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Biochelators as an alternative to EDTA and other synthetic chelators for the phytoextraction of heavy metals (Cu, Cd, Pb) from soil

机译:生物螯合剂可替代EDTA和其他合成螯合剂,用于从土壤中萃取重金属(铜,镉,铅)

摘要

Heavy metal pollution of soil is a global problem. Diffuse contamination of large areas causes particular difficulties, since most classical engineering technology directed at soil decontamination is associated with a loss of land, and is usually costly. For arable land, in which low to medium level contamination threatens soil fertility and human health in the long term, gentle remediation techniques are required which not only reduce toxicological risks, but also restore soil fertility. In order to overcome these problems, the use of plants to extract metals from soil (Phytoextraction) has repeatedly been suggested as a novel clean-up technology. Phytoextraction using hyperaccumulator plants is usually limited by low biomass, whereas metal uptake by high biomass plants usually suffers from low phytoavailability of the metal. One strategy to overcome these limitations is to enhance metal phytoavailability by the application of chelates. EDTA has been the most commonly used chelating agent for phytoextraction. Its disadvantage, though, is its persistence in the environment. This leads to a high risk of metal leaching into the groundwater. Furthermore, there have been signs of high toxicity towards plants and microorganisms. Various naturally occurring chelating agents, such as natural low molecular weight organic acids (NLMWOA), cyclodextrins (CyD), (S,S)-N,N’-ethylenediamine disuccinic acid (EDDS) and wool in hydrolysed form were selected for use. All these chelating agents have a common denominator, they are synthesised by natural processes, such as microorganisms, plants or animals and are thus biodegradable. The ability of the above mentioned chelating agents to mobilise heavy metals was assessed in slurry and column experiments. Phytotoxicity experiments evaluating the toxic effect of the chelates on plants were succeeded by phytoextraction pot experiments in the greenhouse. The degree of biodegradability of the chelates was evaluated with oxitop and pot experiments. Attention was given on the influence of the chelating agents on the bioavailability of heavy metals during the degradation process. Microorganisms which degrade the applied chelating agents were characterised in the case of NLMWOA. The studied NLMWOA, citric acid, oxalic acid and tartaric acid, displayed low toxicity to plants and high Cu mobilisation effectiveness. The high effectiveness was not confirmed in the phytoextraction experiment, where EDTA, considering the amounts applied was more effective. The reason for this lies in the high degree of biodegradability of the NLMWOA. All three investigated NLMWOA were degraded by the same microorganisms and displayed a significant pH increase in the soil during the degradation. This pH increase was accompanied by a decrease in the bioavailability of the heavy metals. The CyD revealed a high toxicity towards tobacco and a very low capacity mobilising heavy metals. Additionally a high degree of biodegradability was observed. EDDS, compared to EDTA, displayed a higher toxicity to tobacco. Both showed the same effectiveness in mobilising Cd and Cu in a column experiment. In the phytoextraction experiment EDDS increased the uptake of Cu but not of Cd, and both chelates failed to increase the root to shoot translocation rate. EDDS displayed a degree of biodegradability lower than often currently stated. A replanting of the pots revealed a prolonged toxicity effect of the remaining EDDS in the soil on the seedlings revealing new challenges for the field of chelate assisted phytoextraction. Wool hydrolysate displayed a high efficiency mobilising Cu in soil. Depending on the degree of hydrolysation for the applied wool, it increased the uptake by up to 850%. It revealed a very high degree of biodegradability, which, moreover was not accompanied by side effects, such as the increase of soil pH, and the accompanied decrease of the bioavailability of the heavy metals. The results from this study demonstrate that hyrolysed wool may be applied as a perfect substitute of the commonly used EDTA for enhancement of phytoextraction. The other tested biochelators, however, are not suitable to replace EDTA.
机译:土壤的重金属污染是一个全球性问题。大面积的扩散污染造成了特别的困难,因为大多数针对土壤去污的经典工程技术都与土地损失有关,而且通常很昂贵。对于中低水平的污染长期威胁土壤肥力和人类健康的耕地,需要采用温和的修复技术,不仅可以降低毒理学风险,而且还可以恢复土壤肥力。为了克服这些问题,已经多次提出使用植物从土壤中提取金属(植物提取)作为一种新颖的净化技术。使用高蓄积植物的植物提取通常受到低生物量的限制,而高生物量植物的金属吸收通常遭受金属的低植物利用率。克服这些局限性的一种策略是通过应用螯合物来提高金属的植物利用率。 EDTA是最常用于植物提取的螯合剂。但是,它的缺点是它在环境中的持久性。这导致金属浸入地下水的高风险。此外,已经有迹象表明对植物和微生物具有高毒性。选择使用各种天然存在的螯合剂,例如天然低分子量有机酸(NLMWOA),环糊精(CyD),(S,S)-N,N'-乙二胺二琥珀酸(EDDS)和水解形式的羊毛。所有这些螯合剂都有一个共同的分母,它们是通过自然过程合成的,例如微生物,植物或动物,因此是可生物降解的。在浆液和柱实验中评估了上述螯合剂移动重金属的能力。通过温室中的植物提取盆栽试验成功地进行了评价螯合剂对植物毒性作用的植物毒性试验。螯合剂的生物降解程度通过oxitop和pot实验进行评估。注意降解过程中螯合剂对重金属生物利用度的影响。在NLMWOA的情况下,表征了降解所施加的螯合剂的微生物。所研究的NLMWOA,柠檬酸,草酸和酒石酸对植物的毒性低,对铜的迁移效率高。考虑到施用量更有效,在植物提取实验中没有证实其高效率,在EDTA中。其原因在于NLMWOA的高度可生物降解性。所有三个调查的NLMWOA均被相同的微生物降解,并且在降解过程中土壤中的pH值显着增加。 pH的增加伴随着重金属生物利用度的降低。 CyD揭示了对烟草的高毒性和极低的重金属吸收能力。另外,观察到高度的生物降解性。与EDTA相比,EDDS对烟草具有更高的毒性。在柱实验中,两者在动员Cd和Cu方面显示出相同的效果。在植物提取实验中,EDDS增加了Cu的吸收,但没有增加Cd的吸收,并且两种螯合物均未能提高根与茎的转运率。 EDDS的可生物降解性程度低于目前通常所说的程度。盆栽重新种植后,土壤中剩余的EDDS对幼苗的毒性延长,这对螯合辅助植物提取领域提出了新的挑战。羊毛水解物在土壤中表现出高效率的铜迁移。根据所用羊毛的水解程度,其吸收率最多可增加850%。它显示出非常高的生物降解度,而且还没有副作用,例如土壤pH值的增加和重金属生物利用度的降低。这项研究的结果表明,水解羊毛可以作为常用EDTA的完美替代品,以增强植物的提取能力。但是,其他经过测试的生物螯合剂不适合替代EDTA。

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