NOAA Climate and Global Change Postdoctoral Fellow, Boston University, Boston, MA, USA.
Biology Department and Ecology Center, Utah State University, Logan, UT, USA.
Glob Chang Biol. 2018 Apr;24(4):1417-1427. doi: 10.1111/gcb.13980. Epub 2017 Dec 1.
The availability of nitrogen (N) is a critical control on the cycling and storage of soil carbon (C). Yet, there are conflicting conceptual models to explain how N availability influences the decomposition of organic matter by soil microbial communities. Several lines of evidence suggest that N availability limits decomposition; the earliest stages of leaf litter decay are associated with a net import of N from the soil environment, and both observations and models show that high N organic matter decomposes more rapidly. In direct contrast to these findings, experimental additions of inorganic N to soils broadly show a suppression of microbial activity, which is inconsistent with N limitation of decomposition. Resolving this apparent contradiction is critical to representing nutrient dynamics in predictive ecosystem models under a multitude of global change factors that alter soil N availability. Here, we propose a new conceptual framework, the Carbon, Acidity, and Mineral Protection hypothesis, to understand the effects of N availability on soil C cycling and storage and explore the predictions of this framework with a mathematical model. Our model simulations demonstrate that N addition can have opposing effects on separate soil C pools (particulate and mineral-protected carbon) because they are differentially affected by microbial biomass growth. Moreover, changes in N availability are frequently linked to shifts in soil pH or osmotic stress, which can independently affect microbial biomass dynamics and mask N stimulation of microbial activity. Thus, the net effect of N addition on soil C is dependent upon interactions among microbial physiology, soil mineralogy, and soil acidity. We believe that our synthesis provides a broadly applicable conceptual framework to understand and predict the effect of changes in soil N availability on ecosystem C cycling under global change.
氮 (N) 的可利用性是控制土壤碳 (C) 循环和储存的关键因素。然而,目前存在相互矛盾的概念模型来解释氮可利用性如何影响土壤微生物群落对有机物的分解。有几条证据表明氮可利用性限制了分解;落叶分解的最早阶段与从土壤环境中净输入氮有关,并且观察和模型都表明,高氮有机物分解得更快。与这些发现直接相反的是,向土壤中添加无机氮通常会抑制微生物活性,这与分解的氮限制不一致。解决这一明显矛盾对于在改变土壤氮可利用性的多种全球变化因素下,在预测生态系统模型中代表养分动态至关重要。在这里,我们提出了一个新的概念框架,即碳、酸度和矿物质保护假说,以理解氮可利用性对土壤碳循环和储存的影响,并通过数学模型探索该框架的预测。我们的模型模拟表明,氮添加对单独的土壤 C 库(颗粒态和矿物质保护态碳)可能具有相反的影响,因为它们受到微生物生物量生长的不同影响。此外,氮可利用性的变化通常与土壤 pH 或渗透胁迫的变化有关,这会独立影响微生物生物量动态并掩盖氮对微生物活性的刺激作用。因此,氮添加对土壤 C 的净效应取决于微生物生理学、土壤矿物学和土壤酸度之间的相互作用。我们相信,我们的综合研究为理解和预测全球变化下土壤氮可利用性变化对生态系统碳循环的影响提供了一个广泛适用的概念框架。