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研究溶解性有机质对河岸渗滤过程中铁、锰和砷迁移的影响特征。

Characterisation of the impact of dissolved organic matter on iron, manganese, and arsenic mobilisation during bank filtration.

机构信息

Delft University of Technology, P.O. Box 5048, 2600 GA, Delft, the Netherlands; IHE Delft Institute for Water Education, P.O.Box 3015, 2601 DA, Delft, the Netherlands.

IHE Delft Institute for Water Education, P.O.Box 3015, 2601 DA, Delft, the Netherlands.

出版信息

J Environ Manage. 2020 Mar 15;258:110003. doi: 10.1016/j.jenvman.2019.110003. Epub 2020 Jan 7.

Abstract

Bank filtration (BF) has been used for many years as an economical technique for providing high-quality drinking water. However, under anaerobic conditions, the aquifer release of undesirable metal(loid)s, such as iron manganese, and arsenic, reduces the bank filtrate quality and thus restricts the application of this technique. This study investigates the impact of the organic-matter composition of source water on the mobilisation of Fe, Mn, and As during the anaerobic BF process. A laboratory-scale column study was conducted at a controlled-temperature (30 ± 2 °C) using different feed water sources. The organic matter characteristics of the feed water were elucidated using excitation-emission spectroscopy techniques integrated with parallel factor framework clustering analysis (PFFCA) model. The experiment was performed at redox conditions between 66 mv and -185 mv. Moreover, batch studies were implemented to study the effect of natural organic matter type (humic, fulvic and tyrosine) and concentration on the mobilisation of the selected metal(loids). The laboratory experiments demonstrated that the mobilisation of Fe, Mn and As during the BF are varied with the organic water concentration and composition of the source water. The fluorescence results revealed that terrestrial and condensed structure humic compounds are more capable to release Fe into the filtrate water. In contrast, Mn exhibited an equal tendency of mobilisation towards all the humic compounds regardless of its origin and structure. However, at a humic concentration higher than 5 mg-C/L, Mn showed more affinity towards lower molecular weight humic compounds. Arsenic was found to be the least impacted by the alteration in the source water organic matter composition; its mobilisation was highly correlated with iron releasing process. On the other hand, the biodegradable organic matter at high concentration (>10 mg-C/L) was found to be highly effective to turn the infiltration area into Fe-reducing environment and thereby elevating Fe and As concentrations in the pumped water. In conclusion, this study revealed that the DOM composition and concentration of the raw water could play an important role in the mobilisation of metal(loids) during the BF processes.

摘要

多年来,地下水自然渗滤(BF)一直被用作提供高质量饮用水的经济技术。然而,在厌氧条件下,含水层释放出不受欢迎的金属(如铁、锰和砷),降低了渗滤水的质量,从而限制了该技术的应用。本研究调查了水源中有机物组成对厌氧 BF 过程中 Fe、Mn 和 As 迁移的影响。在受控温度(30±2°C)下,使用不同的原水进行了实验室规模的柱实验。使用激发-发射光谱技术与平行因子框架聚类分析(PFFCA)模型相结合,阐明了原水的有机物特性。实验在 66 mV 至-185 mV 的氧化还原条件下进行。此外,还进行了批量研究,以研究天然有机物类型(腐殖质、富里酸和酪氨酸)和浓度对所选金属(类)迁移的影响。实验室实验表明,BF 过程中 Fe、Mn 和 As 的迁移随水源中有机物浓度和组成的变化而变化。荧光结果表明,陆地和浓缩结构的腐殖质化合物更有能力将 Fe 释放到滤出水中。相比之下,Mn 表现出对所有腐殖质化合物同等的迁移趋势,无论其来源和结构如何。然而,在腐殖质浓度高于 5 mg-C/L 时,Mn 对低分子量腐殖质化合物表现出更高的亲和力。发现砷受原水有机物组成变化的影响最小;其迁移与铁释放过程高度相关。另一方面,高浓度(>10 mg-C/L)的可生物降解有机物被发现非常有效地将渗透区转变为铁还原环境,从而提高了抽水中的铁和砷浓度。总之,本研究表明,原水中 DOM 的组成和浓度在 BF 过程中金属(类)的迁移中可能起着重要作用。

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