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纳米零价铁与生物炭或腐殖酸联合修复六价铬污染土壤及其对植物生长的影响

Remediation of Cr(VI)-Contaminated Soil by Nano-Zero-Valent Iron in Combination with Biochar or Humic Acid and the Consequences for Plant Performance.

作者信息

Sun Yuhuan, Zheng Fangyuan, Wang Wenjie, Zhang Shuwu, Wang Fayuan

机构信息

College of Environment and Safety Engineering, Qingdao University of Science and Technology, Qingdao 266042, China.

Key Laboratory of Soil Resources and Environment in Qianbei of Guizhou Province, Zunyi Normal University, Zunyi 563002, China.

出版信息

Toxics. 2020 Apr 3;8(2):26. doi: 10.3390/toxics8020026.

Abstract

Nano-scale zero-valent iron (nZVI) is among the most common nanoparticles widely used for the treatment of various environmental contaminants. However, little is known about the combined effects of nano-zero-valent iron (nZVI) and other soil amendments on soil remediation and plant performance. For the first time, we studied the remediation of Cr(VI)-contaminated soil using bare nZVI (B-nZVI) and starch-supported nZVI (S-nZVI) in combination with either biochar (BC) or humic acid (HA), and the consequent effects on plant growth and Cr accumulation. Both S-nZVI and B-nZVI decreased the contents of Cr(VI) and available Cr in soil, but increased available Fe content, with S-nZVI generally showing more pronounced effects at a higher dose (1000 mg/kg). B-nZVI exerted no inhibition and even stimulation on plant growth, but 1000 mg/kg S-nZVI produced significant phytotoxicity, resulting in decreased plant growth, low chlorophyll content in leaves, and excessive accumulation of Fe in roots. Each nZVI decreased shoot and root Cr concentrations. BC and HA produced synergistic effects with nZVI on Cr(VI) removal from soil, but HA decreased soil pH and increased the availability of Cr and Fe, implying a potential environmental risk. Addition of BC or HA did not alter the effects of either nZVI on plant growth. In conclusion, combined application of 100 mg/kg nZVI and BC could be an ideal strategy for the remediation of soil contaminated with Cr(VI), whereas high-dose S-nZVI and HA are not recommended in the remediation of agricultural soils for crop production or in the phytostabilization of Cr(VI).

摘要

纳米零价铁(nZVI)是广泛用于处理各种环境污染物的最常见纳米颗粒之一。然而,关于纳米零价铁(nZVI)与其他土壤改良剂对土壤修复和植物生长性能的联合作用知之甚少。我们首次研究了使用裸纳米零价铁(B-nZVI)和淀粉负载纳米零价铁(S-nZVI)结合生物炭(BC)或腐殖酸(HA)对六价铬污染土壤的修复作用,以及对植物生长和铬积累的后续影响。S-nZVI和B-nZVI均降低了土壤中六价铬和有效铬的含量,但增加了有效铁含量,在较高剂量(1000 mg/kg)下,S-nZVI的效果通常更显著。B-nZVI对植物生长没有抑制作用,甚至有促进作用,但1000 mg/kg的S-nZVI产生了显著的植物毒性,导致植物生长下降、叶片叶绿素含量降低以及根部铁过量积累。每种纳米零价铁都降低了地上部和根部的铬浓度。生物炭和腐殖酸与纳米零价铁在从土壤中去除六价铬方面产生了协同作用,但腐殖酸降低了土壤pH值并增加了铬和铁的有效性,这意味着潜在的环境风险。添加生物炭或腐殖酸并没有改变纳米零价铁对植物生长的影响。总之,联合施用100 mg/kg纳米零价铁和生物炭可能是修复六价铬污染土壤的理想策略,而在农业土壤修复用于作物生产或六价铬的植物稳定化中,不建议使用高剂量的S-nZVI和腐殖酸。

https://cdn.ncbi.nlm.nih.gov/pmc/blobs/b6b9/7357137/55419a08c3b7/toxics-08-00026-g001.jpg

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