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金属矿山 ›› 2023, Vol. 52 ›› Issue (11): 91-100.

• “矿物材料基础理论与应用技术”专题 • 上一篇    下一篇

半干旱矿区蒙脱石基人工藻结皮的构建及其固铅机制

毕玉晶1 周克强1 夏 令1 宋少先1 朱 江2 胡 勇2
  

  1. 1. 武汉理工大学资源与环境工程学院,湖北 武汉 430070;2. 湖北三鑫金铜股份有限公司,湖北 大冶 435100
  • 出版日期:2023-11-15 发布日期:2024-01-02
  • 基金资助:
    国家自然科学基金项目(编号:32061123009)。

Establishment of Montmorillonite-based Artificial Cyanobacterial Biocrusts and Its Mechanism of Lead Fixation in Semi-arid Mining Area

BI Yujing1 ZHOU Keqiang1 XIA Ling1 SONG Shaoxian1 ZHU Jiang2 HU Yong2 #br#   

  1. 1. School of Resources and Environmental Engineering,Wuhan University of Technology,Wuhan 430070,China;2. Hubei Sanxin Gold and Copper Co. ,Ltd. ,Daye 435100,China
  • Online:2023-11-15 Published:2024-01-02

摘要: 基于半干旱铅矿区水分匮乏、地表退化、铅污染等极端环境问题,构建蒙脱石基人工藻结皮旨在稳定表 土层,防止地表侵蚀,同时固定基质铅,避免尾矿铅浸出威胁生态安全。 本研究采用藻(Microcoleus steenstruppi)与蒙脱 石(MT)在铅基沙土上构建人工藻结皮,通过观察人工藻结皮的形貌变化,同时监测藻结皮的生物学指标变化,获得 蒙脱石促进蓝藻增殖的最佳投入量。 通过粒度、Zeta 电位、SEM-EDS、铅化学形态、FTIR、XRD 分析,探究人工藻结皮 对基质铅的固定能力及解毒机制。 结果表明,M500 中蓝藻的长势最好,其藻丝密度较 M0 大大提高。 第 62 d,最佳处 理组 M500 的叶绿素 a 含量为 M0 的 1. 9 倍。 基质铅可分布于藻丝、胞外聚合物和蒙脱石上。 第 62 d,最佳处理组 M500 的总固铅量为 231. 97 μg / cm2,为 M0 的 1. 2 倍。 在固铅阶段,蒙脱石促使弱酸可交换态、碳酸盐结合态的铅化合物转 化为更稳定的有机结合态、残渣态的铅化合物。 根据表征,人工藻结皮促使基质铅转化为溶解度极低的碱式碳酸铅 和碱式磷酸铅。 因此,蒙脱石基人工藻结皮扩充了其对基质铅的固定效果,并通过降低铅的生物可利用性达到机体 解毒的功效。 本研究首次提出一种粘土型人工藻结皮治理铅污染土壤的新方法,并揭示了人工藻结皮的固铅机理, 为半干旱铅污染矿区生态修复提供了绿色科学的治理手段,对绿水青山工程实践具有重要的理论和实践意义。

关键词: 蒙脱石, 藻, 人工藻结皮, 铅污染, 矿区修复

Abstract: The goal of creating montmorillonite-based artificial algal crusts is to stabilize the topsoil layer,prevent surface erosion,fix the matrix lead,and avoid the threat of tailing lead leaching to ecological security. These artificial cyanobacterial biocrusts are being built in semi-arid lead mining areas because of the extreme environmental problems,such as water shortage,surface degradation,and lead pollution. In this work,lead-based sandy soil was covered with artificial algal crusts made of Microcoleus steenstruppi and montmorillonite (MT). The optimal input of montmorillonite to encourage the growth of cyanobacteria was achieved by studying the morphological changes of artificial cyanobacterial biocrusts and tracking the changes of biological markers of algal crusts. The capacity of artificial cyanobacterial biocrusts on matrix lead to fix lead and its detoxification process were investigated by the use of particle size,Zeta potential,SEM-EDS,lead chemical form,FTIR,and XRD analysis. The findings revealed that M500 had the highest development of cyanobacteria,with a substantially greater filament density than M 0. On day 62,M500,the best treatment group,had a chlorophyll a level that was 1. 9 times higher than M0. Cyanobacterial filaments,extracellular polymers,and montmorillonite can all include matrix lead. On day 62,M500,the best treatment group,had a chlorophyll a level that was 1. 9 times higher than M0. Cyanobacterial filaments,extracellular polymers and montmorillonite can all include matrix lead. On day 62,the ideal treatment group M500 had a total solid lead level of 231. 97 μg / cm2,which is 1. 2 times that of M 0. Montmorillonite encourages the transformation of unstable weak acid exchangeable and carbonate-bound lead compounds into more stable organic-bound and residual lead compounds during the lead fixation process. The transformation of matrix lead into extremely low solubility basic lead carbonate and basic lead phosphate is promoted by artificial cyanobacterial biocrusts,according to characterisation. Thus,the artificial cyanobacterial biocrusts based on montmorillonite increase their fixing effect on the matrix lead and achieve the body′s detoxifying impact by lowering the bioavailability of lead. This work discloses the lead fixation mechanism of artificial cyanobacterial biocrusts and offers for the first time a novel way for treating lead polluted soil utilizing clay type artificial cyanobacterial biocrusts. Additionally,it has significant theoretical and practical implications for the practice of green water and green mountain engineering. It offers a sustainable and scientific management technique for ecological restoration in semi-arid lead poisoned mining sites.

Key words: montmorillonite,microcoleus steenstruppi,artificial cyanobacterial biocrusts,lead pollution,mine restoration