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The response of heterotrophic CO2 flux to soil warming

机译:异养CO2通量对土壤变暖的响应

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摘要

In a forest ecosystem at steady state, net carbon (C) assimilation by plants and C loss through soil and litter decomposition by heterotrophic organisms are balanced. However, a perturbation to the system, such as increased mean soil temperature, will lead to faster decay, enhancing CO2 release from decomposers, and thus upsetting the balance. Recent in situ experiments have indicated that the stimulation of soil respiration following a step increase in annual average soil temperature declines over time. One possible explanation for this decline may be changes in substrate availability. This hypothesis is examined by using the ecosystem model G'DAY, which simulates C and nitrogen (N) dynamics in plants and soil.We applied the model to observations from a soil-warming experiment in a Norway spruce (Picea abies (L.) Karst.) stand by simulating a step increase of soil temperature. The model provided a good qualitative reproduction of the observed reduction of heterotrophic respiration (R-h) under sustained warming. The simulations showed how the combined effects of faster turnover and reduced substrate availability lead to a transient increase of R-h. The simulated annual increase in R-h from soil was 60% in the first year after perturbation but decreased to 30% after a decade.One conclusion from the analysis of the simulations is that R-h can decrease even though the temperature response function for decomposition remains unchanged. G'DAY suggests that acclimation of R-h to soil warming is partly an effect of substrate depletion of labile C pools during the first decade of warming as a result of accelerated rates of mineralization. The response is attributed mainly to changing levels of C in pools with short time constants, reflecting the importance of high-quality soil C fractions. Changes of the structure or physiology of the decomposer community were not invoked. Therefore, it becomes a question of definition whether the simulated dynamics of the declining response of CO2 release to the warming should be named acclimation or seen as a natural part of the system dynamics.
机译:在稳定的森林生态系统中,植物的净碳(C)同化与土壤和异养生物分解的凋落物所造成的碳损失是平衡的。但是,对系统的干扰(例如平均土壤温度升高)将导致更快的衰减,从而增加分解器释放的CO2,从而破坏平衡。最近的原位实验表明,随着年平均土壤温度的逐步升高,土壤呼吸的刺激随着时间的推移而下降。对于这种下降的一种可能的解释可能是基材利用率的变化。通过使用生态系统模型G'DAY检验了该假设,该模型模拟了植物和土壤中的碳和氮(N)动态。我们将该模型应用于挪威云杉(Picea abies(L.)喀斯特地区)模拟土壤温度的逐步升高。该模型对观察到的持续变暖下异养呼吸(R-h)减少提供了良好的定性再现。仿真表明,更快的周转速度和降低的基板利用率会共同导致R-h的瞬时增加。模拟的土壤中R-h的年均增加量在扰动后的第一年为60%,但在十年后降至30%。从模拟分析得出的结论是,即使分解的温度响应函数保持不变,R-h仍会减少。 G'DAY认为,由于矿化速度加快,在变暖的头十年中,R-h适应土壤变暖部分是不稳定的C池底物耗竭的影响。响应主要归因于时间常数短的池中碳水平的变化,反映了高质量土壤碳组分的重要性。没有调用分解者社区的结构或生理变化。因此,定义CO 2释放对气候变暖的下降响应的模拟动力学是否应被称为驯化或被视为系统动力学的自然组成部分,就成为了一个定义问题。

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