School of Resources and Environmental Engineering, Anhui University, Hefei 230601, China; Anhui Province Engineering Laboratory for Mine Ecological Remediation, Hefei 230601, China.
School of Resources and Environmental Engineering, Anhui University, Hefei 230601, China; Anhui Province Engineering Laboratory for Mine Ecological Remediation, Hefei 230601, China.
J Environ Manage. 2023 Dec 1;347:119127. doi: 10.1016/j.jenvman.2023.119127. Epub 2023 Oct 3.
This study prepared and characterized bamboo-derived biochar loaded with different ratios of iron and manganese; evaluated its remediation performance in arsenic-contaminated soil by studying the changes in various environmental factors, arsenic speciation, and arsenic leaching amount in the soil after adding different materials; proposed the optimal ratio and mechanism of iron-manganese removal of arsenic; and explained the multivariate relationship between enzyme activity and soil environmental factors based on biological information. Treatment with Fe-Mn-modified biochar increased the organic matter, cation exchange capacity, and N, P, K, and other nutrient contents. During the remediation process, O-containing functional groups such as Mn-O/As and Fe-O/As were formed on the surface of the biochar, promoting the transformation of As from the mobile fraction to the residual fraction and reducing the phytotoxicity of As, and the remediation ability for As was superior to that of Fe-modified biochar. Mn is indispensable in the FeMn-BC synergistic remediation of As, as it can increase the adsorption sites and the number of functional groups for trace metals on the surface of biochar. In addition to electrostatic attraction, the synergistic mechanism of ferromanganese-modified biochar for arsenic mainly involves redox and complexation. Mn oxidizes As(Ⅲ) to more inert As(V). In this reaction process, Mn(Ⅳ) is reduced to Mn(Ⅲ) and Mn(II), promoting the formation of Fe(Ⅲ) and the conversion of As into Fe-As complexes, while As is fixed due to the formation of ternary surface complexes. Moreover, the effect of adding Fe-Mn-modified biochar on soil enzyme activity was correlated with changes in soil environmental factors; catalase was correlated with soil pH; neutral phosphatase was correlated with soil organic matter; urease was correlated with ammonia nitrogen, and sucrase activity was not significant. This study highlights the potential value of FM1:3-BC as a remediation agent in arsenic-contaminated neutral soils.
本研究制备并表征了不同铁锰比例负载的竹基生物炭;通过研究添加不同材料后土壤中各种环境因素、砷形态和土壤浸出量的变化,评估了其在砷污染土壤中的修复性能;提出了铁锰去除砷的最佳比例和机制;并基于生物信息解释了酶活性与土壤环境因素之间的多元关系。用 Fe-Mn 改性生物炭处理后,土壤的有机质、阳离子交换量和 N、P、K 等养分含量增加。在修复过程中,生物炭表面形成了 Mn-O/As 和 Fe-O/As 等含氧官能团,促进了 As 从可移动态向残渣态的转化,降低了 As 的植物毒性,修复 As 的能力优于 Fe 改性生物炭。Mn 在 FeMn-BC 协同修复 As 中是不可或缺的,因为它可以增加生物炭表面痕量金属的吸附点位和官能团数量。除了静电吸引外,铁锰改性生物炭协同去除砷的机制主要涉及氧化还原和络合。Mn 将 As(Ⅲ)氧化为更惰性的 As(V)。在这个反应过程中,Mn(Ⅳ)被还原为 Mn(Ⅲ)和 Mn(II),促进了 Fe(Ⅲ)的形成和 As 的转化为 Fe-As 络合物,而由于三元表面络合物的形成,As 被固定。此外,添加 Fe-Mn 改性生物炭对土壤酶活性的影响与土壤环境因素的变化有关;过氧化氢酶与土壤 pH 有关;中性磷酸酶与土壤有机质有关;脲酶与氨氮有关,而蔗糖酶活性不显著。本研究突出了 FM1:3-BC 作为一种修复剂在中性砷污染土壤中的潜在价值。