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首页> 外文期刊>Global change biology >Soil-specific response functions of organic matter mineralization to the availability of labile carbon.
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Soil-specific response functions of organic matter mineralization to the availability of labile carbon.

机译:有机物矿化对土壤中不稳定碳的可用性的土壤特异性响应函数。

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Soil organic matter (SOM) mineralization processes are central to the functioning of soils in relation to feedbacks with atmospheric CO2 concentration, to sustainable nutrient supply, to structural stability and in supporting biodiversity. Recognition that labile C-inputs to soil (e.g. plant-derived) can significantly affect mineralization of SOM ('priming effects') complicates prediction of environmental and land-use change effects on SOM dynamics and soil C-balance. The aim of this study is to construct response functions for SOM priming to labile C (glucose) addition rates, for four contrasting soils. Six rates of glucose (3 atm% 13C) addition (in the range 0-1 mg glucose g-1 soil day-1) were applied for 8 days. Soil CO2 efflux was partitioned into SOM- and glucose-derived components by isotopic mass balance, allowing quantification of SOM priming over time for each soil type. Priming effects resulting from pool substitution effects in the microbial biomass ('apparent priming') were accounted for by determining treatment effects on microbial biomass size and isotopic composition. In general, SOM priming increased with glucose addition rate, approaching maximum rates specific for each soil (up to 200%). Where glucose additions saturated microbial utilization capacity (>0.5 mg glucose g-1 soil), priming was a soil-specific function of glucose mineralization rate. At low to intermediate glucose addition rates, the magnitude (and direction) of priming effects was more variable. These results are consistent with the view that SOM priming is supported by the availability of labile C, that priming is not a ubiquitous function of all components of microbial communities and that soils differ in the extent to which labile C stimulates priming. That priming effects can be represented as response functions to labile C addition rates may be a means of their explicit representation in soil C-models. However, these response functions are soil-specific and may be affected by several interacting factors at lower addition rates.
机译:土壤有机物(SOM)的矿化过程对于土壤的功能至关重要,涉及大气CO 2 浓度的反馈,可持续的营养供应,结构的稳定性以及对生物多样性的支持。认识到土壤中不稳定的碳输入(例如植物来源)会严重影响SOM的矿化作用(``启动效应''),这使得环境和土地利用变化对SOM动态和土壤C平衡的影响的预测变得复杂。这项研究的目的是针对四种对比土壤,构建SOM引发对不稳定的C(葡萄糖)添加速率的响应函数。六种添加葡萄糖(3 atm% 13 C)的速率(在0-1 mg葡萄糖g -1 土壤日 -1 范围内)申请了8天。通过同位素质量平衡将土壤CO 2 外排分为SOM和葡萄糖衍生成分,从而可以对每种土壤随时间的SOM启动进行定量。通过确定对微生物生物量大小和同位素组成的处理效应,可以解释由微生物生物量中库替代效应(“表观引发”)产生的引发效应。通常,SOM引发随葡萄糖添加速率的增加而增加,接近每种土壤的最大最大速率(最高200%)。当葡萄糖添加达到饱和微生物利用能力(> 0.5 mg葡萄糖g -1 土壤)时,引发是土壤中葡萄糖矿化速率的特定函数。在低至中等的葡萄糖添加速率下,启动作用的大小(和方向)更加可变。这些结果与以下观点是一致的:不稳定的C的可用性支持SOM引发,引发不是微生物群落所有组成部分的普遍功能,土壤在不稳定的C刺激引发的程度上也不同。引发效应可以表示为对不稳定碳添加速率的响应函数,这可能是其在土壤C模型中明确表示的一种方式。但是,这些响应函数是特定于土壤的,并且在较低的添加速率下可能会受到多种相互作用因素的影响。

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