欢迎登录材料期刊网

材料期刊网

高级检索

以石英超细纤维滤膜采集上海市长宁区的大气颗粒物(PM2.5)样品,采用球磨机将滤膜研磨成细微颗粒,并以0.7% Triton X-100作为分散剂,制备了稳定均一悬浮液,建立了一种简便、绿色、快速的悬浮液进样-石墨炉原子吸收法测定PM2.5中铅和镉的方法。铅在0.1~75μg/L范围内,镉在0.2~3μg/L范围内,校正曲线的线性相关性大于0.998;铅和镉的检出限分别为0.36和0.06μg/L,相对标准偏差小于5%。采用HF-HNO3体系酸消解样品,并与电感耦合等离子体质谱法和石墨炉原子吸收光谱法测试结果对比,验证了方法的准确性。采用本方法对2014年11月~2015年5月期间上海市区大气中PM2.5及铅和镉的污染特性进行分析,结果表明,铅和镉的质量浓度随时间变化趋势与PM2.5的质量浓度随时间的变化趋势呈现良好的一致性。

A green, simple and convenient method for determination of cadmium and lead in PM2.5 by slurry sampling graphite furnace atomic absorption spectrometry was established. PM2.5 samples were collected from Changning district in Shanghai using quartz microfiber filters membranes and grinded into μm-size fine particles by grinding mill for 4 min. The 0.7% Triton X-100 was used as dispersing agent and the pH value was adjusted to 2 by 1% HNO3. The detection limit of cadmium and lead was 0.36 and 0.06 μg/L, respectively, and the linear correlation coefficient of the calibration curves of cadmium in the range of 0.2-3 μg/L and lead in the range of 0.1-75 μg/L was better than 0.998, with a relative standard deviation being not more than 5.0%. The accuracy of the proposed method was verified by comparing the determination result with that by graphite furnace atomic absorption spectrometry and inductively coupled plasma mass spectrometry using solution of acid digestion. The pollution characteristics of cadmium and lead in PM2.5 were analyzed and the result showed that the trend of the mass concentration of PM2.5 with time was consistent with the trends of cadmium and lead.

参考文献

[1] QIN Yu, ZHAO Chun-Sheng. Atmospheric Chemistry. Beijing:China Meteorological Press, 2003:98-142
秦 瑜, 赵春生.大气化学,北京:气象出版社,2003:98-142
[2] LV Yong-Da, HUO Zhong-Hou. Special Environmental Physiology, Beijing:Military Medical Science Press, 2003:251-252
吕永达, 霍仲厚.特殊环境生理学,北京:军事医学科学出版社, 2003:251-252
[3] Watson J G. J. Air Waste Manage. Assoc., 2002,52(6):628-713
[4] Chow J C, Bachmann J D,Wierman S S G, Mathai C, Malm W C, White W H, Mueller P K, Kumar N, Watson J G. J. Air Waste Manage. Assoc., 2002,52(9):973-999
[5] Dockery D W, Pope C A,Xu X P, Spengler J D, Ware J H, Fay M E, Ferris B G, Speizer F E. New Engl. J. Med., 1993,329(24):1753-1759
[6] Pope C A,Thun M J, Namboodiri M M, Dockery D W, Evans J S, Speizer F E, Heath C W. Am. J. Respir. Crit. Care Med., 1995,151(3):669-674
[7] Pope C A, Dockery D W. J. Air Waste Manage. Assoc., 2006,56(6):709-742
[8] Franklin M,Koutrakis P, Schwartz P. Epidemiology, 2008,19(5):680-689
[9] WANG Yu-Jie, TU Zhen-Quan, ZHOU Li, CHI Yong-Jie, LUO Qin. Spectroscopy and Spectral Analysis, 2015,35(4):1030-1032
汪玉洁, 涂振权, 周理, 迟永杰, 罗勤.光谱学与光谱分析,2015,35(4):1030-1032
[10] USEPA (United States Environmental Protection Agency). The Clean Air Act Amendments of [1990] List of Hazardous Air Pollutants[EB/OL].http://www.Epa.gov/ttnatw01/orig189.Html,2010
[11] ATSDR (Agency for Toxic Substances and Disease Registry). Toxicological Profile Information Sheet[EB/OL]. http://www.atsdr.cdc.gov/toxprofiles,2003
[12] Chen L W A, Lowenthal D H, Watson J G, Koracin D, Kumar N, Knipping E M, Wheeler N, Craig K, Reid S. J. Air Waste Manage. Assoc., 2010,60(1):43-54
[13] 甘 亭, 李梅, 黄正旭, 陈多宏, 高伟, 李磊, 卢江林, 蒋斌, 毕新慧, 周振.分析化学,2015,43(12):1934-1941
GAN Ting, LI Mei, HUANG Zheng-Xu, CHEN Duo-Hong, GAO Wei, LI Lei, LU Jiang-Lin, JIANG Bin, BI Xin-Hui, ZHOU Zhen. Chinese J. Anal. Chem., 2015,43(12):1934-1941
[14] LU Gui-Ping, WANG Zheng, QIU De-Ren, ZOU Hui-Jun, HE Yan-Feng. Spectrosc. Spect. Anal., 2011,31(1):244-248
卢桂萍, 汪正, 邱德仁, 邹慧君, 贺岩峰.光谱学与光谱分析,2011,31(1):244-248
[15] SONG Xiao-Lan, WU Xue-Lan, QU Peng, WANG Hai-Bo, QIU Guan-Zhou. Cement and Concrete Comprise, 2005,01:3-7
宋晓岚, 吴雪兰, 曲鹏, 王海波, 邱冠周.硅酸盐学报,2005,01:3-7
上一张 下一张
上一张 下一张
计量
  • 下载量()
  • 访问量()
文章评分
  • 您的评分:
  • 1
    0%
  • 2
    0%
  • 3
    0%
  • 4
    0%
  • 5
    0%