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生物炭衍生溶解有机物的释放特性及其对Cr(Ⅵ)吸附和还原的影响。

Release characteristics of biochar-derived dissolved organic matter and its impact on Cr(vi) adsorption and reduction.

作者信息

Liu Hui, Wang Ying, Wang Shixu, Wu Jing, Wang Yulai

机构信息

School of Energy and Environment, Anhui University of Technology Maanshan City 243002 China

出版信息

RSC Adv. 2024 Dec 2;14(51):38171-38182. doi: 10.1039/d4ra06172a. eCollection 2024 Nov 25.

Abstract

Biochar has received widespread attention as a promising amendment for heavy metal stabilization due to its abundant porosity and surface functional groups. However, the role of biochar-derived dissolved organic matter (BDOM) is usually overlooked. In this study, we systematically investigated the leaching dynamics of BDOM from garden wastes through hydrothermal carbonization (HC), pyrolysis (PC) and hydro/pyrolysis (HPC) and explored their impacts on Cr(vi) environmental behavior in an extremely acidic environment. Results showed that BDOM leaching dynamics followed the first order model, and HC leached more BDOM than PC and HPC, especially for Ar-P, SMP and Ha-L fractions. Although carbonized using various methods, the biochars displayed a similar adsorption capacity for Cr(vi) at an environmental-related concentration of 2 mg L. The presence of BDOM accelerated the Cr(vi) adsorption rate on biochars due to their pre-complexing. Simultaneously, HC-BDOM acted as an electron donor and participate in Cr(vi) reduction directly, resulting in the synchronous reduction of Cr(vi) during its adsorption process. However, PC- and HPC-BDOM preferentially acted as electron acceptors, thus competing with Cr(vi) for Fe(ii) oxidation and decreased the Cr(vi) reduction rate. This study suggested that biochar from garden wastes has a great remediation potential for Cr-contaminated land and that BDOM (especially HC-BDOM) plays a significant role in increasing soil organic matter, stabilizing heavy metals and detoxifying toxic substances by oxidation-reduction.

摘要

生物炭因其丰富的孔隙率和表面官能团,作为一种有前景的重金属稳定剂受到广泛关注。然而,生物炭衍生的溶解有机物(BDOM)的作用通常被忽视。在本研究中,我们系统地研究了通过水热碳化(HC)、热解(PC)和水热/热解(HPC)从园林废弃物中浸出BDOM的动力学,并探讨了它们在极端酸性环境中对Cr(VI)环境行为的影响。结果表明,BDOM浸出动力学遵循一级模型,且HC浸出的BDOM比PC和HPC更多,尤其是对于Ar-P、SMP和Ha-L组分。尽管采用不同方法碳化,但在环境相关浓度2 mg L时,生物炭对Cr(VI)表现出相似的吸附容量。BDOM的存在由于其预络合作用加速了生物炭对Cr(VI)的吸附速率。同时,HC-BDOM作为电子供体直接参与Cr(VI)的还原,导致其在吸附过程中Cr(VI)同步还原。然而,PC-和HPC-BDOM优先作为电子受体,从而与Cr(VI)竞争Fe(II)氧化,降低了Cr(VI)的还原速率。本研究表明,园林废弃物生物炭对Cr污染土地具有巨大的修复潜力,且BDOM(尤其是HC-BDOM)在增加土壤有机质、稳定重金属以及通过氧化还原解毒有害物质方面发挥着重要作用。

https://cdn.ncbi.nlm.nih.gov/pmc/blobs/8282/11610041/9ef235f60906/d4ra06172a-f1.jpg

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