{"title":"天然粘土负载的零价铁纳米颗粒作为工业废水中氨还原的潜在混凝剂","authors":"Wighens I. Ngoie","doi":"10.33552/mcms.2019.01.000512","DOIUrl":null,"url":null,"abstract":"Water pollution is one of the largest environment problems in several countries. It mainly arises from wastewater released from household, industrial and agricultural processes. These effluents typically contain high concentrations of organic and inorganic chemicals such as hydrocarbon solvents, heavy metals, pesticides, dyes and so on. The toxicity, persistency and concentration of the contaminants result in serious environmental, public health and economic impacts [5]. Consequently, treatment of wastewater effluents before release into the environment is required. There are several wastewater treatment techniques including physical, chemical or biological processes i.e. coagulation, flocculation, adsorption, reverse osmosis, activated sludge and so on, which are used to remove pollutants from wastewater influents. Nevertheless, these conventional techniques have shown limitations, for the removal of ammonia. Use of activated clay, is one of the most promising techniques because the natural clay is of low-cost, is easy to obtain, and has good effectiveness and ability of degrading contaminants due to its adsorptive properties enhanced by sulphuric acid, which will supply charges to break the stability of ammonia in water by attracting them at the coagulant surface, then the activated clay will secondly be supported by zero valent iron nanoparticles in a homogenous mixture to increase the surface area on which the adsorption of pollutants will effectively take place [6,7,8]. Ion exchange and reverse osmosis have failed to destroy efficiently nitrate species and regenerate secondary brine wastes; electro-catalytic process necessitates higher potential to reduce nitrate into nitrogen. Basically, according to samples that were collected from several Wastewater plants in Cape Town, for instance, here below is the concentration trend of ammonia from the current WWTPs (red) comparatively to the standards (blue) (Figure 1). *Corresponding author: Wighens I Ngoie, Department of Chemical Engineering, Biocatalysis & Technical Biology Research Group, Cape Peninsula University of Technology, Bellville Campus, South Africa. 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These effluents typically contain high concentrations of organic and inorganic chemicals such as hydrocarbon solvents, heavy metals, pesticides, dyes and so on. The toxicity, persistency and concentration of the contaminants result in serious environmental, public health and economic impacts [5]. Consequently, treatment of wastewater effluents before release into the environment is required. There are several wastewater treatment techniques including physical, chemical or biological processes i.e. coagulation, flocculation, adsorption, reverse osmosis, activated sludge and so on, which are used to remove pollutants from wastewater influents. Nevertheless, these conventional techniques have shown limitations, for the removal of ammonia. Use of activated clay, is one of the most promising techniques because the natural clay is of low-cost, is easy to obtain, and has good effectiveness and ability of degrading contaminants due to its adsorptive properties enhanced by sulphuric acid, which will supply charges to break the stability of ammonia in water by attracting them at the coagulant surface, then the activated clay will secondly be supported by zero valent iron nanoparticles in a homogenous mixture to increase the surface area on which the adsorption of pollutants will effectively take place [6,7,8]. Ion exchange and reverse osmosis have failed to destroy efficiently nitrate species and regenerate secondary brine wastes; electro-catalytic process necessitates higher potential to reduce nitrate into nitrogen. Basically, according to samples that were collected from several Wastewater plants in Cape Town, for instance, here below is the concentration trend of ammonia from the current WWTPs (red) comparatively to the standards (blue) (Figure 1). *Corresponding author: Wighens I Ngoie, Department of Chemical Engineering, Biocatalysis & Technical Biology Research Group, Cape Peninsula University of Technology, Bellville Campus, South Africa. 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引用次数: 1
摘要
水污染是一些国家最大的环境问题之一。它主要来自家庭、工业和农业过程中排放的废水。这些废水通常含有高浓度的有机和无机化学品,如碳氢化合物溶剂、重金属、农药、染料等。污染物的毒性、持久性和浓度造成了严重的环境、公共卫生和经济影响[5]。因此,需要在废水排放到环境之前对其进行处理。有几种废水处理技术,包括物理、化学或生物过程,即混凝、絮凝、吸附、反渗透、活性污泥等,用于去除废水中的污染物。然而,这些传统技术在去除氨方面显示出局限性。使用活性粘土是最有前途的技术之一,因为天然粘土成本低,易于获得,并且由于其吸附性能被硫酸增强而具有良好的降解污染物的效果和能力,硫酸会通过在混凝剂表面吸引它们来提供电荷以打破水中氨的稳定性。然后,活性粘土将被零价铁纳米颗粒在均匀混合物中支撑,以增加有效吸附污染物的表面积[6,7,8]。离子交换和反渗透都不能有效地破坏硝态氮和再生二次卤水废物;电催化过程需要更高的电位将硝酸盐还原成氮。基本上,根据从开普敦几家污水厂收集的样本,例如,下图是目前污水处理厂中氨的浓度趋势(红色)与标准(蓝色)(图1)。*通讯作者:Wighens I Ngoie,南非开普半岛理工大学贝尔维尔校区生物催化与技术生物学研究小组化学工程系。收稿日期:2018年11月9日发布日期:2019年6月10日ISSN: 2692-5397 DOI: 10.33552/MCMS.2020.01.000512
Natural Clay Supported Zerovalent Iron Nanoparticles as a Potential Coagulant for Ammonia Reduction from Industrial Wastewater Effluents
Water pollution is one of the largest environment problems in several countries. It mainly arises from wastewater released from household, industrial and agricultural processes. These effluents typically contain high concentrations of organic and inorganic chemicals such as hydrocarbon solvents, heavy metals, pesticides, dyes and so on. The toxicity, persistency and concentration of the contaminants result in serious environmental, public health and economic impacts [5]. Consequently, treatment of wastewater effluents before release into the environment is required. There are several wastewater treatment techniques including physical, chemical or biological processes i.e. coagulation, flocculation, adsorption, reverse osmosis, activated sludge and so on, which are used to remove pollutants from wastewater influents. Nevertheless, these conventional techniques have shown limitations, for the removal of ammonia. Use of activated clay, is one of the most promising techniques because the natural clay is of low-cost, is easy to obtain, and has good effectiveness and ability of degrading contaminants due to its adsorptive properties enhanced by sulphuric acid, which will supply charges to break the stability of ammonia in water by attracting them at the coagulant surface, then the activated clay will secondly be supported by zero valent iron nanoparticles in a homogenous mixture to increase the surface area on which the adsorption of pollutants will effectively take place [6,7,8]. Ion exchange and reverse osmosis have failed to destroy efficiently nitrate species and regenerate secondary brine wastes; electro-catalytic process necessitates higher potential to reduce nitrate into nitrogen. Basically, according to samples that were collected from several Wastewater plants in Cape Town, for instance, here below is the concentration trend of ammonia from the current WWTPs (red) comparatively to the standards (blue) (Figure 1). *Corresponding author: Wighens I Ngoie, Department of Chemical Engineering, Biocatalysis & Technical Biology Research Group, Cape Peninsula University of Technology, Bellville Campus, South Africa. Received Date: November 09, 2018 Published Date: June 10, 2019 ISSN: 2692-5397 DOI: 10.33552/MCMS.2020.01.000512