Chen Ning, Geng Mengyuan, Huang Danyu, Tan Mengxi, Li Zipeng, Liu Guangxia, Zhu Changyin, Fang Guodong, Zhou Dongmei
State Key Laboratory of Pollution Control and Resource Reuse, School of the Environment, Nanjing University, Nanjing 210023, Jiangsu, China.
Key Laboratory of Soil Environment and Pollution Remediation, Institute of Soil Science, Chinese Academy of Sciences, Nanjing 210008, Jiangsu, China.
J Hazard Mater. 2022 Jul 15;434:128861. doi: 10.1016/j.jhazmat.2022.128861. Epub 2022 Apr 6.
Many studies have examined the redox behavior of ferrous ions (Fe(II)) sorbed to mineral surfaces. However, the associated hydroxyl radical (OH) formation during Fe(II) oxidation by O was rarely investigated at circumneutral pH. Therefore, we examined OH formation during oxygenation of adsorbed Fe(II) (Fe(II)) on common minerals. Results showed that 16.7 ± 0.4-25.6 ± 0.3 μM of OH was produced in Fe(II) and α/γ-AlO systems after oxidation of 24 h, much more than in systems with dissolved Fe(II) (Fe) alone (10.3 ± 0.1 μM). However, OH production in Fe(II) and α-FeOOH/α-FeO systems (6.9 ± 0.1-8.3 ± 0.1 μM) slightly decreased compared to Fe only. Further analyses showed that enhanced oxidation of Fe(II) was responsible for the increased OH production in the Fe(II)/AlO systems. In comparison, less Fe(II) was oxidized in the α-FeOOH/α-FeO systems, which was probably ascribed to the quick electron-transfer between Fe(II) and Fe(III) lattice due to their semiconductor properties and induced formation of high-crystalline Fe(II) phases that hindered Fe(II) oxidation and OH formation. The types of minerals and solution pH strongly affected Fe(II) oxidation and OH production, which consequently impacted phenol degradation. This study highlights that the properties of minerals exert great impacts on surface-Fe(II) oxidation and OH production during water/soil redox fluctuations.
许多研究都考察了吸附在矿物表面的亚铁离子(Fe(II))的氧化还原行为。然而,在接近中性的pH值条件下,由O氧化Fe(II)过程中相关的羟基自由基(OH)生成情况却鲜有研究。因此,我们研究了常见矿物上吸附的Fe(II)(Fe(II))在氧化过程中的OH生成情况。结果表明,在24小时氧化后,Fe(II)与α/γ-AlO体系中产生了16.7±0.4 - 25.6±0.3 μM的OH,比仅含有溶解态Fe(II)(Fe)的体系(10.3±0.1 μM)多得多。然而,与仅含Fe的体系相比,Fe(II)与α-FeOOH/α-FeO体系中的OH生成量(6.9±0.1 - 8.3±0.1 μM)略有下降。进一步分析表明,Fe(II)氧化增强是Fe(II)/AlO体系中OH生成量增加的原因。相比之下,α-FeOOH/α-FeO体系中被氧化的Fe(II)较少,这可能归因于Fe(II)与Fe(III)晶格之间由于其半导体性质而发生的快速电子转移,以及诱导形成的高结晶度Fe(II)相阻碍了Fe(II)氧化和OH生成。矿物类型和溶液pH值强烈影响Fe(II)氧化和OH生成,进而影响苯酚降解。本研究强调,在水/土壤氧化还原波动过程中,矿物性质对表面Fe(II)氧化和OH生成有很大影响。