Wang Xue, Zhang Peng, Wu Meixuan, He Ting, Li Can, Liu Lijuan, Li Shunling, Chang Zhaofeng, Lang Di, Du Wei, Li Hao, Pan Bo
Yunnan Provincial Key Laboratory of Soil Carbon Sequestration and Pollution Control, Faculty of Environmental Science & Engineering, Kunming University of Science & Technology, Kunming, 650500, China.
Yunnan Provincial Key Laboratory of Soil Carbon Sequestration and Pollution Control, Faculty of Environmental Science & Engineering, Kunming University of Science & Technology, Kunming, 650500, China.
Chemosphere. 2023 Dec;343:140245. doi: 10.1016/j.chemosphere.2023.140245. Epub 2023 Sep 20.
Due to large specific surface area, abundant surface functional groups, and stable chemical structure, biochar has been widely used in many environmental fields, including the remediation of Cr pollution. Alternatively, electrochemically active organic matter (e-OM), which is prevalent in both natural environments and industrial wastewater, exerts an inevitable influence on the mechanisms underlying Cr(VI) removal by biochar. The synergistic interplay between biochar and e-OM in the context of Cr(VI) remediation remains to be fully elucidated. In this study, disodium anthraquinone-2,6-disulfonate (AQDS) was used as a model for e-OM, characterized by its quinone group's ability to either donate or accept electrons. We found that AQDS sped up the Cr(VI) removal process, but the enhancement effect decreased with the increase in pyrolysis temperature. With the addition of AQDS, the removal amount of Cr(VI) by BC300 and BC600 increased by 160.0% and 49.5%, respectively. AQDS could release more electrons trapped in the lower temperature biochar samples (BC300 and BC600) for Cr(VI) reduction. However, AQDS inhibited the Cr(VI) removal by BC900 due to the adsorption of AQDS on biochar surface. In the presence of the small molecule carbon source lactate, more AQDS was adsorbed onto the biochar surface. This led to an inhibition of the electron transfer between biochar and Cr(VI), resulting in an inhibitory effect. This study has elucidated the electron transfer mechanism involved in the removal of Cr(VI) by biochar, particularly in conjunction with e-OM. Furthermore, it would augment the efficacy of biochar in applications targeting the removal of heavy metals.
由于具有较大的比表面积、丰富的表面官能团和稳定的化学结构,生物炭已被广泛应用于许多环境领域,包括铬污染的修复。另外,电化学活性有机物(e-OM)在自然环境和工业废水中普遍存在,对生物炭去除Cr(VI)的潜在机制产生了不可避免的影响。生物炭与e-OM在Cr(VI)修复方面的协同相互作用仍有待充分阐明。在本研究中,蒽醌-2,6-二磺酸钠(AQDS)被用作e-OM的模型,其特征在于醌基团具有供电子或接受电子的能力。我们发现AQDS加速了Cr(VI)的去除过程,但随着热解温度的升高,增强效果降低。添加AQDS后,BC300和BC600对Cr(VI)的去除量分别增加了160.0%和49.5%。AQDS可以释放被困在较低温度生物炭样品(BC300和BC600)中的更多电子,用于还原Cr(VI)。然而,由于AQDS吸附在生物炭表面,它抑制了BC900对Cr(VI)的去除。在小分子碳源乳酸存在的情况下,更多的AQDS吸附到生物炭表面。这导致生物炭与Cr(VI)之间的电子转移受到抑制,从而产生抑制作用。本研究阐明了生物炭去除Cr(VI)所涉及的电子转移机制,特别是与e-OM结合时的机制。此外,它将提高生物炭在去除重金属应用中的功效。