Zhang Jinlan, Xie Lihong, Ma Qiyan, Liu Yiyang, Li Jie, Li Zhifeng, Li Shangyi, Zhang Tingting
Department of Environmental Science and Engineering, College of Chemical Engineering, Beijing University of Chemical Technology, Beijing 100029, China.
Department of Environmental Science and Engineering, College of Chemical Engineering, Beijing University of Chemical Technology, Beijing 100029, China.
Chemosphere. 2023 Jan;311(Pt 2):137174. doi: 10.1016/j.chemosphere.2022.137174. Epub 2022 Nov 8.
Zero-valent iron biochar composites (ZVI/BC) have been widely used to remove Cr(VI) from water. However, the application of ZVI/BC prepared by the carbothermal reduction was limited by the non-uniform dispersion of ZVI on the biochar surface. In this work, ball milling technique was introduced to modify ZVI/BC. Results showed that after ball milling, the maximum Langmuir adsorption capacity for Cr(VI) was 117.7 mg g (298 K) which was 2.08 times higher than ZVI/BC. The initial adsorption rate of the Elovich model increased from 4.57 × 10 mg g min to 3.74 × 10 mg g min after ball milling. Dispersibility of ZVI on biochar surface and contact between ZVI and biochar were improved by the ball milling, thus accelerating the electron transfer. Besides, ball milling increased the content of oxygen-containing functional groups in biochar, contributing to the chemisorption of Cr(VI). The response sequence of oxygen-containing functional groups was analyzed by two-dimensional correlation spectroscopy, indicating that Cr(VI) preferentially complexed with phenolic -OH. Shielding experiments showed that Fe (0) was the dominant reducing species with a contribution of 73.4%, followed by surface-bound Fe(II) (21.3%) and dissolved Fe (5.24%). Density functional theory calculations demonstrated that ball milled ZVI/BC improved the adsorption affinity and electron transfer flux towards Cr(VI) by introducing phenolic -OH and Fe (0). Combining all the textural characterization, the Cr(VI) removal mechanism of the ball milled ZVI/BC could be proposed as adsorption, reduction, and precipitation. Eventually, stable Cr-Fe oxides (FeOCrO and CrFeO) were formed. This work not only provides a simple method to modify ZVI/BC to remove Cr(VI) in water efficiently and rapidly, but also improves the mechanistic insight into the Cr(VI) removal by iron-carbon composites via the response sequence of functional group analysis and the quantitative analysis of reducing species.
零价铁生物炭复合材料(ZVI/BC)已被广泛用于去除水中的Cr(VI)。然而,通过碳热还原制备的ZVI/BC的应用受到ZVI在生物炭表面分散不均匀的限制。在这项工作中,引入了球磨技术来改性ZVI/BC。结果表明,球磨后,Cr(VI)的最大Langmuir吸附容量为117.7 mg g(298 K),比ZVI/BC高2.08倍。球磨后,Elovich模型的初始吸附速率从4.57×10 mg g min提高到3.74×10 mg g min。球磨改善了ZVI在生物炭表面的分散性以及ZVI与生物炭之间的接触,从而加速了电子转移。此外,球磨增加了生物炭中含氧官能团的含量,有助于Cr(VI)的化学吸附。通过二维相关光谱分析了含氧官能团的响应顺序,表明Cr(VI)优先与酚羟基络合。屏蔽实验表明,Fe(0)是主要的还原物种,贡献为73.4%,其次是表面结合的Fe(II)(21.3%)和溶解态Fe(5.24%)。密度泛函理论计算表明,球磨后的ZVI/BC通过引入酚羟基和Fe(0)提高了对Cr(VI)的吸附亲和力和电子转移通量。综合所有结构表征,可提出球磨后ZVI/BC去除Cr(VI)的机制为吸附、还原和沉淀。最终形成了稳定的Cr-Fe氧化物(FeOCrO和CrFeO)。这项工作不仅提供了一种简单的方法来改性ZVI/BC以高效快速地去除水中的Cr(VI),还通过官能团分析的响应顺序和还原物种的定量分析,提高了对铁碳复合材料去除Cr(VI)机制的认识。