A Fenton-like system of biochar loading Fe–Al layered double hydroxides (FeAl-LDH@BC) / H2O2 for phenol removal

化学 苯酚 烧焦 核化学 傅里叶变换红外光谱 氢氧化物 生物炭 电子顺磁共振 过氧化氢 无机化学 催化作用 2,4-二氯苯酚 热解 化学工程 有机化学 物理 核磁共振 生物 细菌 工程类 遗传学
作者
Xiaoliang Fan,Qingqing Cao,Fanyue Meng,Bing Song,Zhongqiang Bai,Yan Zhao,Dandan Chen,Yan Zhou,Min Song
出处
期刊:Chemosphere [Elsevier BV]
卷期号:266: 128992-128992 被引量:67
标识
DOI:10.1016/j.chemosphere.2020.128992
摘要

FeAl-layered double hydroxide (FeAl-LDH) supported by char was synthesized using the hydrothermal method in order to activate hydrogen peroxide (H2O2) to degrade phenol. The effects of char type, char synthesis amount, and several important parameters on the degradation were investigated. In addition, the physicochemical properties of [email protected] were revealed by instruments including the transmission electron microscope (TEM), X–ray diffraction (XRD), and Fourier–transform infrared (FT–IR). The results showed that the degradation efficiency of phenol (80 mg/L) by [email protected]0.25 was 85.28% at a pH of 3 and H2O2 concentration of 400 mg/L, and exhibited good reusability with a small amount of iron leaching. Electron paramagnetic resonance (EPR) and radical quenching results indicated that ·OH radicals were the main participant during the degradation process, and XRD and FTIR spectra showed that FeAl-LDH was dissolved and rebuilt during the degradation process, and a small amount of iron was leached out resulting in the homogeneous catalysis. Hence, both homogeneous and heterogeneous processes occurred in the phenol oxidation process. Further soil remediation experiments showed that [email protected]0.25 could also effectively degrade phenol in soil, although the efficiency was lower than that in solution.
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