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首页> 外文期刊>Environmental Science and Pollution Research >Effects of long-term radionuclide and heavy metal contamination on the activity of microbial communities, inhabiting uranium mining impacted soils
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Effects of long-term radionuclide and heavy metal contamination on the activity of microbial communities, inhabiting uranium mining impacted soils

机译:长期放射性核素和重金属污染对居住在铀矿开采受影响土壤中的微生物群落活动的影响

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Ore mining and processing have greatly altered ecosystems, often limiting their capacity to provide ecosystem services critical to our survival. The soil environments of two abandoned uranium mines were chosen to analyze the effects of long-term uranium and heavy metal contamination on soil microbial communities using dehydrogenase and phosphatase activities as indicators of metal stress. The levels of soil contamination were low, ranging from 'precaution' to 'moderate', calculated as Nemerow index. Multivariate analyses of enzyme activities revealed the following: (i) spatial pattern of microbial endpoints where the more contaminated soils had higher dehydrogenase and phosphatase activities, (ii) biological grouping of soils depended on both the level of soil contamination and management practice, (iii) significant correlations between both dehydrogenase and alkaline phosphatase activities and soil organic matter and metals (Cd, Co, Cr, and Zn, but not U), and (iv) multiple relationships between the alkaline than the acid phosphatase and the environmental factors. The results showed an evidence of microbial tolerance and adaptation to the soil contamination established during the long-term metal exposure and the key role of soil organic matter in maintaining high microbial enzyme activities and mitigating the metal toxicity. Additionally, the results suggested that the soil microbial communities are able to reduce the metal stress by intensive phosphatase synthesis, benefiting a passive environmental remediation and provision of vital ecosystem services.
机译:矿石开采和加工极大地改变了生态系统,常常限制了它们提供对我们的生存至关重要的生态系统服务的能力。选择了两个废弃铀矿的土壤环境,以脱氢酶和磷酸酶活性为金属胁迫指标,分析了长期铀和重金属污染对土壤微生物群落的影响。土壤污染水平很低,从“预防”到“中等”,以Nemerow指数计算。酶活性的多变量分析表明:(i)受污染更严重的土壤具有较高的脱氢酶和磷酸酶活性的微生物终点的空间格局,(ii)土壤的生物分类取决于土壤污染水平和管理实践,(iii )脱氢酶和碱性磷酸酶活性与土壤有机质和金属(Cd,Co,Cr和Zn,而不是U)之间存在显着相关性,并且(iv)碱性磷酸酶比酸性磷酸酶与环境因素之间存在多重关系。结果显示出微生物耐受性和对长期金属暴露期间建立的土壤污染物的适应性证据,以及土壤有机质在维持高微生物酶活性和减轻金属毒性方面的关键作用。此外,结果表明,土壤微生物群落能够通过密集的磷酸酶合成来减轻金属胁迫,从而有利于被动的环境修复和提供重要的生态系统服务。

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