人工湿地及其在植物-微生物相互作用修复工业废水中的作用综述

Filza Hussain, G. Mustafa, Rabisa Zia, Ali Faiq, M. Matloob, Haseeb-ur-Rehman Shah, A. Raza, Jazib Ali Irfan
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Constructed wetland treatment systems efficiently remove several kinds of pollutants from wastewater, drinking water, and industrial effluents within the controlled environment and are considered as environment-friendly. Removal of effluents, metal and waste are performed through a variety of processes i.e., by increasing sorption, hydrolysis, filtration and oxidation, precipitation, binding with iron oxide, microbial activity and uptake by plants. In response to removing pollution, constructed wetlands differ in their processes, cost effectiveness and their design and also enhance the waste removal performance by using different substrates i.e., Phosphorus (P). In the recent years, scientists have tried to remediate or clean up wastewater through phytoremediation and bioremediation. Constructed wetland treatment systems use microbes and rooted plants to remove contaminants from soil or wastewater. It takes advantage of natural wetland processes (biological, physical and chemical processes ) to remove contaminants but the efficiency of all the processes (Chemical, physical and Biological) differ with water residence time. This technology is now widely used (in America, China, Argentina, Czech Republic, Greece, Netherlands, and Europe) and tested to efficiently improve water quality. However, the industrial and environmental sector pay more attention to remove heavy metals form industrial effluents using CWs. CWs are more effective and have significantly low capital costs as compared to conventional system (ITRC 2003) and also require less labor and electricity to operated (USEPA 1988). The main objective of constructing the constructed wetland is to optimize the interaction of the substrate with microbial species and plants cells and then bioconversion into harmless products. The haplotype plants and microbes that are used in wastewater treatment not only accumulate heavy metals but also perform the function of catalysts for purification reaction. Several factors also influence the remediation process which includes plant transpiration, and growth rates, storage, and accumulation in root and leaf cells, sedimentation, pH of media. CWs are composed of one or two chambers which are filled with the substrate that support the growth of haplotype plants and microorganisms. The substrate is both directly and indirectly involved in the remediation of pollutants, directly these substrates are involved in precipitation and filtration of suspended solids, sorption of heavy metals and organic matter and indirectly act as adhesion of microorganisms and support to root system. Nowadays an integrated technique is used to efficiently remediate the contaminants or pollutants from drinking water and industrial effluents from the soil. The main aim of this review is to evaluate and explain the role of constructed wetlands to remove industrial effluent. Conclusion: Phytoremediation in the past years has shown a promising evidence in case of the removal of different kinds of industrial effluents from the soils as well as the waters. Removal of contaminants discharged from the industries is essential for the better sustenance of the ecosystem and the protection of the various life forms including, humans, animals, and the microbial life forms. Removal of these contaminants discharged from the industries is of extreme importance and is the most focused area research for the environmental scientists of today because of the increase in the industrialization as well as the population of the developing and under-developed countries has made it an utter requirement for the wealthy people to establish industries and fulfill the increasing demands of the increasing world population. Phytoremediation is the cheap and the most accurate and widely adopted method to remove industrial effluents from