Ou Jiun-Hau, Wang Chih-Chieh, Verpoort Francis, Chien Chih-Ching, Zhong Hua-Bin, Kao Chih-Ming
Institute of Environmental Engineering, National Sun Yat-Sen University, Kaohsiung, Taiwan.
Hershey Environmental Technology Corp., Ltd., Kaohsiung, Taiwan.
Chemosphere. 2024 Feb;350:141035. doi: 10.1016/j.chemosphere.2023.141035. Epub 2023 Dec 29.
In this study, the magnesium oxide (MgO)-based adsorbents [granulated MgO aggregates (GA-MgO) and surface-modified MgO powder (SM-MgO)] were developed to remediate a fluoride-contaminated groundwater site. Both GA-MgO and SM-MgO had porous, spherical, and crystalline structures. Diameters for GA-MgO and SM-MgO were 1-1.7 mm and 1-10 μm, respectively. The pseudo second-order dynamic adsorption and the Freundlich isotherm could be applied to express the chemical adsorption phenomena. The monolayer adsorption was the dominant mechanism at the initial adsorption period. During the latter part of fluoride adsorption, the multilayer adsorption became the dominant mechanism for fluoride removal from the water phase, which also resulted in the increased adsorption capacity. Higher hydroxide, phosphate, and carbonate concentrations caused a decreased fluoride removal efficiency due to the competition of sorption sites between fluoride and other anions with similar electronic properties. Fluoride removal mechanism using GA-MgO and SM-MgO as the adsorbents was mainly carried out by the chemical adsorption. Reaction paths contained two main processes: (1) formation of magnesium hydroxide after the reaction of MgO with water, and (2) the hydroxyl group of the magnesium hydroxide was replaced by fluoride ions to form magnesium fluoride precipitation. Results from column tests show that up to 61 and 73% of fluoride removal (initial fluoride concentration = 9.3 mg/L) could be obtained after 50 pore volumes of groundwater pumping with GA-MgO and SM-MgO injection, respectively. The GA-MgO system could be applied to contain and remediate fluoride-contaminated groundwater, and SM-MgO could be applied as an immediate fluoride removal alternative to achieve a rapid pollutant removal for emergency responses. Up to 71% of fluoride removal (fluoride concentration = 10.8 mg/L) could be obtained with GA-MgO injection after 30 days of operation. The developed GA-MgO system is a potential and green remediation alternative to contain the fluoride plume significantly.
在本研究中,开发了基于氧化镁(MgO)的吸附剂[粒状MgO聚集体(GA-MgO)和表面改性MgO粉末(SM-MgO)],用于修复受氟化物污染的地下水场地。GA-MgO和SM-MgO均具有多孔、球形和晶体结构。GA-MgO和SM-MgO的直径分别为1-1.7毫米和1-10微米。准二级动力学吸附和Freundlich等温线可用于描述化学吸附现象。初始吸附阶段以单层吸附为主导机制。在氟化物吸附后期,多层吸附成为从水相中去除氟化物的主导机制,这也导致吸附容量增加。较高的氢氧化物、磷酸盐和碳酸盐浓度导致氟化物去除效率降低,这是由于氟化物与其他具有相似电子性质的阴离子之间对吸附位点的竞争。以GA-MgO和SM-MgO为吸附剂的氟化物去除机制主要通过化学吸附进行。反应路径包含两个主要过程:(1)MgO与水反应后形成氢氧化镁,(2)氢氧化镁的羟基被氟离子取代形成氟化镁沉淀。柱试验结果表明,分别注入GA-MgO和SM-MgO并抽取50孔隙体积的地下水后,氟化物去除率分别可达61%和73%(初始氟化物浓度=9.3毫克/升)。GA-MgO系统可用于控制和修复受氟化物污染的地下水,而SM-MgO可作为一种即时去除氟化物的替代方法,以实现应急响应中污染物的快速去除。运行30天后,注入GA-MgO可实现高达71%的氟化物去除率(氟化物浓度=10.8毫克/升)。所开发的GA-MgO系统是一种潜在的绿色修复替代方法,可显著控制氟化物羽流。