School of Civil Engineering and Surveying, Faculty of Health, Engineering and Sciences, University of Southern Queensland, West Street, Toowoomba, Queensland 4350, Australia.
Korea Biochar Research Centre & Division of Environmental Sciences and Ecological Engineering, Korea University, Seoul, Republic of Korea.
Sci Total Environ. 2023 Jan 10;855:158877. doi: 10.1016/j.scitotenv.2022.158877. Epub 2022 Sep 20.
A modified chitosan-polyvinyl alcohol (PVA) hydrogel was developed by incorporating FeO nanoparticles. Four chitosan-FeO (ChFe) hydrogel types were developed based on chitosan:FeO ratio as 1:0, 1:1, 1:0.5 and 1:0.25. Batch sorption experiments were conducted with different pH, dosage, kinetics, and isotherms. The exhausted ChFe hydrogels were evaluated for their regeneration and reuse capability with different acids and bases. The best hydrogel for arsenic (V) [As(V)] adsorption was 1:0.5 ratio ChFe hydrogel. The highest As(V) adsorption (89 %) was at pH 4 and the adsorption capacity gradually decreased with increasing solution pH. Within the pH 4-6 range, the hydrogel surface became positively charged due to protonation of NH and OH groups in the polymer chain and the positive surface attracted HAsO and HAsO oxyanions. The experimental kinetic data was well-fitted to the Elovich model (R of 0.99) while the Freundlich isotherm model best described the isotherm data (R of 0.97). The models predicted chemisorption mechanisms on ChFe hydrogel composites. Electrostatic attractions with NH and OH, ligand-exchange inner-sphere complexes formation and bidentate corner-sharing (C) and bidentate edge-sharing (E) trimetric surface complexes formation have been proposed as the adsorption mechanism of As(V) into ChFe hydrogel. 0.1 M CHCOOH showed the best regeneration pattern with 75, 96, 81, 53 and 43 % of 1, 2, 3, 4 and 5 adsorption respectively. Because of this re-usable capability, the As(V) adsorption capacity is not a single value from one adsorption cycle, but a cumulative value of several adsorption cycles and it was 17.39 mg/g for five adsorption cycles. Open for regeneration and reuse, no post-treatment is needed for adsorbent-water separation, allow applications of the ChFe hydrogel composite in a wide range of applications such as water filtration and purification systems. The modification with ChFe further expands the application capacity since the ChFe can remove other contaminants as well.
一种改良的壳聚糖-聚乙烯醇(PVA)水凝胶通过掺入 FeO 纳米粒子而开发。根据壳聚糖:FeO 的比例,开发了四种壳聚糖-FeO(ChFe)水凝胶类型:1:0、1:1、1:0.5 和 1:0.25。进行了不同 pH 值、剂量、动力学和等温线的批量吸附实验。用过的 ChFe 水凝胶用不同的酸和碱评估其再生和再利用能力。对于砷(V)[As(V)]吸附,最佳水凝胶是 1:0.5 比例的 ChFe 水凝胶。在 pH 4 时,As(V)吸附率最高(89%),随着溶液 pH 值的增加,吸附率逐渐降低。在 pH 4-6 范围内,由于聚合物链中 NH 和 OH 基团的质子化,水凝胶表面带正电荷,正表面吸引 HAsO 和 HAsO 含氧阴离子。实验动力学数据很好地符合 Elovich 模型(R 为 0.99),而 Freundlich 等温线模型很好地描述了等温线数据(R 为 0.97)。这些模型预测了 ChFe 水凝胶复合材料的化学吸附机制。静电吸引与 NH 和 OH、配体交换内球络合形成以及双齿角共享(C)和双齿边共享(E)三角表面络合形成已被提出作为 As(V)进入 ChFe 水凝胶的吸附机制。0.1 M CHCOOH 表现出最佳的再生模式,分别为 1、2、3、4 和 5 次吸附的 75%、96%、81%、53%和 43%。由于这种可重复使用的能力,As(V)的吸附容量不是一个单一值,而是几个吸附循环的累积值,五个吸附循环的吸附容量为 17.39mg/g。由于可进行再生和再利用,无需对吸附剂-水进行后处理即可进行分离,这使得 ChFe 水凝胶复合材料在水过滤和净化系统等广泛应用中得到应用。ChFe 的修饰进一步扩大了应用能力,因为 ChFe 也可以去除其他污染物。