College of Life and Environmental Sciences, Minzu University of China, Beijing, 100081, China.
Technical Centre for Soil, Agriculture and Rural Ecology and Environment, Ministry of Ecology and Environment, Beijing, 100012, China.
Environ Res. 2024 Jun 1;250:118470. doi: 10.1016/j.envres.2024.118470. Epub 2024 Feb 17.
In-situ passivation technique has attracted increasing attention for metal-contaminated agricultural soil remediation. However, metal immobilization mechanisms are mostly illustrated based on metal speciation changes and alterations in soil physicochemical properties from a macroscopic and abiotic perspective. In this study, a ferrihydrite-synthetic humic-like acid composite (FH-SHLA) was fabricated and applied as a passivator for a 90-day soil incubation. The heavy metals immobilization mechanisms of FH-SHLA were investigated by combining both abiotic and biotic perspectives. Effects of FH-SHLA application on soil micro-ecology were also evaluated. The results showed that the 5%FH-SHLA treatment significantly decreased the DTPA-extractable Pb, Cd and Zn by 80.75%, 46.82% and 63.63% after 90 days of incubation (P < 0.05), respectively. Besides, 5% FH-SHLA addition significantly increased soil pH, soil organic matter content and cation exchange capacity (P < 0.05). The SEM, FTIR, and XPS characterizations revealed that the abiotic metal immobilization mechanisms by FH-SHLA included surface complexation, precipitation, electrostatic attraction, and cation-π interactions. For biotic perspective, in-situ microorganisms synergistically participated in the immobilization process via sulfide precipitation and Fe mineral production. FH-SHLA significantly altered the diversity and composition of the soil microbial community, and enhanced the intensity and complexity of the microbial co-occurrence network. Both metal bioavailability and soil physiochemical parameters played a vital role in shaping microbial communities, while the former contributed more. Overall, this study provides new insight into the heavy metal passivation mechanism and demonstrates that FH-SHLA is a promising and environmentally friendly amendment for metal-contaminated soil remediation.
原位钝化技术因其能有效修复重金属污染土壤而受到广泛关注。然而,从宏观和非生物的角度来看,金属固定机制主要是通过金属形态变化和土壤理化性质的改变来阐明的。本研究采用合成的类腐殖质铁(FH-SHLA)作为钝化剂进行了为期 90 天的土壤培养实验,从非生物和生物两方面研究了 FH-SHLA 对重金属的固定机制,并评估了 FH-SHLA 对土壤微生态的影响。结果表明,在 90 天的培养期内,5%FH-SHLA 处理可使土壤中 DTPA 可提取态 Pb、Cd 和 Zn 分别显著降低 80.75%、46.82%和 63.63%(P<0.05)。此外,添加 5%FH-SHLA 可显著增加土壤 pH、土壤有机质含量和阳离子交换容量(P<0.05)。SEM、FTIR 和 XPS 分析表明,FH-SHLA 对重金属的非生物固定机制包括表面络合、沉淀、静电吸引和阳离子-π相互作用。从生物角度来看,原位微生物通过硫化物沉淀和 Fe 矿物生成协同参与了固定过程。FH-SHLA 显著改变了土壤微生物群落的多样性和组成,并增强了微生物共生网络的强度和复杂性。土壤中重金属的生物有效性和理化参数都对土壤微生物群落的结构有重要影响,而前者的贡献更大。总的来说,本研究为重金属钝化机制提供了新的见解,并证明 FH-SHLA 是一种有前景且环境友好的修复重金属污染土壤的改良剂。