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用铁纳米颗粒回收同时被铬和多氯联苯污染的土壤。

Iron nanoparticles to recover a co-contaminated soil with Cr and PCBs.

机构信息

Dpto. Investigación Agroambiental, IMIDRA, Finca "El Encín", A-2, km 38.2, Alcalá de Henares, 28805, Madrid, Spain.

Dpto. Medio Ambiente y Agronomía, INIA-CSIC, A-6, km 7, 28040, Madrid, Spain.

出版信息

Sci Rep. 2022 Mar 3;12(1):3541. doi: 10.1038/s41598-022-07558-w.

Abstract

Little attention has been given to the development of remediation strategies for soils polluted with mixture of pollution (metal(loid)s and organic compounds). The present study evaluates the effectiveness of different types of commercial iron nanoparticles (nanoscale zero valent iron (nZVI), bimetallic nZVI-Pd, and nano-magnetite (nFeO)), for the remediation of an industrial soil co-contaminated with Cr and PCBs. Soil samples were mixed with nZVI, nZVI-Pd, or nFeO at doses selected according to their reactivity with PCBs, homogenized, saturated with water and incubated at controlled conditions for 15, 45 and 70 days. For each sampling time, PCBs and chromium were analyzed in aqueous and soil fractions. Cr(VI) and Cr leachability (TCLP test) were determined in the soil samples. The treatment with the three types of iron nanoparticles showed significant reduction in Cr concentration in aqueous extracts at the three sampling times (> 98%), compared to the control samples. The leachability of Cr in treated soil samples also decreased and was stable throughout the experiment. Results suggested that nZVI and nZVI-Pd immobilized Cr through adsorption of Cr(VI) on the shell and reduction to Cr(III). The mechanism of interaction of nFeO and Cr(VI) included adsorption and reduction although its reducing character was lower than those of ZVI nanoparticles. PCBs significantly decreased in soil samples (up to 68%), after 15 days of treatment with the three types of nanoparticles. However, nFeO evidenced reversible adsorption of PCBs after 45 days. In general, nZVI-Pd reduced PCB concentration in soil faster than nZVI. Control soils showed a similar reduction in PCBs concentration as those obtained with nZVI and nZVI-Pd after a longer time (45 days). This is likely due to natural bioremediation, although it was not effective for Cr remediation. Results suggest that the addition of nZVI or nZVI-Pd and pseudo-anaerobic conditions could be used for the recovery of soil co-contaminated with Cr and PCBs.

摘要

人们很少关注同时受到金属(类)和有机化合物污染的土壤的修复策略的发展。本研究评估了不同类型的商业铁纳米粒子(纳米零价铁(nZVI)、双金属 nZVI-Pd 和纳米磁铁矿(nFeO))对同时受到 Cr 和 PCB 污染的工业土壤的修复效果。将土壤样品与 nZVI、nZVI-Pd 或 nFeO 混合,剂量根据它们与 PCB 的反应性选择,均匀混合,饱和水后在控制条件下孵育 15、45 和 70 天。对于每个采样时间,都分析水相和土壤相中的 PCB 和铬。测定土壤样品中的 Cr(VI)和 Cr 浸出性(TCLP 测试)。与对照样品相比,三种类型的铁纳米粒子处理在三个采样时间都显著降低了水相提取物中的 Cr 浓度(>98%)。处理后土壤样品中 Cr 的浸出率也降低,并在整个实验过程中保持稳定。结果表明,nZVI 和 nZVI-Pd 通过 Cr(VI)在壳上的吸附和还原为 Cr(III)来固定 Cr。nFeO 与 Cr(VI)的相互作用机制包括吸附和还原,尽管其还原特性低于 ZVI 纳米粒子。三种类型的纳米粒子处理后 15 天,土壤样品中的 PCB 显著降低(高达 68%)。然而,nFeO 在 45 天后表现出对 PCB 的可逆吸附。一般来说,nZVI-Pd 比 nZVI 更快地降低土壤中 PCB 的浓度。对照土壤在较长时间(45 天)后获得与 nZVI 和 nZVI-Pd 相似的 PCB 浓度降低,这可能是由于自然生物修复的原因,尽管它对 Cr 的修复没有效果。结果表明,添加 nZVI 或 nZVI-Pd 和准厌氧条件可用于回收同时受到 Cr 和 PCB 污染的土壤。

https://cdn.ncbi.nlm.nih.gov/pmc/blobs/a2c9/8894337/6a69eae71042/41598_2022_7558_Fig1_HTML.jpg

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