首页> 外文会议>NATO Advanced Research Workshop on Environmental and Biological Risks of Hybrid Organic-Silicon Nanodevices >EVALUATION OF SUSTAINABILITY OF THE CARBON AND SILICON ECOSYSTEM: FROM NANOPARTICLES TO MACROWORLD
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EVALUATION OF SUSTAINABILITY OF THE CARBON AND SILICON ECOSYSTEM: FROM NANOPARTICLES TO MACROWORLD

机译:评估碳和硅生态系统的可持续性:从纳米颗粒到Macroworld

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Rapid development of nanotechnologies has led to a complicated problem of utilization, storage and treatment of waste nanodevices of silicon and carbon origin. The processes of physico-chemical and biogeochemical destruction of carbon—silicon—uranium nanoparticles of Chernobyl origin has been studied. The period of half-destruction assessed by leaching of different radionuclide from particles is between 5 and 25 years. Natural ecosystems are generally of carbon and silicon origin. The behavior of radionuclide in natural media is observed over a period of 20 years. For the balance calculations we have utilized the Geochemical Transition Factor (GTF) that represents the quantity of substance, which is accumulated by living matter from the area unit. The main part of total carbon is involved in biogeochemical cycles in the forest ecosystem. Anthropogenic activity leads to a considerable imbalance of carbon isotopes. The distri-bution of carbon isotopes between different biotic levels demonstrates that radiocarbon of artificial emission is substantially less bio-available than those from natural sources. The environmental ability to recovery, lies in decontamination of carbon trophic circuits, is an order of magnitude greater than the rate of natural attenuation and corresponds to the removal of artificial matter from natural silicon media. The modern sustainability of the silicon and carbon ecosystem is determined by an insignificant quantity of artificial matter involved in biogeochemical cycles.
机译:纳米技术的快速发展导致了硅和碳源性废物纳米型的使用,储存和处理的复杂问题。研究了碳 - 硅 - 铀纳米粒子的物理化学和生物地球化学破坏的方法研究。通过从颗粒中浸出不同放射性核素的半毁灭的时期在5至25岁之间。天然生态系统通常是碳和硅原产的。在20年内观察到放射性核素在天然培养基中的行为。对于平衡计算,我们利用了代表物质量的地球化学过渡因子(GTF),该物质由来自面积单位的生物累积。总碳的主要部分参与了森林生态系统中的生物地球化学循环。人为的活性导致碳同位素相当不平衡。不同的生物水平之间的碳同位素的分布性分布证明人工排放的辐射碳基本上比来自天然来源的生物可用。恢复环境能力,位于碳疏通电路的净化,是大于自然衰减速率的数量级,并且对应于来自天然硅介质的人造物质的去除。硅和碳生态系统的现代可持续性由参与生物地球化学循环中的人造物质的不显着量决定。

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