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改性纳米零价铁修复镉污染土壤:植物根系分泌物的作用及内在机制。

Remediation of Cd-Contaminated Soil by Modified Nanoscale Zero-Valent Iron: Role of Plant Root Exudates and Inner Mechanisms.

机构信息

College of Environmental Science and Engineering, Hunan University, Changsha 410082, China.

Key Laboratory of Environmental Biology and Pollution Control, Hunan University, Ministry of Education, Changsha 410082, China.

出版信息

Int J Environ Res Public Health. 2021 May 30;18(11):5887. doi: 10.3390/ijerph18115887.

DOI:10.3390/ijerph18115887
PMID:34070880
原文链接:https://pmc.ncbi.nlm.nih.gov/articles/PMC8197846/
Abstract

In this study, the role of exogenous root exudates and microorganisms was investigated in the application of modified nanoscale zero-valent iron (nZVI) for the remediation of cadmium (Cd)-contaminated soil. In this experiment, citric acid (CA) was used to simulate root exudates, which were then added to water and soil to simulate the pore water and rhizosphere environment. In detail, the experiment in water demonstrated that low concentration of CA facilitated Cd removal by nZVI, while the high concentration achieved the opposite. Among them, CA can promote the adsorption of Cd not only by direct complexation with heavy metal ions, but also by indirect effect to promote the production of iron hydroxyl oxides which has excellent heavy metal adsorption properties. Additionally, the H dissociated from CA posed a great influence on Cd removal. The situation in soil was similar to that in water, where low concentrations of CA contributed to the immobilization of Cd by nZVI, while high concentrations promoted the desorption of Cd and the generation of CA-Cd complexes which facilitated the uptake of Cd by plants. As the reaction progressed, the soil pH and cation exchange capacity (CEC) increased, while organic matter (OM) decreased. Meanwhile, the soil microbial community structure and diversity were investigated by high-throughput sequencing after incubation with CA and nZVI. It was found that a high concentration of CA was not conducive to the growth of microorganisms, while CMC had the effect of alleviating the biological toxicity of nZVI.

摘要

在这项研究中,研究了外源根分泌物和微生物在改性纳米零价铁(nZVI)应用于修复镉(Cd)污染土壤中的作用。在本实验中,使用柠檬酸(CA)模拟根分泌物,然后将其添加到水和土壤中,以模拟孔隙水和根际环境。具体而言,水实验表明,低浓度的 CA 有利于 nZVI 去除 Cd,而高浓度则相反。其中,CA 不仅可以通过与重金属离子直接络合来促进 Cd 的吸附,还可以通过间接作用促进具有优异重金属吸附性能的铁羟基氧化物的生成。此外,CA 解离出的 H 对 Cd 的去除也有很大影响。土壤中的情况与水相似,低浓度的 CA 有助于 nZVI 固定 Cd,而高浓度则促进 Cd 的解吸和 CA-Cd 配合物的生成,从而促进 Cd 被植物吸收。随着反应的进行,土壤 pH 值和阳离子交换容量(CEC)增加,而有机质(OM)减少。同时,通过高通量测序研究了添加 CA 和 nZVI 后土壤微生物群落结构和多样性的变化。结果发现,高浓度的 CA 不利于微生物的生长,而 CMC 具有缓解 nZVI 生物毒性的作用。

https://cdn.ncbi.nlm.nih.gov/pmc/blobs/be37/8197846/c70c8bae7e47/ijerph-18-05887-g010.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/be37/8197846/1b4e2164ec4b/ijerph-18-05887-g001.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/be37/8197846/9c28d33983e0/ijerph-18-05887-g002.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/be37/8197846/803a7066afc3/ijerph-18-05887-g003.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/be37/8197846/153e3ecdefc2/ijerph-18-05887-g004.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/be37/8197846/0d2815807096/ijerph-18-05887-g005.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/be37/8197846/2b24b4d9cf08/ijerph-18-05887-g006.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/be37/8197846/1c707d6d1322/ijerph-18-05887-g007.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/be37/8197846/597689f04a3c/ijerph-18-05887-g008.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/be37/8197846/5bbfe5fb4c22/ijerph-18-05887-g009.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/be37/8197846/c70c8bae7e47/ijerph-18-05887-g010.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/be37/8197846/1b4e2164ec4b/ijerph-18-05887-g001.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/be37/8197846/9c28d33983e0/ijerph-18-05887-g002.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/be37/8197846/803a7066afc3/ijerph-18-05887-g003.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/be37/8197846/153e3ecdefc2/ijerph-18-05887-g004.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/be37/8197846/0d2815807096/ijerph-18-05887-g005.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/be37/8197846/2b24b4d9cf08/ijerph-18-05887-g006.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/be37/8197846/1c707d6d1322/ijerph-18-05887-g007.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/be37/8197846/597689f04a3c/ijerph-18-05887-g008.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/be37/8197846/5bbfe5fb4c22/ijerph-18-05887-g009.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/be37/8197846/c70c8bae7e47/ijerph-18-05887-g010.jpg

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