Kwon Oh-Hun, Kim Jong-Oh, Cho Dong-Wan, Kumar Rahul, Baek Seung Han, Kurade Mayur B, Jeon Byong-Hun
Department of Natural Resources and Environmental Engineering, Hanyang University, 222 Wangsimni-ro, Seongdong-gu, Seoul 133-791, South Korea.
Department of Civil and Environmental Engineering, Hanyang University, 222 Wangsimni-ro, Seongdong-gu, Seoul 133-791, South Korea.
Chemosphere. 2016 Oct;160:126-33. doi: 10.1016/j.chemosphere.2016.06.074. Epub 2016 Jun 30.
A composite adsorbent to remove arsenite [As(III)], arsenate [As(V)], and copper [Cu(II)] from aqueous phase was synthesized by immobilizing zirconium oxide on alginate beads (ZOAB). The composition (wt%) of ZOAB (Zr-34.0; O-32.7; C-21.3; Ca-1.0) was confirmed by energy dispersive X-ray (EDX) analysis. Sorption studies were conducted on single and binary sorbate systems, and the effects of contact time, initial adsorbate concentration, and pH on the adsorption performance of ZOAB (pHPZC = 4.3) were monitored. The sorption process for As(III)/As(V) and Cu(II) reached an equilibrium state within 240 h and 24 h, respectively, with maximum sorption capacities of 32.3, 28.5, and 69.9 mg g(-1), respectively. The addition of Cu(II) was favorable for As(V) sorption in contrast to As(III). In the presence of 48.6 mg L(-1) Cu(II), the sorption capacity of As(V) increased from 1.5 to 3.8 mg g(-1) after 240 h. The sorption data for As(III)/As(V) and Cu(II) conformed the Freundlich and Langmuir isotherm models, respectively. The adsorption of As(III), As(V), and Cu(II) followed pseudo second order kinetics. The effect of arsenic species on Cu(II) sorption was insignificant. The results of present study demonstrated that the synthesized sorbent could be useful for the simultaneous removal of both anionic and cationic contaminants from wastewaters.
通过将氧化锆固定在海藻酸钠珠粒(ZOAB)上,合成了一种用于从水相中去除亚砷酸盐[As(III)]、砷酸盐[As(V)]和铜[Cu(II)]的复合吸附剂。通过能量色散X射线(EDX)分析确定了ZOAB的组成(重量百分比)(Zr-34.0;O-32.7;C-21.3;Ca-1.0)。对单一和二元吸附质体系进行了吸附研究,并监测了接触时间、初始吸附质浓度和pH对ZOAB(零电荷点pH = 4.3)吸附性能的影响。As(III)/As(V)和Cu(II)的吸附过程分别在240小时和24小时内达到平衡状态,最大吸附容量分别为32.3、28.5和69.9 mg g(-1)。与As(III)相比,Cu(II)的添加有利于As(V)的吸附。在存在48.6 mg L(-1) Cu(II)的情况下,240小时后As(V)的吸附容量从1.5增加到3.8 mg g(-1)。As(III)/As(V)和Cu(II)的吸附数据分别符合Freundlich和Langmuir等温线模型。As(III)、As(V)和Cu(II)的吸附遵循准二级动力学。砷形态对Cu(II)吸附的影响不显著。本研究结果表明,合成的吸附剂可用于同时去除废水中的阴离子和阳离子污染物。