School of Resource and Environmental Science, Wuhan University, Wuhan 430072, Hubei, China; Zhaoqing (Wuhan University) Environmental Technology Research Institute, Zhaoqing 526200, Guangdong, China.
Central-southern Safety & Environmental Technology Institute Co., Ltd, Wuhan 430071, Hubei, China.
Sci Total Environ. 2022 Jan 10;803:149866. doi: 10.1016/j.scitotenv.2021.149866. Epub 2021 Sep 3.
Heavy metal (HM) soil pollution has become an increasingly serious problem with the development of industries. Application of biochar in HMs remediation from contaminated environment has attracted considerable research attention during the past decade. Although the mechanism of HMs passivation with biochar has been investigated, effects and mechanisms of interaction among soil-indigenous microbes and novel carbon matrix composites for HMs adsorption and passivation are still unclear. Four different biochar-loaded aerogels, namely, BNCA-1-600, BNCA-1-900, BNCA-2-600, and BNCA-2-900, were synthesized in this study. Adsorption capacity of four kinds of synthetic materials and two types of contrast biochars (BC600 and BC900) to HMs in aqueous solution, passivation capacity of HMs in soil, and effects on soil organic matter and microbial community were explored. Results showed that BNCA-2-900 exhibits excellent adsorption property and a maximum removal capacity of 205.07 mg·g at 25 °C for Pb(II), 105.56 mg·g for Cd(II), and 137.89 mg·g for Zn(II). Leaching concentration of HMs in contaminated soil can meet the national standard of China (GB/T 5085.3-2007) within 120 days. Results of this study confirmed that the additive BNCA-2-900 and coexistence of indigenous microorganisms can effectively reduce bioavailability of HMs. Another potential mechanism may be to remove the passivation of HMs by porous structure and surface functional groups as well as improve the content of organic matter and microbial abundance. The research results may provide a novel perceptive for the development of functional materials and strategies for eco-friendly and sustainable multiple HMs remediation in contaminated soil and water by using a combination of carbon matrix composites and soil-indigenous microorganisms.
重金属(HM)土壤污染随着工业的发展而变得日益严重。在过去的十年中,生物炭在修复受污染环境中的重金属方面的应用引起了相当多的研究关注。尽管已经研究了生物炭对重金属的钝化机制,但土壤中原生微生物与新型碳基质复合材料之间的相互作用及其对重金属吸附和钝化的影响和机制仍不清楚。本研究合成了四种不同负载生物炭的气凝胶,即 BNCA-1-600、BNCA-1-900、BNCA-2-600 和 BNCA-2-900。探讨了四种合成材料和两种对照生物炭(BC600 和 BC900)对水溶液中重金属的吸附能力、土壤中重金属的钝化能力以及对土壤有机质和微生物群落的影响。结果表明,BNCA-2-900 在 25°C 下对 Pb(II)、Cd(II)和 Zn(II)的最大去除容量分别为 205.07、105.56 和 137.89mg·g,表现出优异的吸附性能。在 120 天内,污染土壤中重金属的浸出浓度可达到中国国家标准(GB/T 5085.3-2007)的要求。本研究结果证实,添加剂 BNCA-2-900 和土著微生物的共存可以有效降低重金属的生物有效性。另一个潜在的机制可能是通过多孔结构和表面官能团去除重金属的钝化作用,同时提高有机质含量和微生物丰度。研究结果可能为利用碳基质复合材料和土壤中原生微生物的组合开发功能材料和生态友好且可持续的多种重金属污染土壤和水修复策略提供新的思路。