Zhang Wenjie, Qin Xiang'ao, Li Xibin
School of Civil Engineering and Architecture, Taizhou University, Taizhou, 318000, China.
School of Mechanics and Engineering Science, Shanghai University, Shanghai, 200444, China.
Environ Res. 2025 Apr 1;270:121008. doi: 10.1016/j.envres.2025.121008. Epub 2025 Jan 31.
Iron-manganese oxide modified biochar (FMO-BC) was prepared for remediation of contaminated soil with As content of 1300 mg kg. The remediation scheme mainly includes oxidizing As(III) into less mobile As(V) by manganese oxide, stabilizing As(V) by iron oxide, and simultaneously reducing the aggregation of iron-manganese oxide (FMO) by BC support. The remediation effect and detailed mechanism were investigated through leaching tests, freeze-thaw experiment, sequential extraction procedure, and a series of spectroscopic/microscopic analyses. The results showed that the optimal FMO loading rate on BC was 25%. Owning to neutralization of alkaline BC and acidic hydrolysate of ferric iron, the addition of FMO-BC caused only a little change in soil pH, thereby mitigating the risk of As leaching under high pH condition. The FMO-BC treatment is more effective than FMO. After freeze-thaw cycles, the further dispersion of FMO and the presence of more functional groups enhanced the treatment effect. At 7 wt% of FMO-BC, the leaching concentration of As was reduced to 0.456 mg L, and the stabilization efficiency reached 98.6%. The FMO-BC treatment reduced fractions of exchangeable and carbonate-bound forms of As from 41.1% to 1.84%, substantially reducing the environmental risk. FMO-BC oxidized most As(III) in the soil into As(V), facilitated the formation of Fe-O-As and Mn-O-As complexes. The stabilization mechanism included oxidation, precipitation, and complexation reactions. By loading on BC, the aggregation of FMO was reduced and FMO dosage can be lowered. The proposed technique showed high efficiency, environmental friendliness, and great application prospect.
制备了铁锰氧化物改性生物炭(FMO-BC)用于修复砷含量为1300 mg/kg的污染土壤。修复方案主要包括通过氧化锰将As(III)氧化为迁移性较低的As(V),通过氧化铁稳定As(V),同时通过生物炭载体减少铁锰氧化物(FMO)的团聚。通过浸出试验、冻融实验、连续提取程序以及一系列光谱/显微镜分析研究了修复效果和详细机理。结果表明,生物炭上FMO的最佳负载率为25%。由于碱性生物炭与铁离子酸性水解产物的中和作用,添加FMO-BC对土壤pH值的影响很小,从而降低了高pH条件下砷浸出的风险。FMO-BC处理比FMO更有效。经过冻融循环后,FMO的进一步分散以及更多官能团的存在增强了处理效果。在FMO-BC含量为7 wt%时,砷的浸出浓度降至0.456 mg/L,稳定化效率达到98.6%。FMO-BC处理使可交换态和碳酸盐结合态砷的比例从41.1%降至1.84%,大幅降低了环境风险。FMO-BC将土壤中大部分As(III)氧化为As(V),促进了Fe-O-As和Mn-O-As络合物的形成。稳定化机制包括氧化、沉淀和络合反应。通过负载在生物炭上,减少了FMO的团聚,降低了FMO的用量。所提出的技术具有高效、环保和广阔的应用前景。