应用现代环境技术修复土壤覆盖层重金属和放射性核素污染

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In the first stage, geochemical survey of the territory of the landfill is carried out before the pollutants are introduced; an artificial GB is created from materials of industrial waste – iron sulfate (FeSO4 ∙ nH2O); the contaminated sites of the landfill are identified by sampling soil for analysis of the contents of НM. In the second stage of the experiment, the characteristics of the artificial artificial GB are determined and the process of soil phytoremediation using special agrocenoses is investigated. Quantitative determination of the content of НM in the selected samples is performed on a SRM-25 RF spectrometer. To analyze the content of HM, the plant material is dried to air-dry state, ground to a powdered state and pelleted under a press. Results. The analysis of the performed researches of phytoremediation technologies makes it possible to state with confidence that the most priority is the combination of phytoremediation technologies with the cessation of migration and concentration of НМ with artificial GB. As a result of the conducted research the following results are obtained: – existing phytotechnologies of soil purification are being improved due to the combination of artificially created GBs with selected agrocenoses; – it is established that the most representative pollutants of landfill soils are – Cu and Zn; – the optimal composition of agrocenoses for soil phytoremediation is determined: calendula, annual lupine and dwarf sunflower, which allow to obtain representative results on the efficiency of Cu and Zn phytochemical extraction. Maximum concentrations of Cu are recorded in sunflower tissues; high concentrations of Zn compared to Cu – in the tissues of calendula and lupine. 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引用次数: 0

摘要

问题的表述。本文致力于改进现有的利用人工地球化学屏障(GB)修复重金属污染土壤的技术(НM)。本文的目的包括两个方面:开发和改进利用GB净化土壤的现有植物技术;通过特定的НM确定土壤污染的最佳植物修复农病培养物。材料和方法。利用特殊农藓提供土壤植物修复的能力作为主要工作工具。污染VM土壤的植物修复技术包括准备和修复两个阶段。第一阶段,在污染物进入前对垃圾填埋场进行地界地球化学调查;以工业废料硫酸铁(FeSO4∙nH2O)为原料制备人工GB;通过采样土壤来分析НM的含量,确定了垃圾填埋场的污染地点。在第二阶段的实验中,确定了人工人工GB的特性,并研究了利用特殊的农藓类植物修复土壤的过程。在所选样品中НM的含量在SRM-25射频光谱仪上进行定量测定。为了分析HM的含量,将植物材料干燥到风干状态,研磨成粉末状态,并在压力下成粒。通过对已开展的植物修复技术研究的分析,我们可以自信地说,最优先的是植物修复技术与停止迁移和НМ与人工GB浓度的结合。研究结果表明:-人工合成的GBs与选定的agrocenses相结合,改善了现有的土壤净化植物技术;-确定了填埋场土壤中最具代表性的污染物是- Cu和Zn; -确定了土壤修复中agrocenses的最佳组成:金盏菊、一年生羽扇豆和矮向日葵,从而获得具有代表性的Cu和Zn植物化学提取效率的结果。在向日葵组织中记录了Cu的最大浓度;与铜相比,金盏花和羽扇豆的组织中锌的浓度更高。实验的最后一部分是在植被的最后阶段消除土壤萎蔫病,土壤萎蔫病在其组成中积累了高浓度的Cu和Zn。据估计,在几个消除这种混耕作物的周期内,土壤污染物的含量应达到可接受的水平。具有科学新颖性和现实意义。科学新颖性——由于植物修复技术的改进而恢复土壤生态特性的过程得到了科学的证实。所得结果的实际应用是在以铜和锌为主污染的地区实施所提出的土壤修复技术。
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Remediation of contaminated heavy metals and radionuclides of soil covering with the application of modern environmental technologies
Formulation of the problem. The article is dedicated to the improvement of existing technologies for the restoration of soil contaminated with heavy metals (НM) by phytoremediation using artificially created geochemical barriers (GB). The purpose of the article includes 2 aspects: to develop and improve existing phytotechnology of soil purification through the use of GB; determine agrocenosis cultures for optimal phytoremediation of soil contamination by specific НM. Materials and methods. The ability of special agrocenoses to provide soil phytoremediation is used as the main working tool. Phytoremediation technology of contaminated VM soils involves two stages: preparatory and phytoremediation. In the first stage, geochemical survey of the territory of the landfill is carried out before the pollutants are introduced; an artificial GB is created from materials of industrial waste – iron sulfate (FeSO4 ∙ nH2O); the contaminated sites of the landfill are identified by sampling soil for analysis of the contents of НM. In the second stage of the experiment, the characteristics of the artificial artificial GB are determined and the process of soil phytoremediation using special agrocenoses is investigated. Quantitative determination of the content of НM in the selected samples is performed on a SRM-25 RF spectrometer. To analyze the content of HM, the plant material is dried to air-dry state, ground to a powdered state and pelleted under a press. Results. The analysis of the performed researches of phytoremediation technologies makes it possible to state with confidence that the most priority is the combination of phytoremediation technologies with the cessation of migration and concentration of НМ with artificial GB. As a result of the conducted research the following results are obtained: – existing phytotechnologies of soil purification are being improved due to the combination of artificially created GBs with selected agrocenoses; – it is established that the most representative pollutants of landfill soils are – Cu and Zn; – the optimal composition of agrocenoses for soil phytoremediation is determined: calendula, annual lupine and dwarf sunflower, which allow to obtain representative results on the efficiency of Cu and Zn phytochemical extraction. Maximum concentrations of Cu are recorded in sunflower tissues; high concentrations of Zn compared to Cu – in the tissues of calendula and lupine. The final part of the experiment is the elimination of agrocenosis at the final stage of vegetation, which accumulates in its composition high concentrations of Cu and Zn. It is estimated that in several cycles of elimination of such agrocenoses, the content of soil contaminants should reach acceptable levels. Scientific novelty and practical significance. Scientific novelty – the process of restoration of ecological properties of soils due to the improvement of phytoremediation technology is scientifically substantiated. The practical application of the obtained results is the implementation of the proposed technology of soil restoration in territories contaminated mainly by Cu and Zn.
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