实验室条件下萍萍植物修复潜力研究

Upekha Mandakini Lenaduwa Lokuge
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Under three main experiments, the fern’s phytoremediation ability was investigated. In the first experiment, A. pinnata was exposed to prepared solutions of Cr, Ni and Pb of 2ppm, 4ppm, 6ppm, 8ppm and 10ppm and of Cd solutions of 0.5ppm, 1.0ppm, 1.5ppm, 2.0ppm, 2.5ppm and 3.0ppm respectively. Experiments were carried out separately for Cr, Ni, Cd and Pb concentrations for 7 days. The concentrations of heavy metals used in the experiments largely agreed with the environmentally measured values, although in certain experiments, the initial concentrations exceeded the environmental pollution levels. The presence of Cr, Ni, Cd and Pb caused a maximum inhibition of A.pinnata growth by 47%, 54%, 52% and 45% respectively while the highest removal percentages of Cr- 98%, Ni- 57%, Cd- 88% and Pb- 86% were recorded in 2ppm, 2ppm, 0.5ppm and 8ppm treatments respectively. The highest Bio Concentration Factor (BCF) for Cr was 1376.67 when treated with 6ppm, 684.95 at 4ppm for Ni, 1120.06 at 0.5ppm for Cd and 1332.53 at 8ppm for Pb respectively. At the end of the experiments toxic symptoms were observed in plats exposed to Cd and Ni. The findings of this experiment revealed that A. pinnata is an excellent candidate for the removal of Pb and Cr even at higher concentrations and for Cd at lower concentrations while it is only partially efficient for Ni removal. The ability of A. pinnata to remove Cr, Ni, Cd and Pb from open dump site leachate was investigated in the experiment two. A. pinnata was exposed to a leachate dilution series of 5%, 15%, 25%, 50%, 75% and 100%. For all four metals, the highest removal percentages as well as the highest BCFs were given by the plants exposed to 5% leachate concentration. The maximum removal percentages were 70%, 52%, 50% and 72% and highest BCFs were 1248.51, 1199.19,867.33 and 1355.43 for Cr, Ni, Cd and Pb respectively. Growth of the fern was limited by around 90% when exposed to leachate treatments. The influence of interactive effects of Cr, Cd, Ni and Pb on their removal capacities of Azolla pinnata and the metal selectivities were determined bythe experiment three. Two treatments were prepared based on the findings of experiment one and two. Treatment I consisted of Cr, Ni, Cd and Pb concentrations that gave the highest BCFs in experiment one where treatment II was based on concentrations of 5% leachate treatment that gave the highest BCFs in experiment two. BCFs obtained from the treatment I were 1023.77, 679.97, 1048.39 and 939.77 for Cr, Ni, Cd and Pb respectively, hence all the BCFs were lower than of experiment one results proving the influence of interactive effects among the heavy metals on the uptake efficiency. In treatment I and II, the removal efficiency of Cr was 81% and 100%, for Ni it was 56% and 93%, 83% and 100% for Cd and for Pb it was 85% and 99%. Thus the metal selectivity of A. pinnata was Pb> Cd> Cr> Ni. Azolla pinnata can be designated as a good phytoremediation tool for the mitigation of heavy metal pollution due to its high BCFs (over 1000) in relation to Pb (2-10ppm), Cr (2-10ppm) and Cd (0.5-1ppm). However, field studies are warranted to further our claims. 