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ZIRCONIUM MODIFIED ACTIVATED CARBON MATERIALS FOR WATER DEFLUORIDATION

机译:用于水分渗透的锆改性活性炭材料

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Introduction Research in fluoride removal from drinking water has been conducted for several years. The guideline value (permissible upper limit) for fluoride in drinking water has been set at 1.5 mg L~(-1) according to the World Health Organization [1], however, the U.S. Department of Health and Human Services recommended 0.7 mg L~(-1) in January 2011 since recent studies confirmed the hazard of this element for human beings. Unfortunately, many places around the world have high fluoride concentrations, up to 30 mg L~(-1), in water supplies that may cause widespread fluorosis and skeletal illneses among the world population [2]. Many methods have been developed for fluoride removal from water including adsorption, ion exchange, electrodialysis and precipitation. Nevertheless, more efficient and cost-effective processes and materials are needed to fulfill the present regulations. Adsorption has been widely used because is the most cost-effective methodology for removal of ionic contaminants, like fluoride ions, in aqueous streams. Various fluoride adsorbents such as activated alumina, activated carbon, minerals, among others have been tested and have shown that large surface area and the interaction adsorbent-fluoride are important factors for defluoridation process [3,4]. Although activated carbon poorly removes fluoride from water, when it is impregnated with metal ions the adsorption capacity increases [5]. Zirconium and its metal complexes have been used for fluoride monitoring due to their high affinity for fluoride ions. When loaded in activated carbon, zirconium complexes increase the fluoride removal by 3 to 5 times at high fluoride concentrations [6]. The authors consider that the surface area of modified adsorbents is a key factor to increase their fluoride adsorption capacity, however, this is often neglected. The aim of this research is to improve the fluoride adsorption capacity of Zr(IV) modified granular activated carbon by controlling the particle size of the metal ion with a complexing agent such as oxalic acid during the impregnation process.
机译:借助于饮用水氟化物的研究已经进行了几年。根据世界卫生组织的饮用水中氟化物中氟化物的准则值(允许的上限)[1],然而,美国卫生和人类服务部推荐0.7毫克〜 (-1)2011年1月以来,最近的研究确认了对人类这种要素的危害。不幸的是,世界各地的许多地方都有高氟浓度高达30毫克L〜(-1),在供水,可能导致世界人口[2]的广泛和氟骨illneses。已经开发了许多方法,用于氟化物从含水中除去,包括吸附,离子交换,电渗析和沉淀。尽管如此,需要更高效,更具成本效益的流程和材料来履行本规定。吸附已被广泛使用,因为是最具成本效益的方法,用于除去离子污染物,如氟离子在含水物流中。已经测试了各种氟化物吸附剂,例如活性氧化铝,活性炭,矿物质,并且已经测试了,并且已经显示出大的表面积和相互作用吸附剂 - 氟化物是偏氟化过程的重要因素[3,4]。虽然活性炭含量不足,但是当它浸渍金属离子时,吸附能力增加[5]。由于它们对氟离子的高亲和力,锆及其金属配合物已被用于氟化物监测。当装载活性炭时,锆配合物在高氟化物浓度下将氟化物加热3至5倍增加[6]。作者认为改性吸附剂的表面积是提高氟化物吸附能力的关键因素,然而,这通常被忽略。该研究的目的是通过在浸渍过程中控制络合剂如草酸如草酸,通过控制金属离子的粒度来改善Zr(IV)改性粒状活性炭的氟化物吸附容量。

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