the water as well as the contaminated soils. Plant-microbe interaction in most cases does not work efficiently as it is needed to, in that case, the scientists are making their efforts to engineer certain plant growth-promoting and contaminant degrading bacteria which would harm the environment and the plants to a neglectable level and would efficiently degrade the contaminants present in the soils and in water. Several plant species like Lolium multiflorum (Italian ryegrass), Typha domingensis (Southern cattail), Vetiver grass, Lolium prenne, Brachaiaria mutica etc. are known as the best for the phytoremediation which work efficiently in association with the microbes colonizing their roots. 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引用次数: 14

摘要

人工湿地(CWs)是污水处理和净化的一种替代方法。在过去的几十年里,尽管Kathe Seidel博士在20世纪50年代初首次使用人工湿地进行废水处理,但CW技术几乎没有被用于去除污染物。但自20世纪90年代以来,该技术开始进入发展阶段,用于处理各种类型的废水,如工业废水、城市污水和饮用水。化粪池是通过去除污染物或将污染物水平降低到可排放限度来模拟自然过程的工程系统。人工湿地处理系统在控制环境内有效地去除废水、饮用水和工业废水中的几种污染物,被认为是环境友好型的。废水、金属和废物的去除是通过各种过程进行的,即通过增加吸附、水解、过滤和氧化、沉淀、与氧化铁结合、微生物活动和植物吸收。为了消除污染,人工湿地在工艺、成本效益和设计上都有所不同,并且通过使用不同的基质(如磷)来提高废物的去除性能。近年来,科学家们试图通过植物修复和生物修复来修复或清理废水。人工湿地处理系统利用微生物和有根植物去除土壤或废水中的污染物。它利用天然湿地过程(生物、物理和化学过程)去除污染物,但所有过程(化学、物理和生物)的效率因水停留时间而异。该技术现已广泛应用于(美国、中国、阿根廷、捷克、希腊、荷兰和欧洲),并经过测试有效地改善了水质。然而,工业和环境部门越来越重视利用化粪池去除工业废水中的重金属。与传统系统相比,化学武器更有效,资本成本显著降低(ITRC 2003),并且需要更少的劳动力和电力来操作(USEPA 1988)。构建人工湿地的主要目的是优化基质与微生物物种和植物细胞的相互作用,并将其转化为无害产品。污水处理中使用的单倍型植物和微生物不仅能积累重金属,还能起到净化反应的催化剂作用。有几个因素也会影响修复过程,包括植物的蒸腾作用、生长速率、根和叶细胞的储存和积累、沉降、培养基的pH值。CWs由一个或两个室组成,其中充满了支持单倍型植物和微生物生长的底物。基质直接和间接参与污染物的修复,直接参与悬浮物的沉淀和过滤、重金属和有机物的吸附,间接参与微生物的粘附和对根系的支持。目前,人们采用一种综合技术来有效地修复土壤中饮用水和工业废水中的污染物。本文的主要目的是评价和解释人工湿地在去除工业废水中的作用。结论:近年来,植物修复技术在土壤和水体中各种工业废水的去除方面显示出良好的效果。清除工业排放的污染物对于更好地维持生态系统和保护各种生命形式至关重要,包括人类,动物和微生物生命形式。清除工业排放的这些污染物是极其重要的,也是当今环境科学家最关注的研究领域,因为工业化的增加以及发展中国家和欠发达国家的人口的增加,使得富人建立工业和满足日益增长的世界人口的需求成为绝对的要求。植物修复是一种经济、准确、广泛采用的去除水中工业废水和污染土壤的方法。在大多数情况下,植物与微生物的相互作用并不像需要的那样有效地起作用,在这种情况下,科学家们正在努力设计某些促进植物生长和降解污染物的细菌,这些细菌会对环境和植物造成可忽略不计的危害,并能有效地降解土壤和水中的污染物。 几种植物,如黑麦草(Lolium multiflorum)、香蒲(Typha domingensis)、香根草(香根草)、黑麦草(Lolium prenne)、花蒿(brhaiaria mutica)等,被认为是植物修复效果最好的植物,它们与定植在根部的微生物相关联,有效地发挥作用。适当的植物-微生物相互作用策略和对浮动湿地的管理有助于这种湿地的发展,这种湿地可以用来处理更大的水面面积,并尽可能多地去除污染物,这些污染物不会损害在水中或土壤中茁壮成长的生命形式,否则这些生命形式将因周围环境中无法忍受的污染物而死亡。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
Constructed Wetlands and their Role in Remediation of Industrial Effluents via Plant-Microbe Interaction – A Mini Review
Constructed wetlands (CWs) are an alternative method for wastewater treatment and its purification. In the past decades, CW techniques were hardly used for contamination removal, although first time in early 1950s, Dr. Kathe Seidel used constructed wetland for wastewater treatment. But evolutionary period started since the 1990s, this technique is used to treat various types of wastewaters i.e., industrial effluents, municipal wastewater, and drinking waters. CWs are the engineered systems that mimics the natural processes by removing the pollutants or by reducing the level of pollutants to a dischargeable limit. Constructed wetland treatment systems efficiently remove several kinds of pollutants from wastewater, drinking water, and industrial effluents within the controlled environment and are considered as environment-friendly. Removal of effluents, metal and waste are performed through a variety of processes i.e., by increasing sorption, hydrolysis, filtration and oxidation, precipitation, binding with iron oxide, microbial activity and uptake by plants. In response to removing pollution, constructed wetlands differ in their processes, cost effectiveness and their design and also enhance the waste removal performance by using different substrates i.e., Phosphorus (P). In the recent years, scientists have tried to remediate or clean up wastewater through phytoremediation and bioremediation. Constructed wetland treatment systems use microbes and rooted plants to remove contaminants from soil or wastewater. It takes advantage of natural wetland processes (biological, physical