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通过共热解利用生物浸出的纳米零价铁介导生物炭从水和土壤中去除铬的机制

Mechanisms of Chromium Removal from Water and Soil Using Bioleached Nano Zero-Valent Iron-Mediated Biochar via Co-Pyrolysis.

作者信息

Liu Zhiyi, Zhou Shuhong, Cai Yubing, Zhang Xuehai, Shaaban Muhammad, Peng Qi-An, Cai Yajun

机构信息

School of Resources and Environment, Wuhan Textile University, Wuhan 430200, China.

China National Grain Reserve Management Group Corporation Anhui Branch Lu'an Depot, Lu'an 237000, China.

出版信息

Nanomaterials (Basel). 2024 Nov 26;14(23):1895. doi: 10.3390/nano14231895.

Abstract

Biological charcoal loaded with nano zero-valent iron (nZVI@BC) was synthesized using the bioleaching co-pyrolysis method. This study analyzed the formulation sequence of nZVI@BC and its influence on chromium elimination from water and soil, along with the involved mechanisms. The bioleaching method facilitated ionic iron incorporation onto biochar in the form of yellow potassium ferroalum compounds, which were reduced to Fe by H, CO, and CH generated during biomass co-pyrolysis. In aqueous conditions, the removal capacity of Cr(VI) by nZVI@BC increased by 72.01% and 66.92% compared to biochar (BC) and biochar-bioleachate composite (BBC), respectively. Under optimal conditions, nZVI@BC eliminated 90.11% of 20 mg/L Cr(VI), with experimental data fitting the Freundlich and pseudo-second-order kinetic models. The nZVI@BC also showed a passivation effect on chromium in soil; after 45 days, the exchangeable state of chromium was reduced by 12.89%, while the residual state increased by 10.45%. This enhancement in chromium elimination from soil was evident, as the residual state increased more for nZVI@BC (10.45%) than for BC alone (9.67% and 8.48%). Soil physicochemical properties and microbial community abundance improved as well. Cr(VI) removal mechanisms involved adsorption, reduction, and co-precipitation in water, while soil mechanisms included surface adsorption, electrostatic attraction, ion exchange, and complexation. The synthesis of nZVI@BC offers a novel method for creating iron-modified materials to effectively remove Cr(VI).

摘要

采用生物浸出共热解法合成了负载纳米零价铁的生物炭(nZVI@BC)。本研究分析了nZVI@BC的配方顺序及其对水和土壤中铬去除的影响,以及相关机制。生物浸出法促进了离子铁以黄钾铁矾化合物的形式掺入生物炭中,这些化合物在生物质共热解过程中被H、CO和CH还原为Fe。在水相条件下,nZVI@BC对Cr(VI)的去除能力分别比生物炭(BC)和生物炭-生物浸出液复合物(BBC)提高了72.01%和66.92%。在最佳条件下,nZVI@BC去除了20 mg/L Cr(VI)中的90.11%,实验数据符合Freundlich和准二级动力学模型。nZVI@BC对土壤中的铬也有钝化作用;45天后,铬的可交换态减少了12.89%,而残留态增加了10.45%。nZVI@BC对土壤中铬去除的增强作用明显,因为其残留态的增加(10.45%)比单独的BC(9.67%和8.48%)更多。土壤理化性质和微生物群落丰度也得到了改善。水中Cr(VI)的去除机制包括吸附、还原和共沉淀,而土壤机制包括表面吸附、静电吸引、离子交换和络合。nZVI@BC的合成提供了一种制备铁改性材料以有效去除Cr(VI)的新方法。

https://cdn.ncbi.nlm.nih.gov/pmc/blobs/d179/11643807/d37df58258c9/nanomaterials-14-01895-g001.jpg

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