Abstracts of Annual Meeting of the Geochemical Society of Japan
55th Annual Meeting of the Geochemical Society of Japan
Displaying 1-50 of 421 articles from this issue
  • Katsumi Marumo, Mitsuru Yamamura, Yuka Onoki
    Session ID: 1B10 27-10
    Published: 2008
    Released on J-STAGE: September 06, 2008
    CONFERENCE PROCEEDINGS FREE ACCESS
  • Ashraf Ali Seddique, Harue Masuda, Muneki Mitamura, Keiji Shinoda, Tos ...
    Session ID: 1B11 27-11
    Published: 2008
    Released on J-STAGE: September 06, 2008
    CONFERENCE PROCEEDINGS FREE ACCESS
    To gain a better insight into the influence of redox condition in subsurface shallow sediments that intervene in the formation mechanism of arsenic-contaminated groundwater, detailed geochemistry and mineralogy were studied on modern shallow sediments (up to 5 m thick) including the depth where groundwater table and the associated redox condition change in the dry (December, 2005) and rainy (September, 2006) seasons from the areas at different geological setting and grade of groundwater As contamination in Sonargaon, Bangladesh. Stratigraphic sequences of the studied sediment show three distinct lithofacies, viz. clayey-silt, silty-clay and silty-very fine sand layers, corresponding to fine-grained overbank associations. Total As concentration of the studied sediments ranges from <1 to 16 mg/kg. The comparison of the results of two filed profiles show that slightly increased levels of As are found in the rainy season collected sediments. Sequentially chemical extraction analysis of As reveals that >80 % of As are fixed in insoluble and secondary organic phases, while As in reducible and acid soluble phases is very low (<20%) and changes with respect to the grain size, presence of authigenically formed Fe patches and inversely with the mica content. Total As content varies in accordance with the contents of mica, Al2O3 and Fe2O3, but not that of total organic carbon, indicating that biotite is the major host phase of As. This study is further evident that pyrite and/or other sulfide minerals are not a carrier of As in the study area. In contrast, once As is liberated from biotite due to chemical weathering either from near surface sediments where seasonal cycles the redox conditions or within the aquifer sediments by irregular distribution of local redox conditions in complex subsurface environments, would be partitioning into secondarily formed Fe oxyhydroxides/oxides those are likely to work as a chemical pumps to transport the As in the deeper part of the sediment column in association with vertical infiltration of the groundwater.
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