010 mg·L-1 to 2.0 mg·L-1 with detection limit (3s) of 0.007 μg or 0.7 μg·m-3 when 10 L of air sample were collected. Recovery was tested by the standard addition method giving value of recovery in the range of 105%-110%. Values of RSD (n=6) were found all less than 4%. To test for time of keeping of the CS2 adsorbed on activated carbon in the adsorption tube, 9 portions of 2 μL of CS2 standard reserve solution were taken and treated in the same way in the dynamic dilution instrument separately and 9 adsorption tubes with adsorbed CS2 were obtained and their contents of CS2 were determined by GC-MS after keeping for different times. It was shown that the concentration of CS2 in the adsorption tubes were kept stable at least for 72 h, and in further, the contents of CS2 determined in adsorption tubes kept under room temperature (23℃) and under low temperature (-18℃) showed no significant difference.
中图分类号 O657.63 DOI 10.11973/lhjy-hx201910008
所属栏目 工作简报
基金项目 “十三五”国家重点研发计划(2016YFC0700606)
收稿日期 2019/2/28
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备注赵文燕,硕士,主要从事化学分析检测研究工作,zhaowenyan@ctc.ac.cn
引用该论文: ZHAO Wenyan,GUO Zhongbao,GUAN Hongyan,DING Jianjun,MEI Yifei,LIU Shihua. GC-MS Determination of CS2 in Indoor Air with Separation by Adsorption on Activated Carbon[J]. Physical Testing and Chemical Analysis part B:Chemical Analysis, 2019, 55(10): 1164~1167
赵文燕,郭中宝,关红艳,丁建军,梅一飞,刘实华. 活性炭吸附分离-气相色谱-质谱法测定室内空气中二硫化碳的含量[J]. 理化检验-化学分册, 2019, 55(10): 1164~1167
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参考文献
【1】陈绍兰.二硫化碳对血管内皮细胞的氧化损伤及细胞周期影响和维生素C的保护作用[D].杭州:浙江大学, 2003.
【2】GB/T 14680-1993空气质量二硫化碳测定二乙胺分光光度法[S].
【3】GB 11741-1989居住区大气中二硫化碳卫生检验标准方法气相色谱法[S].
【4】GBZ 160.33-2004工作场所空气有毒物质测定硫化物[S].
【5】刘喜,施玉格.毛细管柱气相色谱法测定空气中二硫化碳[J].干旱环境监测, 2017,31(2):67-69.
【6】刘向军,葛际江,毛源,等.油溶性清蜡剂中二硫化碳的测定方法[J].油气地质与采收率, 2013,20(2):99-102.
【7】朱蓉,张洪海,杨桂朋.海水和大气中挥发性硫化物分析方法的研究[J].分析化学, 2017,45(10):1504-1510.
【8】韦桂欢,张洪彬,龙庆云,等.苏码罐采样-气相色谱-质谱法测定密闭环境空气中的有害气体[J].理化检验-化学分册, 2016,52(5):532-536.
【9】EPA/625/R-96/010b Compendium method TO-17 determination of volatile organic compounds in ambient air using active sampling onto sorbent tubes[S].
【10】刘孟,张莉,王茜.碳分子筛和活性炭吸附氙气性能的研究[J].湘潭大学自然科学学报, 2015,37(2):27-32.
【11】傅若农.气相色谱中碳固定相的演变[J].化学试剂, 2015,37(1):1-7.
【2】GB/T 14680-1993空气质量二硫化碳测定二乙胺分光光度法[S].
【3】GB 11741-1989居住区大气中二硫化碳卫生检验标准方法气相色谱法[S].
【4】GBZ 160.33-2004工作场所空气有毒物质测定硫化物[S].
【5】刘喜,施玉格.毛细管柱气相色谱法测定空气中二硫化碳[J].干旱环境监测, 2017,31(2):67-69.
【6】刘向军,葛际江,毛源,等.油溶性清蜡剂中二硫化碳的测定方法[J].油气地质与采收率, 2013,20(2):99-102.
【7】朱蓉,张洪海,杨桂朋.海水和大气中挥发性硫化物分析方法的研究[J].分析化学, 2017,45(10):1504-1510.
【8】韦桂欢,张洪彬,龙庆云,等.苏码罐采样-气相色谱-质谱法测定密闭环境空气中的有害气体[J].理化检验-化学分册, 2016,52(5):532-536.
【9】EPA/625/R-96/010b Compendium method TO-17 determination of volatile organic compounds in ambient air using active sampling onto sorbent tubes[S].
【10】刘孟,张莉,王茜.碳分子筛和活性炭吸附氙气性能的研究[J].湘潭大学自然科学学报, 2015,37(2):27-32.
【11】傅若农.气相色谱中碳固定相的演变[J].化学试剂, 2015,37(1):1-7.
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