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Assessing and simulating the major pathway and hydrogeochemical transport of arsenic in the Beitou-Guandu area, Taiwan

机译:评估和模拟台湾北投—关渡地区砷的主要途径和水文地球化学迁移

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This study involved assessing and simulating the probable major pathways (surface and subsurface flow) and hydrogeochemical transport of arsenic (As) in the Beitou-Guandu area, Taiwan. A one-dimensional (1-D) generic, reactive, chemical transport model (PHREEQC) was adopted. The calibrated model showed that As transported to the downstream Guandu plain and Tan Shui river mouth accounted for 50.7 and approximately 100 % of the As in the subsurface flow pathway, respectively, suggesting that subsurface flow constituted a major As pathway. The highest As water concentration occurred near the Beitou geothermal valley because of the low pH and high redox potential in both the surface and subsurface pathways. However, As may be scavenged by aqueous Fe(II) in a reducing environment. The As concentrations in the downstream Guandu plain and Guandu wetland decreased as the simulated time increased, resulting in the adsorption of As on the surface of Fe oxydroxides and limiting the mobility of As in the surface flow pathway. The major retardation mechanism of As mobility in the subsurface flow pathway of the Guandu plain and Guandu wetland was governed by the adsorption reactions of iron-oxide and iron-sulfide minerals. The 1-D transport model was applied to predict the evolution of As in the subsurface flow pathway from 2013 to 2020. The results indicated that the As concentrations in all cells gradually increased. The geochemical redox reactions of As in the subsurface pathway subsequently led to the oxidization of As-bearing sulfides, causing As concentrations to rise substantially in the hillside area.
机译:这项研究涉及评估和模拟台湾北投—关渡地区的砷(As)可能的主要途径(地表和地下流动)和水文地球化学迁移。采用一维(1-D)通用反应性化学传输模型(PHREEQC)。校准后的模型表明,运到下游关渡平原和潭水河口的砷分别占地下流路中砷的50.7%和约100%,表明地下流构成了主要的砷路。由于地表和地下路径的pH值低和氧化还原电位高,北水地热谷附近的砷浓度最高。但是,在还原环境中,Fe(II)水溶液可能会清除As。随着模拟时间的增加,下游官渡平原和官渡湿地中的砷浓度降低,导致As吸附在氧化铁表面,并限制了As在表面流路中的迁移率。在关渡平原和关渡湿地地下流动路径中,As迁移的主要延迟机理是由氧化铁和硫化铁矿物的吸附反应决定的。利用一维迁移模型预测了2013年至2020年地下流动路径中As的演化。结果表明,所有细胞中As的浓度逐渐增加。地下路径中As的地球化学氧化还原反应随后导致了含As的硫化物的氧化,导致As浓度在山坡区域显着上升。

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