Institute of Environment and Sustainable Development in Agriculture, Chinese Academy of Agricultural Sciences, Beijing, 100081, China.
College of Environment and Safety, Taiyuan University of Science and Technology, Taiyuan, Shanxi, 030024, China.
Sci Rep. 2017 Jan 18;7:40765. doi: 10.1038/srep40765.
Hydrous ferric oxide (HFO) is most effective with high treatment capacity on arsenate [As(V)] sorption although its transformation and aggregation nature need further improvement. Here, HFO nanoparticles with carboxymethyl cellulose (CMC) or starch as modifier was synthesized for the purpose of stability improvement and As(V) removal from water. Comparatively, CMC might be the optimum stabilizer for HFO nanoparticles because of more effective physical and chemical stability. The large-pore structure, high surface specific area, and the non-aggregated nature of CMC-HFO lead to increased adsorption sites, and thus high adsorption capacities of As(V) without pre-treatment (355 mg·g), which is much greater than those reported in previous studies. Second-order equation and dual-mode isotherm model could be successfully used to interpret the sorption kinetics and isotherms of As(V), respectively. FTIR, XPS and XRD analyses suggested that precipitation and surface complexation were primary mechanisms for As(V) removal by CMC modified HFO nanoparticles. A surface complexation model (SCM) was used to simulate As adsorption over pH 2.5-10.4. The predominant adsorbed arsenate species were modeled as bidentate binuclear surface complexes at low pH and as monodentate complexes at high pH. The immobilized arsenic remained stable when aging for 270 d at room temperature.
水合氧化铁(HFO)在吸附砷酸盐[As(V)]方面具有较高的处理容量,效果最佳,尽管其转化和聚集性质需要进一步改善。在这里,我们合成了以羧甲基纤维素(CMC)或淀粉为修饰剂的 HFO 纳米颗粒,以提高其稳定性并去除水中的 As(V)。相比之下,由于具有更有效的物理和化学稳定性,CMC 可能是 HFO 纳米颗粒的最佳稳定剂。CMC-HFO 的大孔结构、高比表面积和非聚集性质导致吸附位点增加,因此无需预处理即可实现高的 As(V)吸附容量(355mg·g),这远高于以前研究中的报道。二阶方程和双模式等温线模型可分别成功用于解释 As(V)的吸附动力学和等温线。FTIR、XPS 和 XRD 分析表明,沉淀和表面络合是 CMC 修饰的 HFO 纳米颗粒去除 As(V)的主要机制。表面络合模型(SCM)用于模拟 pH 2.5-10.4 范围内的砷吸附。在室温下老化 270 天后,固定化砷仍保持稳定。