and chemical processes ) to remove contaminants but the efficiency of all the processes (Chemical, physical and Biological) differ with water residence time. This technology is now widely used (in America, China, Argentina, Czech Republic, Greece, Netherlands, and Europe) and tested to efficiently improve water quality. However, the industrial and environmental sector pay more attention to remove heavy metals form industrial effluents using CWs. CWs are more effective and have significantly low capital costs as compared to conventional system (ITRC 2003) and also require less labor and electricity to operated (USEPA 1988). The main objective of constructing the constructed wetland is to optimize the interaction of the substrate with microbial species and plants cells and then bioconversion into harmless products. The haplotype plants and microbes that are used in wastewater treatment not only accumulate heavy metals but also perform the function of catalysts for purification reaction. Several factors also influence the remediation process which includes plant transpiration, and growth rates, storage, and accumulation in root and leaf cells, sedimentation, pH of media. CWs are composed of one or two chambers which are filled with the substrate that support the growth of haplotype plants and microorganisms. The substrate is both directly and indirectly involved in the remediation of pollutants, directly these substrates are involved in precipitation and filtration of suspended solids, sorption of heavy metals and organic matter and indirectly act as adhesion of microorganisms and support to root system. Nowadays an integrated technique is used to efficiently remediate the contaminants or pollutants from drinking water and industrial effluents from the soil. The main aim of this review is to evaluate and explain the role of constructed wetlands to remove industrial effluent. Conclusion: Phytoremediation in the past years has shown a promising evidence in case of the removal of different kinds of industrial effluents from the soils as well as the waters. Removal of contaminants discharged from the industries is essential for the better sustenance of the ecosystem and the protection of the various life forms including, humans, animals, and the microbial life forms. Removal of these contaminants discharged from the industries is of extreme importance and is the most focused area research for the environmental scientists of today because of the increase in the industrialization as well as the population of the developing and under-developed countries has made it an utter requirement for the wealthy people to establish industries and fulfill the increasing demands of the increasing world population. Phytoremediation is the cheap and the most accurate and widely adopted method to remove industrial effluents from the water as well as the contaminated soils. Plant-microbe interaction in most cases does not work efficiently as it is needed to, in that case, the scientists are making their efforts to engineer certain plant growth-promoting and contaminant degrading bacteria which would harm the environment and the plants to a neglectable level and would efficiently degrade the contaminants present in the soils and in water. Several plant species like Lolium multiflorum (Italian ryegrass), Typha domingensis (Southern cattail), Vetiver grass, Lolium prenne, Brachaiaria mutica etc. are known as the best for the phytoremediation which work efficiently in association with the microbes colonizing their roots. Proper plant-microbes interaction strategies and the management of the floating wetlands could aid in the development of such wetlands that can be used to treat the greater surface area of water and remove as much contaminant s as possible that could not harm the life forms thriving in the water or in the soil which would otherwise die off due to intolerable level of pollutants in their surrounding environment.
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