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Peak Chromium Pollution in Summer and Winter Caused by High Mobility of Chromium in Sediment of a Eutrophic Lake: In Situ Evidence from High Spatiotemporal Sampling

  • Xianfang Fan
    Xianfang Fan
    State Key Laboratory of Lake Science and Environment, Nanjing Institute of Geography and Limnology, Chinese Academy of Sciences, Nanjing 210008, P. R. China
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  • , 
  • Shiming Ding*
    Shiming Ding
    State Key Laboratory of Lake Science and Environment, Nanjing Institute of Geography and Limnology, Chinese Academy of Sciences, Nanjing 210008, P. R. China
    *Phone: +86-25-86882207; fax: +86-25-86882207; e-mail: [email protected]
    More by Shiming Ding
    Orcidhttp://orcid.org/0000-0001-5317-1899
  • , 
  • Musong Chen
    Musong Chen
    State Key Laboratory of Lake Science and Environment, Nanjing Institute of Geography and Limnology, Chinese Academy of Sciences, Nanjing 210008, P. R. China
    More by Musong Chen
  • , 
  • Shuaishuai Gao
    Shuaishuai Gao
    State Key Laboratory of Lake Science and Environment, Nanjing Institute of Geography and Limnology, Chinese Academy of Sciences, Nanjing 210008, P. R. China
    University of Chinese Academy of Sciences, Beijing 100049, P. R. China
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  • , 
  • Zhen Fu
    Zhen Fu
    State Key Laboratory of Lake Science and Environment, Nanjing Institute of Geography and Limnology, Chinese Academy of Sciences, Nanjing 210008, P. R. China
    University of Chinese Academy of Sciences, Beijing 100049, P. R. China
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  • , 
  • Mengdan Gong
    Mengdan Gong
    State Key Laboratory of Lake Science and Environment, Nanjing Institute of Geography and Limnology, Chinese Academy of Sciences, Nanjing 210008, P. R. China
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  • , 
  • Daniel C. W. Tsang
    Daniel C. W. Tsang
    Department of Civil and Environmental Engineering, The Hong Kong Polytechnic University, Hung Hom, Kowloon, Hong Kong, P. R. China
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    Orcidhttp://orcid.org/0000-0002-6850-733X
  • , 
  • Yan Wang
    Yan Wang
    State Key Laboratory of Lake Science and Environment, Nanjing Institute of Geography and Limnology, Chinese Academy of Sciences, Nanjing 210008, P. R. China
    Nanjing Easysensor Environmental Technology Company, Limited, Nanjing 210018, P. R. China
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  • , and 
  • Chaosheng Zhang
    Chaosheng Zhang
    International Network for Environment and Health, School of Geography and Archaeology, National University of Ireland, Galway H91 CF50, Ireland
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Cite this: Environ. Sci. Technol. 2019, 53, 9, 4755–4764
Publication Date (Web):March 28, 2019
https://doi.org/10.1021/acs.est.8b07060
Copyright © 2019 American Chemical Society
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    Abstract

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    To study the mechanisms of chromium (Cr) mobilization in sediments of eutrophic lakes, monthly sampling was performed in the Meiliang Bay of Lake Taihu, China, combined with laboratory experiments. High-resolution dialysis and diffusive gradients in thin film (DGT) sampling techniques were used. Results indicated that in July 2016 and January 2017, the concentrations of soluble Cr and DGT-labile Cr(VI) in the overlying water exceeded both drinking and fishery water quality standards, resulting from the high mobility of Cr in sediments. In July (summer), the high concentration of soluble Cr (134.04 ± 7.20 μg/L) detected in the anaerobic sediments was primarily caused by the complexation of Cr(III) with dissolved organic matter (DOM). This mechanism was supported by an observed simultaneous increase of soluble Cr and DOM under simulated anaerobic conditions. In January (winter), the high concentrations of soluble Cr (97.55 ± 9.65 μg/L) and DGT-labile Cr(VI) (25.83 ± 1.25 μg/L) in aerobic sediments were primarily caused by reoxidation of Cr(III) by Mn(III/IV) oxides as evidenced by the lowest concentrations of soluble and DGT-labile Mn(II). This study sheds light on the full-year variation and mechanisms of Cr mobilization in eutrophic lake sediments and suggests the urgent need for remediation of Cr pollution especially for winter.

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    The Supporting Information is available free of charge on the ACS Publications website at DOI: 10.1021/acs.est.8b07060.

    • Tables showing water and sediment characteristics of the sampling site, input parameters used for Cr speciation calculation, average values of Cr concentrations and correlation analysis under control, aerobic, and anaerobic treatments; Figures showing vertical distributions of soluble Cr and DGT-labile Cr(VI), total Cr concentrations and fraction concentrations in sampling site, variation of water and sediment parameters in aerobic–anaerobic incubation experiment, hourly changes in soluble Cr concentrations in algae addition experiment, and schematic illustration of Cr mobility in a sediment–water system (DOCX)

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