School of Environmental Science and Engineering, Huazhong University of Science and Technology, Wuhan 430074, PR China.
School of Environmental Science and Engineering, Huazhong University of Science and Technology, Wuhan 430074, PR China; Institute of Energy and Environment, Inner Mongolia University of Science and Technology, Baotou 014010, PR China.
Sci Total Environ. 2020 Dec 20;749:142086. doi: 10.1016/j.scitotenv.2020.142086. Epub 2020 Aug 31.
In this study, biochar R550, obtained from rice husk charred at 550 °C, was used to detoxify Cr(VI) and organic pollutant p-nitrophenol (PNP) with the cooperation of sulfite, simultaneously. Cr(VI) was mainly reduced by sulfite, and the reduction was accelerated by biochar. Also, the reactive oxygen species formed in-situ as a result of enhanced oxidation of sulfite with Cr(VI)/R550 system and the activation of O by R550, led to the degradation of PNP. Production of the radicals viz., SO, SO and OH was followed by Electron Paramagnetic Resonance (EPR) study, and the predominant role of SO towards PNP degradation was confirmed by radical quenching tests. The reaction completed biochar sample was undergone the X-ray photoelectron spectroscopy (XPS) and Fourier Transform Infrared Spectroscopy (FTIR) spectral analysis, which suggested that the carboxyl group of the biochar triggered and enhanced the reactivity of Cr(VI) via coordination linkage, which in turn activated the sulfite and converted the SO into SO to a higher extent by overcoming the undesirable transformation of SO to SO. Such results could also be verified by the other three biochar (Oxi-R550, H-R550, and R800). The results of the present study shed light on the mechanism of biochar mediated sulfite activation process by Cr(VI) and also assured the viability and green approach of the technique in detoxifying the industrial effluents containing Cr(VI) and organic pollutants.
在这项研究中,稻壳在 550°C 下碳化得到的生物炭 R550 被用于同时协同亚硫酸盐来解毒六价铬(Cr(VI))和有机污染物对硝基苯酚(PNP)。Cr(VI)主要通过亚硫酸盐还原,而生物炭加速了还原过程。此外,由于 Cr(VI)/R550 体系中增强的亚硫酸盐氧化和 R550 对 O 的活化,原位形成的活性氧物种导致 PNP 的降解。自由基(如 SO、SO 和 OH)的产生通过电子顺磁共振(EPR)研究得到证实,自由基猝灭实验证实了 SO 在 PNP 降解中的主要作用。反应完成后的生物炭样品进行了 X 射线光电子能谱(XPS)和傅里叶变换红外光谱(FTIR)光谱分析,结果表明生物炭的羧基基团通过配位键触发和增强了 Cr(VI)的反应性,从而进一步激活亚硫酸盐,并将 SO 转化为 SO,从而克服 SO 向 SO 的不利转化,达到更高的程度。其他三种生物炭(Oxi-R550、H-R550 和 R800)的结果也验证了这一点。本研究结果揭示了 Cr(VI)介导的生物炭激活亚硫酸盐过程的机制,也保证了该技术在解毒含 Cr(VI)和有机污染物的工业废水中的可行性和绿色方法。