HaP/SBA-3 Nanostructured Composite to Remove Fluoride Effectively from Contaminated Water

O. Anunziata
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Abstract

Nanostructured materials, based on silica (MCM, SBA [1,2]) and ordered mesoporous carbon (OMC), such as CMK-1, CMK-3 [3] and Multi-Walled Carbon Nanotubes (MWCN) [4], because of their large surface area, pore volume and possibility to vary the pore size, offer a great opportunity for their application in various fields, from industrial processes to biomedical engineering, air and water pollution decontamination and energy reservoirs. Recently, we have developed a technique of preparation of monocrystalline hydroxyapatite (HaP) , and by the same procedure, but in the presence of the respective hosts, forming in situ composites such as HaP/MCM-41 and HaP/SBA15 composites [5]. Numerous approaches for fluoride removal from contaminated water, such as precipitation-coagulation [6], membrane technology [7,8], ion exchange [9] and adsorption [10,11]. Among the above methods, fluoride adsorption on adsorbents is attracting increasing attention due to its advantages of convenient design and operation, and low cost [12]. Different types of adsorbents, such as metal adsorbents [13], carbon adsorbents [14], carbon materials [15], natural materials [16], and biosorbents [17], have been used to remove fluoride from water. MOFs have also been used as new adsorbents for fluoride adsorption due to their surface functional groups and ordered atomic arrangement [18]. Calcium phosphate apatites are compounds of the formula Ca5 (PO4)3X, where X can be an Fion (fluorapatite, FaP), OH(hydroxyapatite, HaP), or a Clion (chlorapatite). The ion is substituted by another ion of the same sign but of different charge. Neutrality is maintained by substitutions of ions with different charges or vacancies [19]. Studied the crystallization of HaP (hydroxyapatite) on polymers containing C-N groups, from supersaturated solutions of HaP has been reported [20]. The growth of hydroxyapatite on silica gels in the presence of organic additives was studied by Rivera-Muñoz et al. [21]. Laghzizil et al. [22] have correlated the results of HaP fluorination with the physicochemical properties of HaP. Recently, morphological modifications of hydroxyapatite using fatty acids as an organic modifier have been reported [23]. The goal of this work is the successful Crimson Publishers Wings to the Research Short Communication
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HaP/SBA-3纳米结构复合材料有效去除污染水中的氟化物
基于二氧化硅(MCM, SBA[1,2])和有序介孔碳(OMC)的纳米结构材料,如CMK-1, CMK-3[3]和多壁碳纳米管(MWCN)[4],由于其大的表面积,孔体积和改变孔大小的可能性,为其在各个领域的应用提供了巨大的机会,从工业过程到生物医学工程,空气和水污染净化和能源储存。最近,我们开发了一种制备单晶羟基磷灰石(HaP)的技术,并通过相同的程序,但在各自的宿主存在下,形成原位复合材料,如HaP/MCM-41和HaP/SBA15复合材料[5]。除氟方法有沉淀-混凝法[6]、膜法[7,8]、离子交换法[9]和吸附法[10,11]等。在上述方法中,吸附剂吸附氟因其设计、操作方便、成本低等优点越来越受到人们的关注[12]。不同类型的吸附剂,如金属吸附剂[13]、碳吸附剂[14]、碳材料[15]、天然材料[16]和生物吸附剂[17],已被用于去除水中的氟化物。mof由于其表面官能团和有序的原子排列,也被用作新型的氟吸附剂[18]。磷酸钙磷灰石是分子式为Ca5 (PO4)3X的化合物,其中X可以是离子(氟磷灰石,FaP)、OH(羟基磷灰石,HaP)或cleon(氯磷灰石)。这个离子被另一个符号相同但带不同电荷的离子所取代。中性是通过不同电荷或空位的离子取代来维持的[19]。有报道研究了羟基磷灰石在含C-N基团的聚合物上从羟基磷灰石的过饱和溶液中结晶[20]。Rivera-Muñoz等[21]研究了有机添加剂存在下羟基磷灰石在硅胶上的生长。Laghzizil等[22]将羟基磷灰石氟化的结果与羟基磷灰石的理化性质联系起来。最近,利用脂肪酸作为有机改性剂对羟基磷灰石进行形态修饰的研究也有报道[23]。这项工作的目标是成功的深红出版社翼的研究短通信
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HaP/SBA-3 Nanostructured Composite to Remove Fluoride Effectively from Contaminated Water Challenges in Postprocessing of Hybrid Manufacturing of Magnet Polymer Composites to Enhance the Energy Product of NdFeB Bonded Magnets Experimental Simulation of Molten Corium and Sacrificial Material Interaction in a Scaled Down Core Catcher Properties in Fe-Doped ZnS Thin Films Recovery of Metallic Values in Smart Cards
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