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Hydrogeochemical evolution of arsenic along groundwater flow paths: Linking aqueous and solid phase arsenic speciation.

机译:沿地下水流动路径的砷的水文地球化学演化:连接水相和固相砷形态。

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The central hypothesis of this Doctoral research work is that changes occurring along groundwater flow paths that accompany chemical weathering and oxidation-reduction reactions catalyze both arsenic (As) mobilization from, and capture by, minerals via adsorption/desorption and/or mineral dissolution/precipitation reactions. This central hypothesis is addressed by (i) quantifying concentrations and speciation of As, and ancillary geochemical parameters, including a number of redox sensitive parameters in groundwater samples collected along flow paths, and (ii) determining solid phase speciation of As in aquifer sediment samples, with specific emphasis on the labile (i.e., surface exchangeable) and non-labile As fractions (e.g., precipitated with Fe oxides). In order to accomplish these objectives, a series of groundwater samples were collected along flow paths in three well characterized, drinking water aquifers: Carrizo Sand (Texas), Upper Floridan (Florida), and Aquia (Maryland). Results of the groundwater studies demonstrate that the Carrizo and the Upper Floridan aquifers exhibit low dissolved As concentrations (1.4 ppb or ∼19 nmol kg -1), whereas the Aquia aquifer has As concentrations in many wells that exceed the current US Environmental Protection Agency's maximum contaminant level for As in drinking waters of 10 ppb (133 nmol kg-1). The results further indicate that the type of As [As(III) vs. As(V)] released in solution is largely dependent on respiratory microbial consortia present within the aquifer [i.e., Fe(III) reducing bacteria, dissimilatory As(V) reducing prokaryotes (DARPs), and Fe(III) reducing DARPs]. In the final aspect of the project, to address the source and lability of As in sediment, samples were collected from within the Aquia and Carrizo Sand aquifers. These sediment samples were examined petrographically and by X-Ray diffraction, and subsequently subjected to a sequential extraction scheme. By combining the results of Aquia groundwater and sediment studies, it was established that dissilimilatory Fe(III) reduction driven by suboxic, non-sulfidogenic Aquia groundwaters release a significant amount of As from the non-labile fraction of As, which is associated with amorphous and/or well crystallized Fe(III) oxide/oxyhydroxides that form coatings on aquifer mineral surfaces. Results of sequential extraction for the Carrizo Sand aquifer are presented in the Appendix for future consideration.
机译:该博士研究工作的主要假设是,沿着地下水流路发生的变化伴随化学风化和氧化还原反应,通过吸附/解吸和/或矿物溶解/沉淀来催化砷从矿物质中迁移出来并被其捕获。反应。通过(i)量化As的浓度和形态以及辅助地球化学参数(包括沿流动路径收集的地下水样品中的许多氧化还原敏感参数),以及(ii)确定含水层沉积物样品中As的固相形态,解决了这一中心假设。 ,特别强调不稳定的(即表面可交换的)和不稳定的As组分(例如,用Fe氧化物沉淀)。为了实现这些目标,在三个特征明确的饮用水含水层中沿流动路径收集了一系列地下水样品:Carrizo Sand(Texas),Upper Floridan(Florida)和Aquia(Maryland)。地下水研究结果表明,卡里索(Carrizo)和上佛罗里达州含水层的溶解态As浓度较低(<1.4 ppb或〜19 nmol kg -1),而许多井中含水层的As浓度均超过了美国环境保护局的标准。饮用水中As的最大污染物水平为10 ppb(133 nmol kg-1)。结果进一步表明,溶液中释放的As [As(III)vs.As(V)]的类型很大程度上取决于含水层中存在的呼吸微生物菌群[即Fe(III)还原菌,异化As(V)]。还原原核生物(DARPs)和铁(III)还原DARPs]。在该项目的最后一个方面,为了解决沉积物中砷的来源和不稳定性,从阿奎亚和卡里佐砂含水层内部收集了样品。对这些沉积物样品进行了岩相学检查和X射线衍射检查,然后进行了顺序提取方案。通过结合Aquia地下水和沉积物研究的结果,可以确定由亚氧的,非硫化性的Aquia地下水驱动的可解离的Fe(III)还原会从As的非不稳定部分中释放出大量的As,这与非晶态有关。和/或结晶良好的Fe(III)氧化物/羟基氧化物,可在含水层矿物表面上形成涂层。附录中列出了Carrizo砂含水层的顺序提取结果,以供将来考虑。

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