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利用糖蜜修复六价铬污染地下水的机制与增强作用。

Mechanism and enhancement of Cr(VI) contaminated groundwater remediation by molasses.

机构信息

Key Laboratory of Groundwater Resources and Environment of Ministry of Education, College of New Energy and Environment, Jilin University, Changchun 130021, China; Jilin Provincial Key Laboratory of Water Resources and Environment, College of New Energy and Environment, Jilin University, Changchun 130021, China; National and Local Joint Engineering Laboratory for Petrochemical Contaminated Site Control and Remediation Technology, Jilin University, Changchun 130021, China.

School of Environmental Studies, China University of Geosciences, 388 Lumo Rd., Wuhan, Hubei 430074, China.

出版信息

Sci Total Environ. 2021 Aug 1;780:146580. doi: 10.1016/j.scitotenv.2021.146580. Epub 2021 Mar 19.

Abstract

The remediation of Cr(VI)-contaminated groundwater with molasses has many advantages compared with traditional in-situ chemical methods, including high cost-effectiveness and negligible secondary contamination. Hence, the reaction conditions and mechanisms of molasses were investigated in this study. The results showed that Cr(VI) was chemically reduced by molasses at acidic pH (3.0), wherein the dominant active components were the hydroxyl and carbonyl groups of molasses. At neutral pH (7.0), molasses mainly acted as an electron donor for direct or indirect reduction of Cr(VI) by microorganisms. The main functional microorganisms were Bacillus and Clostridium Sensu Stricto. Compared with chemical reduction, bio-reduction could completely reduce higher concentrations of Cr(VI) when molasses was added at a concentration of 3 g/L. Ascorbic acid was added to promote the removal rate of bioremediation. Owing to the antioxidant properties of ascorbic acid, the reaction rate increased by 9.3% and 37.5% when 0.05 g/L of ascorbic acid was added to the 50 and 100 mg/L Cr(VI) bioremediation systems, respectively. Due to the decrease in pH during bioremediation, NaHCO was added to buffer the pH changes and promote Cr(III) precipitation. Compared with the addition of NaHCO and molasses simultaneously, separate additions were more effective for precipitation. Furthermore, X-ray absorption near-edge structure analysis revealed that after chemical reduction and biological reduction, Cr was attached to the solid medium in the form of Cr(III).

摘要

与传统的原位化学方法相比,利用糖蜜修复六价铬污染地下水具有许多优势,包括高成本效益和可忽略的二次污染。因此,本研究考察了糖蜜的反应条件和机制。结果表明,在酸性 pH(3.0)下,糖蜜通过化学还原作用将六价铬还原,其中糖蜜的主要活性成分是羟基和羰基。在中性 pH(7.0)下,糖蜜主要作为电子供体,通过微生物直接或间接还原六价铬。主要功能微生物是芽孢杆菌属和严格梭菌属。与化学还原相比,当添加浓度为 3 g/L 的糖蜜时,生物还原可以完全还原更高浓度的六价铬。添加抗坏血酸以促进生物修复的去除率。由于抗坏血酸具有抗氧化特性,当向 50 和 100 mg/L 的六价铬生物修复体系中分别添加 0.05 g/L 的抗坏血酸时,反应速率分别提高了 9.3%和 37.5%。由于生物修复过程中 pH 值降低,添加 NaHCO 缓冲 pH 值变化并促进 Cr(III)沉淀。与同时添加 NaHCO 和糖蜜相比,分别添加更有利于沉淀。此外,X 射线吸收近边结构分析表明,化学还原和生物还原后,Cr 以 Cr(III)的形式附着在固体介质上。

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