Japan Geoscience Union Meeting 2014

Presentation information

Poster

Symbol A (Atmospheric, Ocean, and Environmental Sciences) » A-HW Hydrology & Water Environment

[A-HW25_2PO1] Isotope Hydrology 2014

Fri. May 2, 2014 4:15 PM - 5:30 PM Poster (3F)

Convener:*Yasuhara Masaya(Geological Survey of Japan, AIST), Kohei Kazahaya(Geological Survey of Japan, AIST), Shinji Ohsawa Shinji(Institute for Geothermal Sciences, Graduate School of Science, Kyoto University), Masaaki Takahashi(Geological Survey of Japan (GSJ), National Institute of Advanced Industrial Science and Technology (AIST)), YUICHI SUZUKI(Faculty of Geo-Environmental Sience,Rissho University), Futaba Kazama(Social Cystem Engineering, Division of Engineering, Interdiciplinary Graduate School of Medical and Engineering, University of Yamanashi), Kazuyoshi Asai(Geo Science Laboratory)

4:15 PM - 5:30 PM

[AHW25-P01] GC/C/IRMS as a tool to evaluate the degradation of chlorinated organic compounds in groundwater

*Yuki YONEYAMA1, Yohei ARAI2, Takashi NAKAMURA1, Futaba KAZAMA1 (1.ICRE, UNIVERSITY OF YAMANASHI, 2.Hitachi Plant Services Co.,Ltd)

Keywords:GC/C/IRMS, chlorinated organic compounds, biodegradation

The in-situ remediation techniques by microbial activity are used for reduction of chlorinated organic compounds in polluted groundwater. However, the evaluation of microbial activity for decomposition of chlorinated organic compounds is not clear by only the concentration analysis. So, we focus on the usage of the stable carbon isotope analysis of chlorinated organic compounds such as trichloroethylene (TCE), and its daughter products; cis-dichloroethylene (cis-DCE) and vinyl chloride (VC). The stable carbon isotope ratio (δ13C) of these organic compounds were analyzed by a GC (Agilent : 7890A) coupled to an isotope ratio mass spectrometer(SerCon : 20-22) with combustion interface (SerCon : GC-CP) (GC/C/IRMS). The system was equipped with a purge-and-trap concentrator (GL science : AQUA PT 5000J PLUS) connected to the GC. In the δ13C value measurement, the measurement limit was usually 200ng-C, and standard deviation in TCE, cis-DCE and VC were ±0.08, ±0.37, ±0.11 permil, respectively. Groundwater samples were collected at polluted site with and without bioremediation treatment. In samples from without treatment site, even the concentration decreasing were detected, the δ13C values of TCE are almost same as original one. On the other hands, δ13C values of not only TCE but also the daughter products increase with a decrease in concentration of TCE. These results show the usefulness of GC/C/IRMS for distinguishing the reason of concentration reduction by in-situ microbial activity of decomposition of these organic pollutants from physical factors such as dilution, diffusion, and adsorption.