Mani Sai Kiran, Bhandari Rajni
Department of Chemistry, Sri Sathya Sai Institute of Higher Learning, Anantapur Campus, Anantapur 515001, India.
ACS Omega. 2022 Apr 20;7(17):15048-15063. doi: 10.1021/acsomega.2c00834. eCollection 2022 May 3.
Fixed-bed column adsorption studies are performed with metal-complexed polyvinyl alcohol (PVA) hydrogel beads to remove fluoride from groundwater. The fixed-bed column (bed height = 8 ± 0.2 cm) of copper-zirconium-PVA (PCZH), zirconium-PVA (PZH), and iron-zirconium-PVA (PFZH) hydrogel beads have equilibrium fluoride removal capacities of 17.26 ± 0.05, 31.67 ± 0.05, and 11.84 ± 0.05 mg g from a 10 ± 0.20 mg L fluoride solution of pH 6.5 maintained at a flow rate of 1 ± 0.01 mL min. The breakthrough curves for fluoride adsorption are analyzed by non-linear empirical models of Thomas, Bohart-Adams, Yoon-Nelson, and semi-empirical bed depth service time models. The maximum fluoride adsorption capacities obtained from the Thomas model are 25.66 ± 0.05, 38.17 ± 0.05, and 13.75 ± 0.05 mg g for PCZH, PZH, and PFZH. Moreover, the column of PZH (bed height = 4 ± 0.2 cm) removes about 1.67 ± 0.05 mg g of fluoride from the alkaline groundwater sample with high total dissolved solids containing 2.84 ± 0.20 mg L fluoride maintained at a flow rate of 0.5 ± 0.01 mL min. The fluoride removal efficiency decreases marginally (<1 ± 0.02%) in the presence of interfering ions such as chlorides, sulfates, phosphates, bicarbonates, and nitrates. Furthermore, the fixed-bed column (bed height = 4 ± 0.2 cm) of PCZH, PZH, and PFZH remove 7.40 ± 0.05, 14.85 ± 0.05, and 6.53 ± 0.05 mg g fluoride, respectively, even after the third regeneration cycle. Additionally, the hydrogel beads are effective in the removal of arsenate (≤90 ± 0.02%) and chromate ions (≤96 ± 0.02%) from 100 ± 0.20 mg L solution in batch adsorption studies. Therefore, the hydrogel beads could be used as potent filters for the removal of fluoride, chromate, and arsenate ions from water.
采用金属络合聚乙烯醇(PVA)水凝胶珠进行固定床柱吸附研究,以去除地下水中的氟化物。铜 - 锆 - PVA(PCZH)、锆 - PVA(PZH)和铁 - 锆 - PVA(PFZH)水凝胶珠的固定床柱(床高 = 8 ± 0.2 cm),在流速为1 ± 0.01 mL/min、pH值为6.5的10 ± 0.20 mg/L氟化物溶液中,平衡氟去除容量分别为17.26 ± 0.05、31.67 ± 0.05和11.84 ± 0.05 mg/g。通过托马斯(Thomas)、博哈特 - 亚当斯(Bohart - Adams)、尹 - 尼尔森(Yoon - Nelson)非线性经验模型和半经验床层深度服务时间模型分析氟吸附的穿透曲线。从托马斯模型获得的PCZH、PZH和PFZH的最大氟吸附容量分别为25.66 ± 0.05、38.17 ± 0.05和13.75 ± 0.05 mg/g。此外,PZH柱(床高 = 4 ± 0.2 cm)在流速为0.5 ± 0.01 mL/min的条件下,从含有2.84 ± 0.20 mg/L氟化物、总溶解固体含量高的碱性地下水样品中去除约1.67 ± 0.05 mg/g的氟化物。在存在氯化物、硫酸盐、磷酸盐、碳酸氢盐和硝酸盐等干扰离子的情况下,氟去除效率略有下降(<1 ± 0.02%)。此外,即使在第三次再生循环后,PCZH、PZH和PFZH的固定床柱(床高 = 4 ± 0.2 cm)分别去除7.40 ± 0.05、14.85 ± 0.05和6.53 ± 0.05 mg/g的氟化物。此外,在批量吸附研究中,水凝胶珠对100 ± 0.20 mg/L溶液中的砷酸盐(≤90 ± 0.02%)和铬酸盐离子(≤96 ± 0.02%)具有有效去除能力。因此,水凝胶珠可作为从水中去除氟化物、铬酸盐和砷酸盐离子的有效过滤器。