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    地下水系统中砷活化的钼同位素地球化学指示

    李梦娣 周炼 王焰新 吴潇 王帅

    李梦娣, 周炼, 王焰新, 吴潇, 王帅, 2014. 地下水系统中砷活化的钼同位素地球化学指示. 地球科学, 39(1): 99-107. doi: 10.3799/dqkx.2014.010
    引用本文: 李梦娣, 周炼, 王焰新, 吴潇, 王帅, 2014. 地下水系统中砷活化的钼同位素地球化学指示. 地球科学, 39(1): 99-107. doi: 10.3799/dqkx.2014.010
    Li Mengdi, Zhou Lian, Wang Yanxin, Wu Xiao, Wang Shuai, 2014. Molybdenum Isotope Geochemistry of Arsenic Mobilization in Groundwater System. Earth Science, 39(1): 99-107. doi: 10.3799/dqkx.2014.010
    Citation: Li Mengdi, Zhou Lian, Wang Yanxin, Wu Xiao, Wang Shuai, 2014. Molybdenum Isotope Geochemistry of Arsenic Mobilization in Groundwater System. Earth Science, 39(1): 99-107. doi: 10.3799/dqkx.2014.010

    地下水系统中砷活化的钼同位素地球化学指示

    doi: 10.3799/dqkx.2014.010
    基金项目: 

    国家自然科学基金 40830748

    国家自然科学基金 41120124003

    科技部"863"计划课题 2012AA062602

    详细信息
      作者简介:

      李梦娣(1986-), 女, 博士, 主要从事地下水防治与污染及同位素地球化学研究.E-mail: limengdi1028@163.com

      通讯作者:

      王焰新, E-mail: yx.wang@cug.edu.cn

    • 中图分类号: P592

    Molybdenum Isotope Geochemistry of Arsenic Mobilization in Groundwater System

    • 摘要: 砷在天然环境中的迁移富集与氧化还原状态密切相关.盆地环境地下水中砷的活化迁移机制主要为沉积物中铁/锰氢氧化物由氧化还原条件变化导致发生还原性溶解进而释放吸附在其表面的砷.钼及钼同位素为氧化还原环境的重要指示参数, 且铁/锰氢氧化物对钼同位素分馏有着重要的控制作用.将地下水的钼同位素应用于砷的活化迁移规律研究.大同盆地地下水中钼同位素比值(δ98Mo)范围为-0.12‰~+2.17‰, 相比于淡水中钼同位素组成偏重.桑干河河水的δ98Mo为+0.72‰, 与文献报道的河水平均钼同位素比值+0.7‰相当.大同盆地地下水中δ98Mo与硫化物之间存在正相关关系, 表明Mo-Fe-S复合物可能形成于特定条件下, 并优先利用水溶液中轻的钼使地下水中δ98Mo比值升高.砷浓度与钼浓度之间的微弱负相关以及砷浓度与钼同位素之间的正相关说明, Mo-Fe-S的形成过程可能与同环境中As-Fe-S的复合物的形成存在竞争关系, 进而使得地下水中砷富集.地下水中相对偏高的δ98Mo可能来源于铁的氢氧化物对溶液中轻的钼的吸附速率高于先前吸附在铁的氢氧化物的钼的释放, 且铁的氢氧化物对水溶液中钼的再吸附这一循环过程会导致地下水中钼浓度降低及钼同位素比值的升高.钼同位素指示的循环性的铁的氢氧化物的还原溶解及再氧化过程对砷的富集也有重要影响.

       

    • 图  1  研究区地质图及采样点分布(图中实心点为钼同位素分析样品分布)

      Fig.  1.  Geological map of study area and sample locations

      图  2  地下水中钼同位素δ98Mo与溶解硫化物的关系

      Fig.  2.  Relationship between δ98Mo and dissolved S2- in groundwater

      图  3  地下水中钼同位素δ98Mo与Fe2+, Fetotal, Mn的关系

      Fig.  3.  Relationships between δ98Mo and Fe2+, Fetotal, and Mn in groundwater

      图  4  地下水中钼的浓度及钼同位素比值δ98Mo的关系

      Fig.  4.  Mo concentrations versus δ98Mo in groundwater

      图  5  地下水中钼同位素组成δ98Mo与pH值的关系

      Fig.  5.  Relationship between δ98Mo and pH in groundwater

      图  6  地下水中砷与亚铁、总铁、钼及钼同位素的关系

      Fig.  6.  Relationships between As and Fe2+, Fetotal, Mo and δ98Mo in groundwater

      表  1  大同盆地地下水中钼同位素组成及砷、铁、锰和其他物理化学参数

      Table  1.   Mo isotopic composition and Mo, As, Fe, Mn and other physicochemical parameters in groundwater in Datong basin

      样品编号 深度(m) pH Ec(μs/cm) S2-(μg/L) Fe2+(mg/L) Fetotal(mg/L) SO4(mg/L) As(μg/L) Mn(μg/L) Mo(μg/L) δ98Mo(‰)
      1 30 7.80 2 320 0 0.13 0.17 576.0 144.00 162.00 2.60 0.80
      2 90 8.12 484 1 0.12 0.11 50.0 16.00 5.43 1.94 1.25
      3 25 8.18 842 4 0.03 0.06 28.3 368.00 27.00 7.32 0.88
      4 30 7.89 1 870 19 0.10 0.72 237.0 875.00 179.00 2.98 2.14
      5 20 7.82 1 169 1 0.13 0.15 46.4 679.00 62.10 9.75 1.02
      6 18 8.09 1 240 -2 0.08 0.07 170.0 8.19 6.20 39.30 0.73
      7 100 8.58 2 000 22 0.28 1.01 82.1 221.00 23.80 14.30 1.56
      8 7.23 878 42 0.01 0.03 293.0 3.66 2.30 24.50 0.72
      9 6 7.93 1 344 7 0.02 0.00 250.0 14.30 1.30 13.00 1.20
      10 70 7.91 1 865 24 0.07 0.40 111.0 299.00 26.70 2.15 2.17
      11 36 7.98 436 193 0.08 0.05 12.9 381.00 130.00 1.32 1.10
      12 10 7.61 1 295 4 0.10 0.14 145.0 15.10 30.50 3.44 0.60
      13 20 8.06 1 089 12 0.04 0.04 97.2 32.30 21.90 5.58 1.09
      14 70 7.78 580 28 0.03 0.62 49.3 11.10 13.70 4.49 0.89
      15 35 7.86 1 601 -1 0.03 0.04 237.0 3.55 559.00 27.30 -0.12
      16 25 8.13 3 300 12 0.03 0.03 571.0 12.60 3.69 23.50 1.14
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