School of Environmental Science & Engineering, Sun Yat-sen University, Guangzhou 510275, China.
School of Environment, Guangdong Provincial Key Laboratory of Chemical Pollution and Environmental Safety & MOE Key Laboratory of Theoretical Chemistry of Environment, South China Normal University, Guangzhou 510006, China.
Water Res. 2024 Apr 1;253:121270. doi: 10.1016/j.watres.2024.121270. Epub 2024 Feb 5.
Sulfidated zero-valent iron (S-ZVI) is an attractive material of permeable reactive barriers (PRBs) for the remediation of contaminated groundwater. However, S-ZVI is prone to be passivated due to the oxidation of reactive and conductive iron sulfide (FeS) shell and the formation of inactive and non-conductive ferric (hydr)oxides, which serve as electron transfer barriers to hinder the electron flow from Fe° core to contaminants. This study thus proposed a novel approach for in-situ reactivation and reuse of micronsized S-ZVI (S-mZVI) in PRB using sulfate-reducing bacteria (SRB) enriched culture to realize long-lasting remediation of Cr(VI)-contaminated groundwater. S-mZVI were passivated after reactions with Cr(VI) due to the formation of electron transfer barriers (mainly inactive and non-conductive Fe(III) (hyd)oxides, which increased the polarization resistance from 16.38 to 27.38 kΩ cm and hindered the electron transfer from the Fe° core. Interestingly, the passivated S-mZVI was efficiently reactivated by providing the SRB-enriched culture and organic carbon within 12 h, and the Cr(VI) removal capacity of S-mZVI in the three use cycles increased to 37.4 mg Cr/g, which was 2.1 times higher than that of the virgin S-mZVI. After biological reactivation, the R of reactivated S-mZVI decreased to 12.30 kΩ cm. SRB-mediated reactivation removed the electron transfer barriers via biotic and abiotic reduction of Fe(III) (hyd)oxides. Especially, the microbial Fe(III) reduction mediated by FmnA-dmkA-fmnB-pplA-ndh2-eetAB-dmkB protein family enhanced the Fe release from the surface and the subsequent re-formation of reactive and conductive FeS shell. A long-term PRB column test further demonstrated the feasibility of in-situ biological reactivation and reuse of S-mZVI for enhanced Cr(VI)-contaminated groundwater remediation. Within 64 days, the Cr(VI) removal capacity of S-mZVI in the four use cycles increased by 3.2 times, compared to the virgin one. The bio-reactivation using the SRB-enriched culture and sulfate locally-available in groundwater will reduce the chemical and maintenance costs associated with the frequent replacement of reactive ZVI-based materials. The PRB technology based on the bio-renewable S-mZVI can be a sustainable alternative to the conventional PRBs for the long-lasting and low-cost remediation of groundwater contaminated by oxidative pollutants.
硫化零价铁 (S-ZVI) 是一种有吸引力的可渗透反应性屏障 (PRB) 材料,可用于修复受污染的地下水。然而,由于反应性和传导性硫化亚铁 (FeS) 壳的氧化以及不活跃和非传导性铁 (氢) 氧化物的形成,S-ZVI 很容易被钝化,这作为电子传递障碍,阻碍电子从 Fe°核心流向污染物。因此,本研究提出了一种使用硫酸盐还原菌 (SRB) 富集培养物原位再激活和再利用微米级 S-ZVI (S-mZVI) 的新方法,以实现对 Cr(VI) 污染地下水的持久修复。S-mZVI 与 Cr(VI) 反应后由于形成电子传递障碍(主要是不活跃和非传导性 Fe(III) (氢) 氧化物)而被钝化,这增加了极化电阻从 16.38 到 27.38 kΩ cm,并阻碍了电子从 Fe°核心传递。有趣的是,通过在 12 小时内提供 SRB 富集培养物和有机碳,被钝化的 S-mZVI 可以有效地被再激活,并且 S-mZVI 在三个使用循环中的 Cr(VI)去除能力增加到 37.4 mg Cr/g,这是原始 S-mZVI 的 2.1 倍。再生物激活后,再激活的 S-mZVI 的 R 降低到 12.30 kΩ cm。SRB 介导的再激活通过生物和非生物还原 Fe(III) (氢) 氧化物去除了电子传递障碍。特别是,由 FmnA-dmkA-fmnB-pplA-ndh2-eetAB-dmkB 蛋白家族介导的微生物 Fe(III) 还原增强了铁从表面的释放和随后反应性和传导性 FeS 壳的再形成。长期的 PRB 柱试验进一步证明了原位生物再激活和再利用 S-mZVI 以增强 Cr(VI) 污染地下水修复的可行性。在 64 天内,与原始 S-mZVI 相比,S-mZVI 在四个使用循环中的 Cr(VI)去除能力增加了 3.2 倍。使用 SRB 富集培养物和地下水中局部可用的硫酸盐进行生物再激活将降低与频繁更换基于反应性 ZVI 的材料相关的化学和维护成本。基于生物可再生 S-mZVI 的 PRB 技术可为传统 PRB 提供一种可持续的替代方案,用于持久和低成本修复受氧化污染物污染的地下水。