Soil Chemistry and Chemical Soil Quality Group, Wageningen University & Research, P.O. BOX 47, Wageningen, AA 6700, Netherlands; Agro-Environmental Protection Institute, Ministry of Agriculture of China, Tianjin 300191, China.
Department of Civil and Environmental Engineering, Shantou University, Shantou 515063, China.
Sci Total Environ. 2020 May 1;715:136957. doi: 10.1016/j.scitotenv.2020.136957. Epub 2020 Jan 27.
The by-product of the traditional Fenton reaction, colloidal arsenic-‑iron oxide, is migratable and may cause secondary environmental pollution. This paper reported a new strategy involving oxidizing and immobilizing inorganic arsenic using the Fenton reaction, and avoiding the risk of secondary contamination. Lab synthesized ferrihydrite-loaded biochar (FhBC) was developed for oxidizing and binding As(III) and As(V) in aqueous solution. Batch experiments and a series of spectrum analysis (e.g., X-ray photoelectron spectroscopy [XPS], electron paramagnetic resonance [EPR], and Fourier transform infrared spectroscopy [FTIR]) were conducted to study the oxidizing or adsorption capacity and mechanism. The maximum adsorption capacity of FhBC for As(III) and As(V) is 1.315 and 1.325 mmol/g, respectively. In addition, FhBC has an efficient oxidizing capacity within a wide pH range, which is because biochar promotes the Fenton reaction by acting as an electron donator, electron shuttler, or by providing persistent free radicals. Moreover, the adsorption mechanism was studied by FTIR spectroscopy, XPS, and X-ray diffraction (XRD). The formation of internal spherical complexes and iron oxides with a higher degree of crystallization was observed, which indicate that the products of adsorption are stable and robust in a complex environment and can exist in a highly crystallized form after adsorbing arsenic ions. Therefore, the use of FhBC as an adsorbent for arsenic represents a new strategy of using the Fenton reaction while reducing secondary contamination. These results may contribute to further mechanistic studies or extensive practical applications of FhBC.
传统芬顿反应的副产物胶体砷-氧化铁是可迁移的,可能会造成二次环境污染。本文报道了一种新策略,涉及使用芬顿反应氧化和固定无机砷,避免二次污染的风险。实验室合成的负载 FhBC 的生物炭(FhBC)被开发用于氧化和结合水溶液中的 As(III)和 As(V)。通过批量实验和一系列光谱分析(例如 X 射线光电子能谱(XPS)、电子顺磁共振(EPR)和傅里叶变换红外光谱(FTIR))研究了其氧化或吸附能力和机制。FhBC 对 As(III)和 As(V)的最大吸附容量分别为 1.315 和 1.325 mmol/g。此外,FhBC 在较宽的 pH 范围内具有高效的氧化能力,这是因为生物炭通过充当电子供体、电子穿梭体或提供持久自由基来促进芬顿反应。此外,通过傅里叶变换红外光谱(FTIR)、X 射线光电子能谱(XPS)和 X 射线衍射(XRD)研究了吸附机理。观察到形成了内球形配合物和具有更高结晶度的氧化铁,这表明吸附产物在复杂环境中是稳定和坚固的,并且在吸附砷离子后可以以高结晶形式存在。因此,使用 FhBC 作为砷的吸附剂代表了一种利用芬顿反应同时减少二次污染的新策略。这些结果可能有助于进一步研究 FhBC 的机理或广泛的实际应用。