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Soil Iron Content as a Predictor of Carbon and Nutrient Mobilization in Rewetted Fens

机译:土壤中的铁含量可预测重新加湿的茴香中碳和营养动员

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摘要

Rewetted, previously drained fens often remain sources rather than sinks for carbon and nutrients. To date, it is poorly understood which soil characteristics stimulate carbon and nutrient mobilization upon rewetting. Here, we assess the hypothesis that a large pool of iron in the soil negatively affects fen restoration success, as flooding-induced iron reduction (Fe3+ to Fe2+) causes a disproportionate breakdown of organic matter that is coupled with a release of inorganic compounds. We collected intact soil cores in two iron-poor and two iron-rich drained fens, half of which were subjected to a rewetting treatment while the other half was kept drained. Prolonged drainage led to the mobilization of nitrate (NO3-, > 1 mmol L-1) in all cores, regardless of soil iron content. In the rewetted iron-rich cores, a sharp increase in pore water iron (Fe) concentrations correlated with concentrations of inorganic carbon (TIC, > 13 mmol L-1) and dissolved organic carbon (DOC, > 16 mmol L-1). Additionally, ammonium (NH4+) accumulated up to phytotoxic concentrations of 1 mmol L-1 in the pore water of the rewetted iron-rich cores. Disproportionate mobilization of Fe, TIC, DOC and NH4+ was absent in the rewetted iron-poor cores, indicating a strong interaction between waterlogging and iron-mediated breakdown of organic matter. Concentrations of dissolved phosphorus (P) rose slightly in all cores upon rewetting, but remained low throughout the experiment. Our results suggest that large pools of iron in the top soil of drained fens can hamper the restoration of the fen’s sink-service for ammonium and carbon upon rewetting. We argue that negative effects of iron should be most apparent in fens with fluctuating water levels, as temporary oxygenation allows frequent regeneration of Fe3+. We conclude that rewetting of iron-poor fens may be more feasible for restoration.
机译:经过重新润湿的,以前沥干的fen通常仍然是碳和养分的来源,而不是汇。迄今为止,人们对哪种土壤特性在重新润湿后会刺激碳和养分的迁移知之甚少。在这里,我们评估以下假设:土壤中大量铁元素对洪水恢复成功有负面影响,因为洪水导致铁还原(Fe 3 + 到Fe 2 + )导致有机物分解不成比例,并释放出无机化合物。我们在两个贫铁和两个富铁排水口中收集了完整的土壤核心,其中一半进行了重新湿润处理,而另一半则保持了排水状态。无论土壤中的铁含量如何,长时间的排水都会使所有岩心中的硝酸盐(NO3 -,> 1 mmol L -1 )动员。在再润湿的富铁岩心中,孔隙水中铁(Fe)浓度的急剧增加与无机碳(TIC,> 13 mmol L -1 )和溶解的有机碳(DOC, 16 mmol L -1 )。此外,铵(NH4 + )在重新润湿的富含铁的岩心的孔隙水中积累的植物毒性浓度高达1 mmol L -1 。再润湿的贫铁岩心中不存在过多的Fe,TIC,DOC和NH4 + 动员,这表明涝渍与铁介导的有机物分解之间存在很强的相互作用。重新润湿后,所有核心的溶解磷(P)浓度均略有上升,但在整个实验过程中仍保持较低水平。我们的结果表明,排水后的的表层土壤中大量铁可能会阻碍重新润湿后tting对铵和碳的沉没服务的恢复。我们认为,在水位波动的环境中,铁的负面影响最明显,因为暂时的氧合可以频繁地再生Fe 3 + 。我们得出的结论是,对贫铁的re进行重新润湿对于恢复可能更为可行。

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