School of Minerals Processing and Bioengineering, Central South University, Changsha 410083, China; Key Laboratory of Biometallurgy of Ministry of Education, Central South University, Changsha 410083, China.
School of Minerals Processing and Bioengineering, Central South University, Changsha 410083, China; Key Laboratory of Biometallurgy of Ministry of Education, Central South University, Changsha 410083, China.
Ecotoxicol Environ Saf. 2022 Jul 1;239:113617. doi: 10.1016/j.ecoenv.2022.113617. Epub 2022 May 14.
The investigation of chemical speciation of primary toxic metal(loid)s (Cd, Pb, and As) in soil profile in nonferrous metal smelting site is a key to the assessment of their mobility characteristics and formulation of subsequent remediation strategy. In this study, 74 soil samples were collected at 12 different soil profiles; soil physio-chemical properties and total content of Cd, Pb and As and corresponding chemical speciation were also determined. The results showed that the mean total concentration followed the order of Pb > As > Cd. A large proportion of Pb, Cd and As were accumulated in upper soil profiles (depth < 3 m). Heavy pollution of Pb, Cd and As were observed in the whole soil profile at the area of fuel oil storage tank (ZY6) and lead smelting area (ZY8). The dominant fraction of Cd was exchangeable fraction (F1); Pb was dominant in Fe/Mn oxides-bound fraction (F3) in most cases; Crystallized Fe/Al hydrous oxides bound fraction (F4) generally accounted for a large proportion of As. Mobility factor (MF) followed the order Cd > As > Pb, indicating that Cd was the most mobile element in soil profiles. Pearson correlation analysis found that MF was significantly positively correlated to soil silt; the F4 fraction percentage of As was significantly positively correlated to soil redox potential (Eh). Additionally, MF was found to be positively correlated to crystalline iron (Fe), while negatively correlated to amorphous iron (Fe). The findings reported in this study, on the basis of distribution characteristics of chemical speciation could provide a new solution for future soil remediation at the site. Long-term solutions to metal(loid)s pollution might be offered by microbial-assisted soil washing technique that promotes the transformation of Fe/Mn oxides-bound fraction and organic/sulfide-bound fraction.
对有色金属冶炼场地土壤剖面中主要有毒金属(镉、铅和砷)的化学形态进行调查,是评估其迁移特性和制定后续修复策略的关键。本研究采集了 12 个不同土壤剖面的 74 个土壤样本,测定了土壤理化性质、镉、铅和砷的总量及相应的化学形态。结果表明,土壤中总浓度均值大小顺序为 Pb>As>Cd。大量的 Pb、Cd 和 As 积累在上部土壤剖面(深度<3 m)中。在储油罐(ZY6)和铅冶炼区(ZY8)的整个土壤剖面中均观察到 Pb、Cd 和 As 的重度污染。Cd 的主要赋存形态为可交换态(F1);在大多数情况下,Pb 主要赋存于铁锰氧化物结合态(F3)中;结晶铁/铝水合氧化物结合态(F4)通常占 As 的很大比例。迁移因子(MF)的顺序为 Cd>As> Pb,表明 Cd 是土壤剖面中最具迁移性的元素。Pearson 相关性分析发现,MF 与土壤粉粒呈显著正相关,As 的 F4 分数与土壤氧化还原电位(Eh)呈显著正相关。此外,MF 与结晶铁(Fe)呈正相关,与非晶质铁(Fe)呈负相关。本研究基于化学形态的分布特征,为该场地未来的土壤修复提供了新的解决方案。微生物辅助土壤淋洗技术可以促进铁锰氧化物结合态和有机/硫化物结合态的转化,为解决金属(类)污染问题提供了长期解决方案。