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有机质对地下水砷迁移的影响:来自孟加拉国西北部(查帕伊-纳瓦布甘杰)、中部(曼尼甘杰)和东南部(钱德普尔)的证据。

Implications of organic matter on arsenic mobilization into groundwater: evidence from northwestern (Chapai-Nawabganj), central (Manikganj) and southeastern (Chandpur) Bangladesh.

机构信息

Department of Earth Sciences, National Cheng Kung University, Tainan 70101, Taiwan.

出版信息

Water Res. 2010 Nov;44(19):5556-74. doi: 10.1016/j.watres.2010.09.004. Epub 2010 Sep 15.

Abstract

Boreholes (50 m depth) and piezometers (50 m depth) were drilled and installed for collecting As-rich sediments and groundwater in the Ganges, Brahmaputra, and Meghna flood plains for geochemical analyses. Forty-one groundwater samples were collected from the three areas for the analyses of cations (Ca(2+), Mg(2+), K(+), Na(+)), anions (Cl(-), NO(3)(-), SO(4)(2-)), total organic carbon (TOC), and trace elements (As, Mn, Fe, Sr, Se, Ni, Co, Cu, Mo, Sb, Pb). X-ray powder diffraction (XRD) and X-ray fluorescence (XRF) were performed to characterize the major mineral and chemical contents of aquifer sediments. In all three study areas, results of XRF analysis clearly show that fine-grained sediments contain higher amounts of trace element because of their high surface area for adsorption. Relative fluorescent intensity of humic substances in groundwater samples ranges from 30 to 102 (mean 58 ± 20, n = 20), 54-195 (mean 105 ± 48, n = 10), and 27-243 (mean 79 ± 71, n = 11) in the Ganges, Brahmaputra and Meghna flood plains, respectively. Arsenic concentration in groundwater (20-50 m of depth) ranges from 3 to 315 μg/L (mean 62.4 ± 93.1 μg/L, n = 20), 16.4-73.7 μg/L (mean 28.5 ± 22.4 μg/L, n = 10) and 4.6-215.4 μg/L (mean 30.7 ± 62.1 μg/L, n = 11) in the Ganges, Brahmaputra and Meghna flood plains, respectively. Specific ultra violet adsorption (SUVA) values (less than 3 m(-1) mg(-1) L) indicate that the groundwater in the Ganges flood plain has relatively low percentage of aromatic organic carbon compared to those in the Brahmaputra and Meghna flood plains. Arsenic content in sediments ranges from 1 to 11 mg/kg (mean 3.5 ± 2.7 mg/kg, n = 17) in the three flood plains. Total organic carbon content is 0.5-3.7 g/kg (mean 1.9 ± 1.1 g/kg) in the Ganges flood plain, 0.5-2.1 g/kg (mean: 1.1 ± 0.7 g/kg) in the Brahmaputra flood plain and 0.3-4.4 g/kg (mean 1.9 ± 1.9 g/kg) in the Meghna flood plain. Arsenic is positively correlated with TOC (R(2) = 0.50, 0.87, and 0.85) in sediments from the three areas. Fourier transform infrared (FT-IR) analysis of the sediments revealed that the functional groups of humic substances in three areas include amines, phenol, alkanes, and aromatic carbon. Arsenic and Fe speciation in sediments were determined using XANES and the results imply that As(V) and Fe(III) are the dominant species in most sediments. The results also imply that As (V) and Fe (III) in most of the sediment samples of the three areas are the dominant species. X-ray absorption fine structure (EXAFS) analysis shows that FeOOH is the main carrier of As in the sediments of three areas. In sediments, As is well correlated with Fe and Mn. However, there is no such correlation observed between As and Fe as well as As and Mn in groundwater, implying that mobilizations of Fe, Mn, and As are decoupled or their concentrations in groundwater have been affected by other geochemical processes following reductive dissolution of Fe or Mn-hydroxides. For example, dissolved Fe and Mn levels may be affected by precipitation of Fe- and Mn-carbonate minerals such as siderite, while liberated As remains in groundwater. The groundwaters of the Brahmaputra and Meghna flood plains contain higher humic substances in relative fluorescence intensity (or fluorescence index) and lower redox potential compared to the groundwater of Ganges flood plain. This leads to the release of arsenic and iron to groundwater of these three plains in considerable amounts, but their concentrations are distributed in spatial variations.

