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载铁地下水的延时曝气双介质砂滤除砷。

Arsenic removal from iron-containing groundwater by delayed aeration in dual-media sand filters.

机构信息

Sanitary Engineering Section, Department of Water Management, Delft University of Technology, The Netherlands.

Sanitary Engineering Section, Department of Water Management, Delft University of Technology, The Netherlands.

出版信息

J Hazard Mater. 2021 Jun 5;411:124823. doi: 10.1016/j.jhazmat.2020.124823. Epub 2020 Dec 11.

Abstract

Generally, abstracted groundwater is aerated, leading to iron (Fe) oxidation to Fe and precipitation as Fe-(hydr)oxide (HFO) flocs. This practice of passive groundwater treatment, however, is not considered a barrier for arsenic (As), as removal efficiencies vary widely (15-95%), depending on Fe/As ratio. This study hypothesizes that full utilization of the adsorption capacity of groundwater native-Fe based HFO flocs is hampered by rapid Fe oxidation-precipitation during aeration before or after storage. Therefore, delaying Fe oxidation by the introduction of an anoxic storage step before aeration-filtration was investigated for As(III) oxidation and removal in Rajshahi (Bangladesh) with natural groundwater containing 329(±0.05) µgAs/L. The results indicated that As(III) oxidation in the oxic storage was higher with complete and rapid Fe oxidation (2±0.01 mg/L) than in the anoxic storage system, where Fe oxidation was partial (1.03±0.32 mg/L), but the oxidized As(V)/Fe removal ratio was comparatively higher for the anoxic storage system. The low pH (6.9) and dissolved oxygen (DO) concentration (0.24 mg/L) in the anoxic storage limited the rapid oxidation of Fe and facilitated more As(V) removal. The groundwater native-Fe (2.33±0.03 mg/L) removed 61% of As in the oxic system (storage-aeration-filtration), whereas 92% As removal was achieved in the anoxic system.

摘要

一般来说,地下水会被曝气充氧,导致铁(Fe)氧化为 Fe 并沉淀为铁(氢)氧化物(HFO)絮体。然而,这种被动地下水处理方法并不能有效去除砷(As),因为去除效率差异很大(15-95%),这取决于 Fe/As 比值。本研究假设,在曝气-过滤之前或之后的储存过程中,由于曝气导致的铁快速氧化-沉淀,会阻碍地下水天然铁基 HFO 絮体吸附能力的充分利用。因此,本研究在孟加拉国拉杰沙希市,用含有 329(±0.05) µgAs/L 的天然地下水,通过在曝气-过滤前引入缺氧储存步骤来延迟铁氧化,以研究其对 As(III)氧化和去除的影响。结果表明,在有氧储存条件下,由于完全和快速的铁氧化(2±0.01 mg/L),As(III)氧化率高于缺氧储存系统(铁氧化率为 1.03±0.32 mg/L),但缺氧储存系统的氧化 As(V)/Fe 去除率相对较高。缺氧储存系统的低 pH 值(6.9)和溶解氧(DO)浓度(0.24 mg/L)限制了铁的快速氧化,有利于更多的 As(V)去除。地下水天然铁(2.33±0.03 mg/L)在有氧系统(储存-曝气-过滤)中去除了 61%的 As,而在缺氧系统中则去除了 92%的 As。

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