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The ability of A. pinnata to remove Cr, Ni, Cd and Pb from open dump site leachate was investigated in the experiment two. A. pinnata was exposed to a leachate dilution series of 5%, 15%, 25%, 50%, 75% and 100%. For all four metals, the highest removal percentages as well as the highest BCFs were given by the plants exposed to 5% leachate concentration. The maximum removal percentages were 70%, 52%, 50% and 72% and highest BCFs were 1248.51, 1199.19,867.33 and 1355.43 for Cr, Ni, Cd and Pb respectively. Growth of the fern was limited by around 90% when exposed to leachate treatments. The influence of interactive effects of Cr, Cd, Ni and Pb on their removal capacities of Azolla pinnata and the metal selectivities were determined bythe experiment three. Two treatments were prepared based on the findings of experiment one and two. 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引用次数: 14

摘要

水生环境中的重金属污染已成为世界各国面临的主要环境问题之一。植物修复是一种基于植物的技术,利用被称为超蓄积体的特殊植物来净化重金属污染场地。超蓄积体能够吸收高浓度的重金属。凤尾花是一种水生植物,因其超积累能力而被认为是一种水生植物。这种绿色技术往往比传统方法更受欢迎,因为它成本低,对环境的影响小,而且更容易被公众接受。本研究在实验室条件下,考察了桄榔子通过根茎过滤去除Cr、Ni、Cd和Pb的能力,这是实验室条件下植物修复策略之一。通过三个主要实验,研究了蕨类植物的修复能力。在第一个实验中,将桄榔子分别暴露于2ppm、4ppm、6ppm、8ppm、10ppm的Cr、Ni、Pb溶液和0.5ppm、1.0ppm、1.5ppm、2.0ppm、2.5ppm、3.0ppm的Cd溶液中。Cr、Ni、Cd和Pb浓度分别进行7 d试验。实验中使用的重金属浓度与环境测量值基本一致,尽管在某些实验中,初始浓度超过了环境污染水平。Cr、Ni、Cd和Pb在2ppm、2ppm、0.5ppm和8ppm处理下的去除率分别为Cr- 98%、Ni- 57%、Cd- 88%和Pb- 86%,其中Cr、Ni、Cd和Pb的去除率分别为47%、54%、52%和45%。6ppm、4ppm、0.5ppm和8ppm处理下Cr的最高生物浓度因子(BCF)分别为1376.67、684.95、1120.06和1332.53。在实验结束时,在暴露于Cd和Ni的植物中观察到中毒症状。实验结果表明,桄子菜对高浓度的Pb、Cr和低浓度的Cd都有较好的去除效果,而对Ni的去除效果较差。试验二考察了桄榔子对露天垃圾场渗滤液中Cr、Ni、Cd和Pb的去除能力。分别用5%、15%、25%、50%、75%和100%稀释的渗滤液处理桄子子草。对于所有四种金属,暴露于5%渗滤液浓度的植物的去除率最高,BCFs最高。Cr、Ni、Cd和Pb的最大去除率分别为70%、52%、50%和72%,最高BCFs分别为1248.51、1199.19,867.33和1355.43。当暴露于渗滤液处理时,蕨类植物的生长受到约90%的限制。通过实验三确定了Cr、Cd、Ni和Pb的相互作用对小红花的去除能力和金属选择性的影响。在实验一和实验二的基础上制备了两种处理。处理1由Cr、Ni、Cd和Pb浓度组成,在实验1中产生最高的BCFs;处理2基于5%的渗滤液浓度处理,在实验2中产生最高的BCFs。处理1对Cr、Ni、Cd和Pb的BCFs分别为1023.77、679.97、1048.39和939.77,均低于试验1,说明重金属间的交互作用对土壤吸收效率的影响。处理ⅰ和处理ⅱ对Cr的去除率分别为81%和100%,对Ni的去除率分别为56%和93%,对Cd的去除率分别为83%和100%,对Pb的去除率分别为85%和99%。因此,对金属的选择性为Pb> Cd> Cr> Ni。由于其相对于Pb (2-10ppm)、Cr (2-10ppm)和Cd (0.5-1ppm)的BCFs值较高(超过1000),可被指定为缓解重金属污染的良好植物修复工具。然而,实地研究有必要进一步证实我们的说法。关键词:植物修复,凤仙花,重金属,生物浓度因子,金属积累
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A study on the Phytoremediation Potential of Azolla pinnata under laboratory conditions
Heavy metal contamination in aquatic environments has become one of the major environmental problems all over the world. Phytoremediation is a plant based technology that utilizes special plants known as hyperaccumulators to purify heavy metal contaminated sites. Hyperaccumulators are capable of absorbing heavy metals in greater concentrations.  Azolla pinnata is an aquatic macrophyte that has been earmarked for its hyperaccumulation ability. This green technology is often more favoured over conventional methods due to its low cost, low environmental impacts and wider public acceptance. This study was conducted under laboratory conditions to assess the ability of A. pinnata for the removal of Cr, Ni, Cd and Pb through rhizofiltration, which is one of the phytoremediation strategies under laboratory conditions. Under three main experiments, the fern’s