School of Civil Engineering and Architecture, Anhui University of Technology, Maanshan, 243002, Anhui, China.
Engineering Research Center of Biomembrane Water Purification and Utilization Technology, Ministry of Education, Maanshan, 243002, Anhui, China.
Environ Sci Pollut Res Int. 2023 Jan;30(4):10697-10709. doi: 10.1007/s11356-022-22858-4. Epub 2022 Sep 9.
It is well known the capacity of potassium ferrate (Fe(VI)) for the oxidation of pollutants or co-precipitation and adsorption of hazardous species. However, little information has been paid on the adsorption and co-precipitation contribution of the Fe(VI) resultant nanoparticles, the in situ hydrolytic ferric iron oxides. Here, the removal of arsenate (As(V)) and arsenite (As(III)) by Fe(VI) was investigated, which focused on the interaction mechanisms of Fe(VI) with arsenic, especially in the contribution of the co-precipitation and adsorption of its hydrolytic ferric iron oxides. pH and Fe(VI) played significant roles on arsenic removal; over 97.8% and 98.1% of As(V) and As(III) removal were observed when Fe(VI):As(V) and Fe(VI):As(III) were 24:1 and 16:1 at pH 4, respectively. The removal of As(V) and As(III) by in situ and ex situ formed hydrolytic ferric iron oxides was examined respectively. The results revealed that As(III) was oxidized by Fe(VI) to As(V), and then was removed though co-precipitation and adsorption by the hydrolytic ferric iron oxides with the contribution content was about 1:3. For As(V), it could be removed directly by the in situ formed particles from Fe(VI) through co-precipitation and adsorption with the contribution content was about 1:1.5. By comparison, As(III) and As(V) were mainly removed through adsorption by the 30-min hydrolytic ferric iron oxides during the ex situ process. The hydrolytic ferric iron oxides size was obviously different in the process of in situ and ex situ, possessing abundant and multiple morphological structures ferric oxides, which was conducive for the efficient removal of arsenic. This study would provide a new perspective for understanding the potential of Fe(VI) treatment on arsenic control.
众所周知,高铁酸钾(Fe(VI))具有氧化污染物或共沉淀和吸附有害物种的能力。然而,对于 Fe(VI) 生成的纳米颗粒即原位水解铁氧化物的吸附和共沉淀贡献,人们知之甚少。在此,研究了高铁酸盐(Fe(VI))对砷酸盐(As(V))和亚砷酸盐(As(III))的去除,重点研究了 Fe(VI) 与砷的相互作用机制,特别是在其水解铁氧化物的共沉淀和吸附贡献方面。pH 值和 Fe(VI) 对砷的去除有显著影响;当 pH 值为 4 时,Fe(VI):As(V) 和 Fe(VI):As(III) 分别为 24:1 和 16:1 时,观察到超过 97.8%和 98.1%的 As(V)和 As(III)去除。分别考察了原位和异位形成的水解铁氧化物对 As(V)和 As(III)的去除。结果表明,As(III)被 Fe(VI)氧化为 As(V),然后通过水解铁氧化物的共沉淀和吸附去除,其贡献含量约为 1:3。对于 As(V),它可以通过 Fe(VI)原位形成的颗粒通过共沉淀和吸附去除,其贡献含量约为 1:1.5。相比之下,在异位过程中,30 分钟水解铁氧化物主要通过吸附去除 As(III)和 As(V)。在原位和异位过程中,水解铁氧化物的粒径明显不同,具有丰富多样的形态结构铁氧化物,有利于砷的有效去除。本研究为理解 Fe(VI)处理在砷控制方面的潜力提供了新的视角。