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Changes in the temperature sensitivity of SOM decomposition with grassland succession: implications for soil C sequestration

机译:草地演替过程中SOM分解的温度敏感性变化:对土壤固碳的影响

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摘要

Understanding the temperature sensitivity (Q10) of soil organic matter (SOM) decomposition is important for predicting soil carbon (C) sequestration in terrestrial ecosystems under warming scenarios. Whether Q10 varies predictably with ecosystem succession and the ways in which the stoichiometry of input SOM influences Q10 remain largely unknown. We investigate these issues using a grassland succession series from free-grazing to 31-year grazing-exclusion grasslands in Inner Mongolia, and an incubation experiment performed at six temperatures (0, 5, 10, 15, 20, and 25°C) and with four substrates: control (CK), glucose (GLU), mixed grass leaf (GRA), and Medicago falcata leaf (MED). The results showed that basal soil respiration (20°C) and microbial biomass C (MBC) logarithmically decreased with grassland succession. Q10 decreased logarithmically from 1.43 in free-grazing grasslands to 1.22 in 31-year grazing-exclusion grasslands. Q10 increased significantly with the addition of substrates, and the Q10 levels increased with increase in N:C ratios of substrate. Moreover, accumulated C mineralization was controlled by the N:C ratio of newly input SOM and by incubation temperature. Changes in Q10 with grassland ecosystem succession are controlled by the stoichiometry of newly input SOM, MBC, and SOM quality, and the combined effects of which could partially explain the mechanisms underlying soil C sequestration in the long-term grazing-exclusion grasslands in Inner Mongolia, China. The findings highlight the effect of substrate stoichiometry on Q10 which requires further study.
机译:了解土壤有机质(SOM)分解的温度敏感性(Q10)对于预测变暖情况下陆地生态系统中的碳(C)固存具有重要意义。 Q10是否随生态系统演替而发生可预测的变化以及输入SOM的化学计量影响Q10的方式仍然很大程度上未知。我们使用内蒙古从自由放牧到31年放牧的草地的草地演替系列研究了这些问题,并在六个温度(0、5、10、15、20和25°C)下进行了孵化实验,具有四种底物:对照(CK),葡萄糖(GLU),混合草叶(GRA)和苜蓿苜蓿(Medicago falcata)叶(MED)。结果表明,草地演替后,基础土壤呼吸(20℃)和微生物量碳(MBC)呈对数下降趋势。第10季度的对数从自由放牧草地的1.43下降到31年放牧草地的1.22。 Q10随着底物的添加而显着增加,而Q10水平则随着底物N:C比率的增加而增加。此外,累积的碳矿化程度由新输入的SOM的N:C比和培养温度控制。 Q10随草地生态系统演替的变化受新输入的SOM,MBC和SOM质量的化学计量控制,其综合作用可部分解释内蒙古长期放牧-排斥草地固碳的基本机制,中国。这些发现突出了底物化学计量对Q10的影响,需要进一步研究。

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