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Iron mineral dissolution releases iron and associated organic carbon during permafrost thaw

机译:铁矿物溶解在Puxafrost解冻期间释放铁和相关的有机碳

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It has been shown that reactive soil minerals, specifically iron(III) (oxyhydr)oxides, can trap organic carbon in soils overlying intact permafrost, and may limit carbon mobilization and degradation as it is observed in other environments. However, the use of iron(III)-bearing minerals as terminal electron acceptors in permafrost environments, and thus their stability and capacity to prevent carbon mobilization during permafrost thaw, is poorly understood. We have followed the dynamic interactions between iron and carbon using a space-for-time approach across a thaw gradient in Abisko (Sweden), where wetlands are expanding rapidly due to permafrost thaw. We show through bulk (selective extractions, EXAFS) and nanoscale analysis (correlative SEM and nanoSIMS) that organic carbon is bound to reactive Fe primarily in the transition between organic and mineral horizons in palsa underlain by intact permafrost (41.8?±?10.8?mg carbon per g soil, 9.9 to 14.8% of total soil organic carbon). During permafrost thaw, water-logging and O 2 limitation lead to reducing conditions and an increase in abundance of Fe(III)-reducing bacteria which favor mineral dissolution and drive mobilization of both iron and carbon along the thaw gradient. By providing a terminal electron acceptor, this rusty carbon sink is effectively destroyed along the thaw gradient and cannot prevent carbon release with thaw.
机译:已经表明,反应性土壤矿物质,特别是铁(III)(氧水)氧化物,可以将有机碳捕获覆盖完整的永久腺润,并且可以限制在其他环境中观察到的碳动员和降解。然而,使用铁(iii) - Bearing矿物作为多年冻土环境中的终端电子受体,因此它们在永久冻土中防止碳动员的稳定性和能力较差地理解。我们遵循铁和碳之间的动态相互作用,在Abisko(瑞典)中的一个梯度横跨Abisko(瑞典)的时间空间方法,湿地由于Permafrost解冻而迅速扩张。我们通过散装(选择性提取,EXAF)和纳米级分析(相关性SEM和纳米粒子)展示有机碳主要是反应性Fe,主要是通过完整的Permafrost(41.8?±10.8×10.8?mg的Palsa内部的有机和矿物视野之间的过渡每G土壤的碳,占总土壤有机碳的9.9%至14.8%)。在Pumafrost解冻期间,水测井和O 2限制导致降低条件和丰富的Fe(III)级细菌的增加,这些细菌有利于矿物溶解和沿着解冻梯度驾驶铁和碳的动员。通过提供终端电子受体,这种生锈的碳水槽沿着解冻梯度有效地破坏,无法防止碳释放。

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