phytoremediation ability was investigated. In the first experiment, A. pinnata was exposed to prepared solutions of Cr, Ni and Pb of 2ppm, 4ppm, 6ppm, 8ppm and 10ppm and of Cd solutions of 0.5ppm, 1.0ppm, 1.5ppm, 2.0ppm, 2.5ppm and 3.0ppm respectively. Experiments were carried out separately for Cr, Ni, Cd and Pb concentrations for 7 days. The concentrations of heavy metals used in the experiments largely agreed with the environmentally measured values, although in certain experiments, the initial concentrations exceeded the environmental pollution levels. The presence of Cr, Ni, Cd and Pb caused a maximum inhibition of A.pinnata growth by 47%, 54%, 52% and 45% respectively while the highest removal percentages of Cr- 98%, Ni- 57%, Cd- 88% and Pb- 86% were recorded in 2ppm, 2ppm, 0.5ppm and 8ppm treatments respectively. The highest Bio Concentration Factor (BCF) for Cr was 1376.67 when treated with 6ppm, 684.95 at 4ppm for Ni, 1120.06 at 0.5ppm for Cd and 1332.53 at 8ppm for Pb respectively. At the end of the experiments toxic symptoms were observed in plats exposed to Cd and Ni. The findings of this experiment revealed that A. pinnata is an excellent candidate for the removal of Pb and Cr even at higher concentrations and for Cd at lower concentrations while it is only partially efficient for Ni removal. The ability of A. pinnata to remove Cr, Ni, Cd and Pb from open dump site leachate was investigated in the experiment two. A. pinnata was exposed to a leachate dilution series of 5%, 15%, 25%, 50%, 75% and 100%. For all four metals, the highest removal percentages as well as the highest BCFs were given by the plants exposed to 5% leachate concentration. The maximum removal percentages were 70%, 52%, 50% and 72% and highest BCFs were 1248.51, 1199.19,867.33 and 1355.43 for Cr, Ni, Cd and Pb respectively. Growth of the fern was limited by around 90% when exposed to leachate treatments. The influence of interactive effects of Cr, Cd, Ni and Pb on their removal capacities of Azolla pinnata and the metal selectivities were determined bythe experiment three. Two treatments were prepared based on the findings of experiment one and two. Treatment I consisted of Cr, Ni, Cd and Pb concentrations that gave the highest BCFs in experiment one where treatment II was based on concentrations of 5% leachate treatment that gave the highest BCFs in experiment two. BCFs obtained from the treatment I were 1023.77, 679.97, 1048.39 and 939.77 for Cr, Ni, Cd and Pb respectively, hence all the BCFs were lower than of experiment one results proving the influence of interactive effects among the heavy metals on the uptake efficiency. In treatment I and II, the removal efficiency of Cr was 81% and 100%, for Ni it was 56% and 93%, 83% and 100% for Cd and for Pb it was 85% and 99%. Thus the metal selectivity of A. pinnata was Pb> Cd> Cr> Ni. Azolla pinnata can be designated as a good phytoremediation tool for the mitigation of heavy metal pollution due to its high BCFs (over 1000) in relation to Pb (2-10ppm), Cr (2-10ppm) and Cd (0.5-1ppm). However, field studies are warranted to further our claims. Key words: Phytoremediation, Azolla pinnata , Heavy metals, Bio Concentration Factor, Metal accumulation
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