Wastewater Treatment Using Biotechnological Approach

H. Kausar
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Abstract

Hazardous chemicals are forming at an accelerating rate due to a growing global population, necessitating ecological response. Wastewater management and treatment is a costly operation that needs the right technological integration to make it more practical and affordable. Algae are highly sought-after as potential feedstocks for a variety of applications, such as sustainability of environmental, the generation of bioproducts with high-worth, and the manufacturing of biofuels. One technique to reduce wastewater contamination is microalgae bioremediation. The demand for effective greenhouse gas reduction, wastewater treatment biomass reuse and nutrient recovery, has spurred a major concern in the microalgae use of wastewater treatment. Algal biomass can also be used to produce high-value bioproducts and bioenergy. Researchers from all over the world have investigated the use of microalgae for food additives, biofuels, and the production of bioactive and medicinal compounds. The commercial use of algae is now prohibited by technological and financial constraints, and efficient downstream processes are required to lower production costs. Therefore, using microalgae for both biofuel generation and wastewater treatment simultaneously could be a cost-effective way to solve both problems [1]. A different method is to use native bacteriophages as markers to detect the existence of enteric viruses of human, taking into account the bacteriophages. Native bacteriophages in particular share many characteristics with enteric viruses of human, including composition, size, structure, and replication-related elements. For instance, bacteriophages e.g FRNA have an isoelectric point (IEP) of 3.9and dimensions of about 25 nm and, which are related to those of the enterovirus (human) and hepatitis A virus (both of which have sizes of 22–30 nm and IEPs of 4.0–6.4). (IEP 2.8, 27e28 nm). Importantly, the technology used in bacteriophage assays is the quickest and least expensive for identifying human enteric viruses. Researchers are actively striving to quantitatively examine the link between human enteric viruses and native bacteriophages in order to determine the best indicator and improve prediction accuracy. Nevertheless, contrasting assumptions have emerged from the published investigations. The elimination of human pathogenic waterborne viruses, particularly enteric viruses of human, is a crucial factor to consider when assessing the efficiency of membrane treatment in the production of wastewater and drinking water [2]. An effective method for treating spent water that uses little energy is deammonification, which combines partial nitridation and anaerobic ammonium oxidation. Since the 1990s, when Anammox bacteria were first found, numerous full-scale side stream deammonification units handling high-ammonia used water have been operating successfully. However, there haven't been many reports of this method being utilized extensively to treat municipal waste water with low ammonia concentrations [3].
利用生物技术方法处理废水
由于全球人口的增长,有害化学物质正在加速形成,因此必须作出生态反应。废水管理和处理是一项昂贵的操作,需要正确的技术集成,使其更加实用和负担得起。藻类作为各种应用的潜在原料,如环境的可持续性、高价值生物产品的产生和生物燃料的制造,受到高度追捧。微藻生物修复是减少废水污染的一种技术。对有效减少温室气体排放、废水处理、生物质回用和养分回收的需求,引发了微藻利用废水处理的主要关注。藻类生物量也可用于生产高价值的生物产品和生物能源。来自世界各地的研究人员已经研究了微藻在食品添加剂、生物燃料以及生物活性和药用化合物生产中的应用。由于技术和资金的限制,藻类的商业用途现在被禁止,需要有效的下游工艺来降低生产成本。因此,将微藻同时用于生物燃料生产和废水处理可能是解决这两个问题的一种经济有效的方法[1]。另一种方法是利用天然噬菌体作为标志物来检测人类肠道病毒的存在,同时考虑到噬菌体的存在。特别是天然噬菌体与人肠道病毒具有许多共同的特征,包括组成、大小、结构和与复制有关的因素。例如,FRNA等噬菌体的等电点(IEP)为3.9,尺寸约为25 nm,与肠道病毒(人类)和甲型肝炎病毒的等电点(IEP)有关(两者的大小为22-30 nm, IEP为4.0-6.4)。(IEP 2.8, 27e28 nm)。重要的是,用于噬菌体测定的技术是鉴定人类肠道病毒的最快和最便宜的技术。研究人员正在积极努力定量研究人类肠道病毒与天然噬菌体之间的联系,以确定最佳指标并提高预测准确性。然而,从已发表的调查中出现了相反的假设。在评估膜处理在废水和饮用水生产中的效率时,消除人类致病性水传播病毒,特别是人类肠道病毒是一个重要的考虑因素[2]。脱氨是一种有效的低能耗处理废水的方法,它将部分硝化和厌氧氨氧化相结合。自20世纪90年代Anammox细菌首次被发现以来,许多处理高氨废水的全规模侧流脱氨装置已成功运行。然而,广泛应用该方法处理低氨浓度城市污水的报道并不多[3]。
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