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不同植物模式对铅锌矿渣修复的根际效应

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[目的]研究不同植物种植模式下根系效应在重金属修复中的效果,为矿山修复奠定理论基础.[方法]构建了基于改良剂的铅锌矿植物修复中试系统,设计CK组(纯矿渣对照)、S0 组(改良矿渣对照),比较单一植物系统S栾(单一乔木栾树)、S夹(单一灌木夹竹桃)、S香(单一草本香根草)、S复(乔灌草复合)的铅锌矿修复效果.[结果]1)试验后,植物组与原矿渣对照组相比pH值提高了 0.14~0.27,含水率、孔隙度、有机质、阳离子交换量分别提高了 5.3%~9.8%、9.6%~11.8%、102.5%~106.9%、54.2%~66.6%;蔗糖酶、脲酶活性分别提升了 130.9%~680.2%、2.4%~8.6%;总氮、总磷、总钾含量分别提升了 85.5%~115.6%、0.0%~22.5%、0.9%~10.5%.2)改良剂显著降低了系统中Zn流失量(P<0.05);植物种植显著降低了Zn、Pb流失量(P<0.05),其中,S复处理中Pb、Zn流失量最低;相比S0,S植物组中重金属Pb、Zn酸可提取态、可还原态组分含量均下降,S栾、S夹、S香、S复残渣态Pb分别提升了 6.5%、5.4%、11.8%、6.4%,残渣态Zn分别提升了 4.0%、3.4%、7.9%、2.1%.3)不同组别间细菌门水平差异不大,主要优势菌种有变形菌门Proteobacteria、拟杆菌门Bacteroidota、酸杆菌门Acidobacteriota等.门水平下主要优势真菌包括子囊菌门Ascomycota、担子菌门Basidiomycota、接合菌门Zygomycota等.[结论]改良剂改善了矿渣的土壤结构,提升了矿渣的土壤肥力,为植物生长提供了有利条件.改良剂和植物种植改变了土壤Pb、Zn的赋存形态,残渣态含量升高,S复重金属流失量最低.植物种植模式对细菌、真菌物种丰度存在影响,改良剂的添加降低了基质中真菌的物种丰富度,而植物的生长又在一定程度上提升了真菌的物种丰富度.
Rhizosphere effect of different plant patterns on lead-zinc slag remediation
[Objective]The effect of root effect under different plant planting modes in heavy metal remediation was studied,which laid a theoretical foundation for mine remediation.[Method]An observer-based phytoremediation pilot system of lead-zinc ore was constructed,and the CK group(pure slag control)and S0 group(modified slag control)were designed to compare the lead-zinc ore restoration effects of single plant system SLuan(a single tree koelreuteria),SJia(a single shrub oleander),SXiang(a single herb vetiver),and SFu(compound of trees,shrubs and herbs).[Result](1)After the experiment,compared with the original slag control group,the pH of the plant group was increased by 0.14-0.27,and the water content,porosity,organic matter and cation exchange capacity were increased by 5.3%-9.8%,9.8%-11.8%,102.5%-106.9%and 54.2%-66.6%,respectively.The activity of sucrase and urease increased by 130.9%-680.2%and 2.4%-8.6%,respectively.The contents of total nitrogen,total phosphorus and total potassium were increased by 85.5%-115.6%,0.0%-22.5%and 0.9%-10.5%,respectively.(2)The modifier significantly reduced the amount of Zn loss in the system(P<0.05).Plant planting significantly decreased the loss of Zn and Pb(P<0.05),and the loss of Pb and Zn was the lowest under the combination of tree,shrub and grass.Compared with the modified slag control group,the extractable and reducible contents of heavy metal Pb and Zn acid in the plant group were decreased,and the residual Pb in the single tree,single shrub,single herb and shrub compound groups was increased by 6.5%,5.4%,11.8%and 6.4%,respectively.Residual Zn increased by 4.0%,3.4%,7.9%and 2.1%,respectively.(3)There was little difference in the level of bacterobacteria among different groups.The main dominant bacteria were Proteobacteria,Bacteroidota,Acidobacteriota and so on.At the phylum level,the dominant fungi included Ascomycota,Basidiomycota,Zygomycota,etc.[Conclusion]The addition of amendments improved the soil structure and fertility of the original slag.Amendments and plant planting changed the occurrence forms of Pb and Zn in soil,the residue content was increased.The species abundance of bacteria and fungi was affected by plant planting patterns.The addition of amendments decreased the species richness of fungi in the substrate,while the growth of plants increased the species richness to some extent.

phytoremediationlead-zinc tailingssoil amendmentmicrobial diversityinterroot effect

王玉竹、陈永华、杜露、付新喜、谭锋、柳俊

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中南林业科技大学 环境科学与工程学院,湖南 长沙 410004

植物修复 铅锌尾矿 土壤改良剂 微生物多样性 根际效应

湖南省环保科研项目湖南省教育厅科研项目

HBKT-202102920B595

2024

中南林业科技大学学报
中南林业科技大学

中南林业科技大学学报

CSTPCD北大核心
影响因子:1.442
ISSN:1673-923X
年,卷(期):2024.44(1)
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