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Consequences of land use change from conventional agriculture to perennial grassland for soil carbon and nitrogen dynamics.

机译:由于土壤碳和氮的动态变化,土地利用的后果从常规农业转变为多年生草地。

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Land use change, including the conversion of agricultural land to perennial grassland, alters levels of soil organic matter (SOM). SOM influences soil moisture, structure, and nutrient supply, and it helps to regulate atmospheric carbon dioxide concentrations. SOM formation is therefore a key process to understanding ecosystem development, yet little is known about the rate, pattern, and type of SOM formed on decadal time scales. In addition, few studies have examined the role of vegetation and soil texture on SOM accumulation at this time scale. I used 40-year chronosequences established on former agricultural fields depleted in SOM that differed in perennial grassland species used to establish vegetation and soil parent material to determine rates and patterns of SOM accumulation, changes in nitrogen (N) transformation, and changes in soil structure over time. I also evaluated how vegetation type and soil clay concentration affect these processes.; On glacial till, the rate of soil organic carbon (SOC) accumulation was 62.0 g−1 m−2 y−1. This linear rate of SOC accumulation did not slow as levels of SOC increased, and it will take 55–75 years for former agricultural fields to attain levels of SOC equal to those of unplowed native prairie. Both labile soil carbon (C) with a short turnover time, as measured by microbial biomass C, light fraction C, and a laboratory incubation, and recalcitrant soil C with a long turnover time, as measured by unhydrolyzable C, pools began to increase immediately after cessation of agriculture, although recalcitrant C pools increased faster. This suggests that some of the new C formed is stable. Several different methods of measuring labile SOC correspond to one another, although the absolute value determined by different techniques varied by an order of magnitude. Vegetation type and clay concentration influenced potential net N mineralization and soil aggregate size, but not soil C pools or dynamics. This work suggests that former agricultural fields are a temporally predictable C sink that will be saturated within a century, and that vegetation and soil texture have minimal capacity to alter the rate of SOM accumulation on these fields.
机译:土地用途的变化,包括将农业用地转变为多年生草地,都会改变土壤有机质(SOM)的水平。 SOM影响土壤水分,结构和养分供应,并有助于调节大气中的二氧化碳浓度。因此,SOM的形成是理解生态系统发展的关键过程,但对以年代为单位的时间尺度上形成的SOM的速度,模式和类型知之甚少。此外,很少有研究检查植被和土壤质地在此时间尺度上对SOM积累的作用。我使用了在SOM枯竭的以前的农业领域上建立的40年时间序列,这些序列不同于用于建立植被和土壤母体的多年生草地物种,以确定SOM积累的速率和模式,氮(N)转化的变化以及土壤结构的变化随着时间的推移。我还评估了植被类型和土壤黏土浓度如何影响这些过程。在冰川耕作上,土壤有机碳(SOC)累积速率为62.0 g -1 m -2 y -1 。 SOC累积的线性速率并不会随着SOC的增加而减慢,并且以前的农田要达到等于未耕种的原始大草原的SOC的水平需要55-75年。通过微生物生物量C,轻质馏分C和实验室温育测量的具有较短周转时间的不稳定土壤碳(C)和具有不可水解C的具有较长周转时间的顽固土壤C都立即开始增加停止农业后,尽管顽固的碳库增长更快。这表明形成的一些新的C是稳定的。尽管通过不同技术确定的绝对值变化了一个数量级,但几种不同的测量不稳定SOC的方法相互对应。植被类型和黏土浓度影响潜在的净氮矿化和土壤团聚体大小,但不影响土壤碳库或动力学。这项工作表明,以前的农田是一个在时间上可预测的碳汇,它将在一个世纪之内饱和,并且植被和土壤质地改变这些土地上SOM积累速率的能力很小。

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