低渗透带中还原性铁矿物对三氯乙烯的非生物氧化与还原

IF 4.3 Q1 ENVIRONMENTAL SCIENCES
Girish Kumar, Albert J. Valocchi, Shenyi Dai, Chun-Yu Shih, Zijie Zheng, Charles E. Schaefer and Charles J. Werth*, 
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引用次数: 0

摘要

三氯乙烯(TCE)从低渗透带(LPZs)反扩散对许多污染场地的地下水修复提出了重大挑战。这项研究调查了非生物氧化和TCE的还原是否可以在好氧含水层和厌氧富铁lpz之间的过渡中共同发生。扩散瓶实验使用还原粘土暴露于TCE和氧气。结果表明,氧与还原铁矿物(RIMs)的反应速度比TCE快,这限制了氧的渗透,使TCE扩散得更深。氧化产物在LPZ表面附近形成,而还原性气体在更深的深度产生。对照实验表明,TCE氧化产物可能通过未知途径形成一些还原性气体。根据实验数据校准的反应输运模型预测,在现场尺度上,由于氧气扩散到LPZ的限制,几十年后,TCE的还原作用大于氧化作用。然而,这种平衡取决于特定地点的因素,如氧可用性、RIM含量和LPZ厚度。这些发现为lpz中TCE的非生物氧化和还原同时发生提供了第一个直接的实验证据,并表明还原可能在长期衰减中发挥更大的作用。为了评估修复效果,需要对不同的LPZ土壤进行实地验证和速率量化。
本文章由计算机程序翻译,如有差异,请以英文原文为准。

Simultaneous Abiotic Oxidation and Reduction of Trichloroethylene by Reduced Iron Minerals in Low-Permeability Zones

Simultaneous Abiotic Oxidation and Reduction of Trichloroethylene by Reduced Iron Minerals in Low-Permeability Zones

Back diffusion of trichloroethylene (TCE) from low-permeability zones (LPZs) poses a major challenge to groundwater remediation at many contaminated sites. This study investigated whether abiotic oxidation and reduction of TCE can co-occur at transitions between aerobic aquifers and anaerobic, iron-rich LPZs. Diffusion-vial experiments were conducted using reduced clay exposed to TCE and oxygen. Results showed that oxygen reacts more rapidly with reduced iron minerals (RIMs) than TCE, limiting oxygen penetration and allowing TCE to diffuse deeper. Oxidation products formed near the LPZ surface, while reduced gases were generated at a greater depth. Control experiments revealed that some reduced gases may form from TCE oxidation products via an unknown pathway. A reactive transport model calibrated to experimental data predicted that, at the field scale, TCE reduction dominates over oxidation after several decades due to limited oxygen diffusion into the LPZ. However, this balance depends on site-specific factors such as oxygen availability, RIM content, and LPZ thickness. These findings provide the first direct experimental evidence for the simultaneous abiotic oxidation and reduction of TCE in LPZs and suggest that reduction likely plays a greater role in long-term attenuation. Field validation and rate quantification over different LPZ soils are needed to assess the remediation impact.

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