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Inverse geochemical modeling of groundwater evolution with emphasis on arsenic in the Mississippi River Valley alluvial aquifer, Arkansas (USA)

机译:美国阿肯色州密西西比河河谷冲积含水层中地下水的逆地球化学建模,重点是砷。

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Inverse geochemical modeling (PHREEQC) was used to identify the evolution of groundwater with emphasis on arsenic (As) release under reducing conditions in the shallow (25-30 m) Mississippi River Valley Alluvial aquifer, Arkansas, USA. The modeling was based on flow paths defined by high-precision (+/- 2 cm) water level contour map; X-ray diffraction (XRD), scanning electron microscopic (SEM), and chemical analysis of boring-sediments for minerals; and detailed chemical analysis of groundwater along the flow paths. Potential phases were constrained using general, trends in chemical analyses data of groundwater and sediments, and saturation indices data (MINTEQA2) of minerals in groundwater. Modeling results show that calcite, halite, fluorite, Fe oxyhydroxide, organic matter, H2S (gas) were dissolving with mote transfers of 1.40E - 03, 2.13E - 04, 4.15E - 06, 1.25E + 01, 3.11, and 9.34, respectively along the dominant flow line. Along the same flow line, FeS, siderite, and vivianite were precipitating with mote transfers of 9.34, 3.11, and 2.64E - 07, respectively. Cation exchange reactions of Ca2+ (4.93E - 04 mol) for Na+ (2.51 E - 04 mol) on exchange sites occurred along the dominant flow line. Gypsum dissolution reactions were dominant over calcite dissolution in some of the flow lines due to the common ion effect. The concentration of As in groundwater ranged from < 0. 5 to 77 mu g/L. Twenty percent total As was complexed with Fe and Mn oxyhydroxides. The redox environment, chemical data of sediments and groundwater, and the results of inverse geochemical modeling indicate that reductive dissolution of Fe oxyhydroxide is the dominant process of As release in the groundwater. The relative rate of reduction of Fe oxyhydroxide over SO42- with co-precipitation of As into sulfide is the limiting factor controlling dissolved As in groundwater. (c) 2007 Elsevier B.V. All rights reserved.
机译:使用逆地球化学模型(PHREEQC)来确定地下水的演化,重点是在美国阿肯色州密西西比河谷冲积含水层浅层(25-30 m)还原条件下砷(As)的释放。建模基于高精度(+/- 2 cm)水位等高线图定义的流路; X射线衍射(XRD),扫描电子显微镜(SEM)和钻孔沉积物的化学分析;以及沿流动路径对地下水进行详细的化学分析。使用地下水和沉积物的化学分析数据的一般性,趋势以及地下水中矿物质的饱和度指数数据(MINTEQA2)来限制位相。建模结果表明,方解石溶解为方解石,石盐,萤石,羟基氧化铁,有机物,H2S(气体),其粉尘转移量为1.40E-03、2.13E-04、4.15E-06、1.25E + 01、3.11和9.34 ,分别沿主导流线。沿着相同的流线,FeS,菱铁矿和堇青石沉淀的微粒转移分别为9.34、3.11和2.64E-07。 Ca2 +(4.93E-04 mol)与Na +(2.51 E-04 mol)的阳离子交换反应在交换位点发生。由于常见的离子效应,在某些流线中,石膏的溶解反应比方解石的溶解更为重要。地下水中As的浓度范围从<0.5到77μg / L。总20%的As与Fe和Mn羟基氧化物络合。氧化还原环境,沉积物和地下水的化学数据以及反地球化学模型的结果表明,羟基氧化铁的还原溶解是地下水中砷释放的主要过程。 Fe氢氧化物在SO42-上还原以及As共沉淀成硫化物的相对速率是控制地下水中溶解As的限制因素。 (c)2007 Elsevier B.V.保留所有权利。

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