纳米零价铁物相转变对砷污染土壤稳定化效果和潜在毒性的影响

吕紫娟; 王华伟; 吴雅静; 孙英杰; 王亚楠

doi:10.13205/j.hjgc.202203005

纳米零价铁物相转变对砷污染土壤稳定化效果和潜在毒性的影响

doi: 10.13205/j.hjgc.202203005

青岛理工大学环境与市政工程学院青岛市固体废物污染控制与资源化工程研究中心, 山东青岛 266033

基金项目:

国家自然科学基金(41907111)

山东省重点研发项目(公益类)(2018GSF117030)

详细信息

作者简介:
吕紫娟(1996-),女,硕士研究生,主要研究方向为污染土壤修复。1322296161@qq.com

通讯作者:
王华伟(1984-),男,副教授,主要研究方向为固体废物污染控制与污染土壤修复技术。wanghuawei210@163.com

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出版历程
- 收稿日期: 2021-03-03
- 网络出版日期: 2022-07-07

EFFECT OF PHASE TRANSFORMATION OF NANO-ZERO-VALENT IRON ON STABILIZATION AND POTENTIAL TOXICITY OF ARSENIC IN CONTAMINATED SOIL

Qingdao Solid Waste Pollution Control and Resource Engineering Research Center, School of Environmental and Municipal Engineering, Qingdao University of Technology, Qingdao 266033, China

摘要

摘要: 为探究纳米零价铁团聚作用和氧化反应等物相转变对土壤中砷的稳定化效果和潜在毒性影响机制,选择纳米零价铁以及其可能的物相转变产物,包括微米零价铁、纳米级Fe₂O₃、微米级Fe₂O₃、纳米级Fe₃O₄等,通过室内模拟实验,研究纳米零价铁物相转变对砷污染土壤稳定化效果和潜在毒性的影响。结果表明:1)相比而言,纳米Fe⁰对土壤中砷的稳定化效率最优,当其添加量为5%时,水溶性砷含量由稳定化处理前的2.20 mg/kg降至0.11 mg/kg,稳定化效率为94.90%,同时,砷的环境风险由处理前的中等风险降至无风险;2)由浸出实验结果可知,团聚作用引起纳米零价铁向微米零价铁转变时,其对砷稳定化效率的影响并不显著(P>0.05);3)由植物毒性实验可知,纳米零价铁的团聚和氧化作用产物均会抑制油菜籽根系生长,影响种子相对根长,而对种子发芽率和种子发芽率指数无抑制作用;4)基于形态分析、植物毒性和风险分析可知,微米级Fe₂O₃和纳米级Fe₃O₄对土壤中砷的稳定化效率较低,稳定化处理后仍有一定环境风险。因此,在实际修复过程中,纳米零价铁物相转变引起土壤中砷的环境风险变化值得关注。
- 纳米零价铁 /
- 团聚氧化 /
- 砷污染 /
- 潜在毒性 /
- 环境风险
Abstract: In order to explore the effect of nano-zero-valent iron agglomeration and oxidation reaction on the stabilization effect and potential toxicity of arsenic (As) in soil, nano-zero-valent iron and its possible phase-transition products, including micro-zero-valent iron, nano-Fe₂O₃, micro-Fe₂O₃ and nano-Fe₃O₄ were selected, and the effect of phase transition of nano-zero-valent iron on the stabilization effect and potential toxicity of As-contaminated soils were studied. The results showed that:1) in comparison, nano-zero-valent iron had the best efficiency for As stabilization in the soil, and the water-soluble As content decreased from 2.20 mg/kg to 0.11 mg/kg, the stabilization efficiency was 94.90% when its addition amount was 5%. At the same time, the environmental analysis of As decreased from the medium risk to no risk level; 2) based on results of leaching experiments, it was found that the agglomeration of nano-zero valent iron to micro-zero-valent iron had no significant on the stabilization efficiency of As (P>0.05); 3) the phytotoxicity experiments indicated that the aggregation and oxidation products of nano-zero-valent iron could inhibit the growth of roots and affect the relative root length of rapeseed seeds, however, it had no inhibitory effect on relative seed germination rate and seed germination index; 4) according to morphological analysis, phytotoxicity and environmental risk analysis, we found that micro-Fe₂O₃ and nano-Fe₃O₄ had low efficiency for As stabilization in soils, certain environmental risks remained after stabilization treatment. Therefore, in the actual remediation process, the environmental risk of As induced by the phase transition of nano-zero-valent iron needs attention.
- nano-zero-valent iron /
- agglomeration oxidation /
- arsenic pollution /
- phytotoxicity /
- environmental risk

