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Long-term elevation of temperature affects organic N turnover and associated N2O emissions in a permanent grassland soil

机译:长期温度升高会影响永久性草地土壤中的有机氮转化和相关的N2O排放

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Over the last century an increase in mean soil surface temperature has been observed, and it is predicted to increase further in the future. In order to evaluate the legacy effects of increased temperature on both nitrogen?(N) transformation rates in the soil and nitrous oxide?(N2O) emissions, an incubation experiment and modelling approaches were combined. Based on previous observations that gross N transformations in soils are affected by long-term elevated-temperature treatments we hypothesized that any associated effects on gaseous N emissions (e.g.?N2O) can be confirmed by a change in the relative emission rates from various pathways. Soils were taken from a long-term in situ warming experiment on temperate permanent grassland. In this experiment the soil temperature was elevated by 0 (control), 1, 2?or 3?°C (four?replicates per treatment) using IR (infrared) lamps over a period of 6 years. The soil was subsequently incubated under common conditions (20?°C and 50?% humidity) and labelled as NO315NH4 Gly, 15NO3NH4 Gly or NO3NH4 15N-Gly. Soil extractions and N2O emissions were analysed using a 15N tracing model and source-partitioning model. Both total inorganic N (NO3??+?NH4+) and NO3? contents were higher in soil subjected to the +2?and +3?°C temperature elevations (pre- and post-incubation). Analyses of N transformations using a 15N tracing model showed that, following incubation, gross organic (but not inorganic) N transformation rates decreased in response to the prior soil warming treatment. This was also reflected in reduced N2O emissions associated with organic N oxidation and denitrification. Furthermore, a newly developed source-partitioning model showed the importance of oxidation of organic N as a source of N2O. In conclusion, long-term soil warming can cause a legacy effect which diminishes organic N turnover and the release of N2O from organic N and denitrification.
机译:在上个世纪中,已经观察到平均土壤表面温度的升高,并且预计将来还会进一步升高。为了评估温度升高对土壤中氮(N)转化速率和一氧化二氮(N2O)排放的遗留影响,将孵化实验和建模方法结合起来。基于以前的观察,土壤中的总氮转化受长期高温处理的影响,我们假设对气态氮排放(例如?N2O)的任何相关影响都可以通过各种途径的相对排放速率的变化来证实。土壤是在温带永久性草地上进行的长期就地变暖实验获得的。在该实验中,使用IR(红外)灯将土壤温度在6年内升高了0(对照),1、2?或3?C(每次处理重复4次)。随后将土壤在普通条件下(20°C和50%湿度)孵育,并标记为NO315NH4 Gly,15NO3NH4 Gly或NO3NH4 15N-Gly。使用15N追踪模型和源划分模型对土壤提取物和N2O排放进行了分析。总无机氮(NO 3 + + NH 4 +)和NO 3-均在+2?和+3?C温度升高(培养前和培养后)下,土壤中的含量较高。使用15N示踪模型对N转化进行的分析表明,孵育后,响应于先前的土壤变暖处理,总有机(而非无机)N转化速率降低。这也反映在与有机氮氧化和反硝化有关的N2O排放减少上。此外,新开发的源分配模型显示出有机氮氧化为N2O的重要性。总之,长期的土壤变暖会导致遗留效应,从而减少有机氮的转化以及有机氮和反硝化过程中N2O的释放。

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