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Sensitivity of organic matter decomposition to warming varies with its quality

机译:有机物分解对变暖的敏感性随其质量而变化

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The relationship between organic matter (OM) lability and temperature sensitivity is disputed, with recent observations suggesting that responses of relatively more resistant OM to increased temperature could be greater than, equivalent to, or less than responses of relatively more labile OM. This lack of clear understanding limits the ability to forecast carbon (C) cycle responses to temperature changes. Here, we derive a novel approach (denoted Q(10-q)) that accounts for changes in OM quality during decomposition and use it to analyze data from three independent sources. Results from new laboratory soil incubations (labile Q(10-q)=2.1 +/- 0.2; more resistant Q(10-q)=3.8 +/- 0.3) and reanalysis of data from other soil incubations reported in the literature (labile Q(10-q)=2.3; more resistant Q(10-q)=3.3) demonstrate that temperature sensitivity of soil OM decomposition increases with decreasing soil OM lability. Analysis of data from a cross-site, field litter bag decomposition study (labile Q(10-q)=3.3 +/- 0.2; resistant Q(10-q)=4.9 +/- 0.2) shows that litter OM follows the same pattern, with greater temperature sensitivity for more resistant litter OM. Furthermore, the initial response of cultivated soils, presumably containing less labile soil OM (Q(10-q)=2.4 +/- 0.3) was greater than that for undisturbed grassland soils (Q(10-q)=1.7 +/- 0.1). Soil C losses estimated using this approach will differ from previous estimates as a function of the magnitude of the temperature increase and the proportion of whole soil OM comprised of compounds sensitive to temperature over that temperature range. It is likely that increased temperature has already prompted release of significant amounts of C to the atmosphere as CO2. Our results indicate that future losses of litter and soil C may be even greater than previously supposed.
机译:有机物(OM)的不稳定性和温度敏感性之间的关系存在争议,最近的观察表明,相对更耐性的OM对升高的温度的响应可能大于,等于或小于相对较不稳定的OM的响应。缺乏清晰的了解限制了预测碳(C)循环对温度变化的响应的能力。在这里,我们推导了一种新颖的方法(称为Q(10-q)),该方法解决了分解过程中OM质量的变化,并使用它来分析来自三个独立来源的数据。新的实验室土壤培养的结果(不稳定的Q(10-q)= 2.1 +/- 0.2;更强的Q(10-q)= 3.8 +/- 0.3)和文献中报道的其他土壤培养的数据重新分析(不稳定Q(10-q)= 2.3;更强的Q(10-q)= 3.3)表明,土壤OM分解的温度敏感性随着土壤OM不稳定性的降低而增加。跨站点野外垃圾袋分解研究(不稳定的Q(10-q)= 3.3 +/- 0.2;抗性Q(10-q)= 4.9 +/- 0.2)的数据分析表明,垃圾OM遵循相同的图案,具有更高的温度敏感度,可更好地抵抗垫料OM。此外,耕作土壤的初始响应(大概包含不稳定的土壤有机质(Q(10-q)= 2.4 +/- 0.3))比未受干扰的草地土壤(Q(10-q)= 1.7 +/- 0.1)大。 )。使用这种方法估算的土壤碳损失量将不同于先前的估算值,这是温度升高幅度和该温度范围内对温度敏感的化合物组成的整个土壤有机质所占比例的函数。升高的温度很可能已经促使大量的二氧化碳以二氧化碳的形式释放到大气中。我们的结果表明,枯枝落叶和土壤C的未来损失可能甚至比以前预期的还要大。

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