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参考文献(23)

[1]	刘辉利,梁美娜,朱义年,等.氢氧化铁对砷的吸附与沉淀机理[J].环境科学学报,2009,29(5):1011-1020.
[2]	费杨,阎秀兰,李永华,等.铁锰双金属材料在不同pH条件下对土壤As和重金属的稳定化作用[J].环境科学,2018,39(3):1430-1437.
[3]	RAI P K,LEE S S,ZHANG M,et al.Heavy metals in food crops:health risks,fate,mechanisms,and management[J].Environment International,2019,125:365-385.
[4]	GONZALEZ A,GARCÍA-GONZALO P,GIL-DIAZ M,et al. Compostassisted phytoremediation of As-polluted soil[J]. Journal of Soils and Sediments,2019,19(7):2971-2983.
[5]	费杨,阎秀兰,廖晓勇,等.铁锰双金属材料对砷和重金属复合污染土壤的稳定化研究[J].环境科学学报,2016,36(11):4164-4172.
[6]	周丽玮,王航,刘阳生.转换电极的电动力强化植物修复高浓度砷污染土壤[J].环境工程,2020,38(10):228-233.
[7]	HASEGAWA H,RAHMAN I M M,RAHMAN M A. Environmental Remediation Technologies for Metal-Contaminated Soils[M]. Springer Japan, 2016.
[8]	SUDA A,MAKINO T. Functional effects of manganese and iron oxides on the dynamics of trace elements in soils with a special focus on arsenic and cadmium:a review[J]. Geoderma,2016,270:68-75.
[9]	宋宜,王华伟,吴雅静,等.三价铁促进生物氧化锰稳定土壤砷的效果和机制[J].环境科学学报,2020,40(4):1460-1466.
[10]	GIL-DÍAZ M,RODRÍGUEZ-VALDES E,ALONSO J,et al. Nanoremediation and long-term monitoring of brownfield soil highly polluted with as and Hg[J]. Science of the Total Environment,2019,675(20):165-175.
[11]	BARAGANO D,ALONSO J,GALLEGO J R,et al. Zero valent iron and goethite nanoparticles as new promising remediation techniques for As-polluted soils[J]. Chemosphere,2020,238:124624.1-124624.10.
[12]	O'CARROLL D,SLEEP B,KROL M,et al. Nanoscale zero valent iron and bimetallic particles for contaminated site remediation[J]. Advances in Water Resources,2013,51:104-122.
[13]	高园园,周启星.纳米零价铁在污染土壤修复中的应用与展望[J].农业环境科学学报,2013,32(3):418-425.
[14]	王侠,王欣,杜艳艳,等.改性纳米零价铁对稻田土壤As污染的修复效能[J].环境科学研究,2017,30(9):1406-1414.
[15]	GIL-DÍAZ M,DIEZ-PASCUAL S,GONZÁLEZ A,et al. A nanoremediation strategy for the recovery of an As-polluted soil[J]. Chemosphere,2016,149:137-145.
[16]	ZUCCONI F,MONACO A,FORTE M,et al. Phytotoxins during the stabilization of organic matter:composting of agricultural and other wastes[J]. Plos One, 1985,9(11):112085.
[17]	EMINO E R,WARMAN P R. Biological assay for compost quality[J]. Compost Science&Utilization,2004,12(4):342-348.
[18]	TESSIER A,CAMPBELL P G,BISSON M. Sequential extraction procedure for the speciation of particulate trace metals[J]. Analytical chemistry,1979,51(7):844-851.
[19]	张塞.赣南某稀土矿区水土环境评价研究[D].北京:中国地质大学(北京),2020.
[20]	陈莉薇,陈海英,武君,等.利用Tessier五步法和改进BCR法分析铜尾矿中Cu、Pb、Zn赋存形态的对比研究[J].安全与环境学报,2020,20(2):735-740.
[21]	ADRIANO D C,WENZEL W W,VANGRONSVELD J,et al. Role of assisted natural remediation in environmental cleanup[J]. Geoderma,2004,122:121-142.
[22]	MATSUMOTO S,KASUGA J,MAKINO T,et al. Evaluation of the effects of application of iron materials on the accumulation and speciation of arsenic in rice grain grown on uncontaminated soil with relatively high levels of arsenic[J]. Environmental and Experimental Botany,2016,125:42-51.
[23]	胡一帆,王文兵,仵彦卿.弱磁场强化零价铁去除水中砷的效果[J].环境化学,2019,38(5):1074-1081.