摘要

在恒河、布拉马普特拉河和梅克纳河泛滥平原中钻取了 50 米深的钻孔和安装了测压计,用于采集富含砷的沉积物和地下水进行地球化学分析。从这三个地区采集了 41 个地下水样本,用于分析阳离子(Ca(2+)、Mg(2+)、K(+)、Na(+))、阴离子(Cl(-)、NO(3)(-)、SO(4)(2-))、总有机碳(TOC)和微量元素(As、Mn、Fe、Sr、Se、Ni、Co、Cu、Mo、Sb、Pb)。进行了 X 射线粉末衍射(XRD)和 X 射线荧光(XRF)分析,以表征含水层沉积物的主要矿物和化学成分。在所有三个研究区域,XRF 分析的结果清楚地表明,由于细颗粒沉积物具有更高的表面积,因此含有更高量的痕量元素。地下水样品中腐殖质物质的相对荧光强度范围为 30 至 102(平均值 58 ± 20,n = 20)、54-195(平均值 105 ± 48,n = 10)和 27-243(平均值 79 ± 71,n = 11)在恒河、布拉马普特拉河和梅克纳河泛滥平原中。地下水(20-50 米深)中的砷浓度范围为 3 至 315μg/L(平均值 62.4 ± 93.1μg/L,n = 20)、16.4-73.7μg/L(平均值 28.5 ± 22.4μg/L,n = 10)和 4.6-215.4μg/L(平均值 30.7 ± 62.1μg/L,n = 11)在恒河、布拉马普特拉河和梅克纳河泛滥平原中。特定紫外吸收(SUVA)值(小于 3m(-1)mg(-1)L)表明,与布拉马普特拉河和梅克纳河泛滥平原相比,恒河泛滥平原中的地下水的芳香有机碳百分比相对较低。沉积物中的砷含量范围为 1 至 11mg/kg(平均值 3.5 ± 2.7mg/kg,n = 17)在三个泛滥平原中。总有机碳含量为 0.5-3.7g/kg(平均值 1.9 ± 1.1g/kg)在恒河泛滥平原,0.5-2.1g/kg(平均值:1.1 ± 0.7g/kg)在布拉马普特拉河泛滥平原和 0.3-4.4g/kg(平均值 1.9 ± 1.9g/kg)在梅克纳河泛滥平原。砷与 TOC(R(2) = 0.50、0.87 和 0.85)在三个地区的沉积物中呈正相关。对沉积物的傅里叶变换红外(FT-IR)分析表明,三个地区腐殖质物质的官能团包括胺、酚、烷烃和芳香碳。使用 XANES 确定了沉积物中的砷和铁的形态,结果表明,砷(V)和铁(III)是大多数沉积物中的主要物种。结果还表明,在三个地区的大多数沉积物样品中,砷(V)和铁(III)是主要物种。X 射线吸收精细结构(EXAFS)分析表明,FeOOH 是沉积物中砷的主要载体。在沉积物中,砷与铁和锰密切相关。然而,在地下水样品中没有观察到砷与铁以及砷与锰之间的这种相关性,这意味着铁、锰和砷的迁移是解耦的,或者它们在地下水中的浓度受到了还原溶解铁或锰氢氧化物后其他地球化学过程的影响。例如,溶解的铁和锰水平可能受到 Fe 和 Mn 碳酸盐矿物(如菱铁矿)沉淀的影响,而释放的砷则留在地下水中。与恒河泛滥平原的地下水相比,布拉马普特拉河和梅克纳河泛滥平原的地下水的相对荧光强度(或荧光指数)更高,氧化还原电位更低。这导致这些三个平原中的大量砷和铁释放到地下水中,但它们的浓度在空间上分布有所不同。

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