National-Regional Joint Engineering Research Center for Soil Pollution Control and Remediation in South China, Guangdong Key Laboratory of Integrated Agro-environmental Pollution Control and Management, Institute of Eco-environmental and Soil Sciences, Guangdong Academy of Sciences, Guangzhou 510650, China; College of Resources and Environment, Chongqing School, University of Chinese Academy of Sciences, Chongqing 400714, China.
National-Regional Joint Engineering Research Center for Soil Pollution Control and Remediation in South China, Guangdong Key Laboratory of Integrated Agro-environmental Pollution Control and Management, Institute of Eco-environmental and Soil Sciences, Guangdong Academy of Sciences, Guangzhou 510650, China; State Key Laboratory of Environmental Geochemistry, Institute of Geochemistry, Chinese Academy of Science, Guiyang 550081, China.
J Environ Sci (China). 2024 Mar;137:626-638. doi: 10.1016/j.jes.2023.03.011. Epub 2023 Mar 21.
Transition metal iron and persistent free radicals (PFRs) both affect the redox properties of biochar, but the electron transfer relationship between them and the coupling reduction mechanism of Cr(VI) requires further investigation. To untangle the interplay between iron and PFRs in biochar and the influences on redox properties, FeCl-modified rice husk biochar (FBCs) was prepared and its reduction mechanism for Cr(VI) without light was evaluated. The FBCs had higher surface positive charges, oxygen-containing functional groups, and PFRs compared with pristine rice husk biochar (BC). Phenoxyl PFRs with high electron-donating capability formed in biochar. The pronounced electron paramagnetic resonance signals showed that the PFRs preferred to form at lower Fe(III) concentrations. While a high concentration of Fe(III) would be reduced to Fe(II) and consumed the formed PFRs. Adsorption kinetics and X-ray photoelectron spectroscopy analysis indicated that the FBCs effectively enhanced the Cr(VI) removal efficiency by 1.54-8.20 fold and the Cr(VI) reduction efficiency by 1.88-9.29 fold compared to those of BC. PFRs quenching and competitive reductant addition experiments revealed that the higher Cr(VI) reduction performance of FBCs was mainly attributed to the formed PFRs, which could contribute to ∼74.0% of Cr(VI) reduction by direct or indirect electron transfer. The PFRs on FBCs surfaces could promote the Fe(III)/Fe(II) cycle through single electron transfer and synergistically accelerate ∼52.3% of Cr(VI) reduction. This study provides an improved understanding of the reduction mechanism of iron-modified biochar PFRs on Cr(VI) in environments.
过渡金属铁和持久性自由基(PFRs)都会影响生物炭的氧化还原特性,但它们之间的电子转移关系和 Cr(VI) 的偶联还原机制仍需进一步研究。为了理清生物炭中铁和 PFRs 之间的相互作用及其对氧化还原性质的影响,制备了 FeCl 改性稻壳生物炭(FBCs),并评价了其在无光照条件下对 Cr(VI)的还原机制。与原始稻壳生物炭(BC)相比,FBCs具有更高的表面正电荷、含氧官能团和 PFRs。生物炭中形成了具有高供电子能力的酚氧 PFRs。明显的电子顺磁共振信号表明,PFRs 更喜欢在较低的 Fe(III)浓度下形成。而高浓度的 Fe(III)会被还原为 Fe(II)并消耗形成的 PFRs。吸附动力学和 X 射线光电子能谱分析表明,与 BC 相比,FBCs 可将 Cr(VI)的去除效率提高 1.54-8.20 倍,Cr(VI)的还原效率提高 1.88-9.29 倍。PFRs 猝灭和竞争性还原剂添加实验表明,FBCs 具有较高的 Cr(VI)还原性能主要归因于形成的 PFRs,它们可通过直接或间接电子转移贡献约 74.0%的 Cr(VI)还原。FBCs 表面的 PFRs 可通过单电子转移促进 Fe(III)/Fe(II)循环,并协同加速约 52.3%的 Cr(VI)还原。本研究为深入了解环境中铁改性生物炭 PFRs 对 Cr(VI)的还原机制提供了依据。