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首页> 外文期刊>Soil Science and Plant Nutrition >Do tillage and conversion of grassland to cropland always deplete soil organic carbon?
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Do tillage and conversion of grassland to cropland always deplete soil organic carbon?

机译:耕作和转化草地到农田总是耗尽土壤有机碳吗?

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摘要

Conversion of grassland to cropland is widely reported to deplete soil organic carbon (SOC) largely due to tillage effects on the decomposition of SOC. However, most studies report on long-term changes in SOC following the conversion and little is known about the changes in the short term. Net ecosystem carbon budget (NECB) measures the difference between total C input (i.e., manure, above- and below-ground plant residues) and C loss through heterotrophic respiration (RH). However, most studies that report temporal SOC do not report other components of the NECB like RH, total C inputs and often do not include the cumulative annualized change of these components. This review evaluated the change in C input, RH, NECB and SOC after conversion of permanent/continuous grassland to cropland within 5 years after the conversion. We also reviewed and compared no-tillage and conventional tillage on SOC storage and accumulation. Total C input was higher in grassland than cropland largely due to high root biomass, as opposed to aboveground residue, and therefore grassland tended to have higher NECB. Despite higher NECB in grassland, the SOC stocks in cropland (cornfield) converted from grassland were greater than that in continuous grassland within first 2?3 years of conversion. The combination of manure C addition and tillage in cropland showed potential to maintain NECB and increase SOC. Within the continuous grassland C addition alone increased NECB but did not result in a corresponding increase in SOC. Residue retention and manure addition are recognized as good practices for increasing SOC, this study however, shows that combining them with occasional tillage, especially in managed grasslands, could increase the rate of SOC storage in soils.
机译:据据报道,Grassland对农田的转换,耗尽土壤有机碳(SoC),主要是由于对SoC分解的耕作效应。然而,大多数研究报告转换后的SOC的长期变化报告以及短期内的变化所知。净生态系统碳预算(NECB)测量总C输入(即,粪便,粪便,低于地下植物残留物)和通过异养呼吸(RH)的C损失之间的差异。但是,报告时间SoC的大多数研究不报告NECB等其他组件,如RH,总C输入,通常不包括这些组件的累积年化变更。该审查评估了在转换后5年内转换永久性/连续草原的C输入,RH,NECB和SOC的变化。我们还审查和比较了SoC储存和积累的无耕作和传统耕作。由于高根生物量而不是地上残留物,Grandland的总C投入大于农作物,而且由于地上残留物,因此草地倾向于具有更高的NECB。尽管草原上的NECB更高,但从草原转换的农田(玉米田)的SoC股比在前2岁的连续草原上大于连续2个?3年的转换。粪便C的组合和耕作在农田中显示出维持NECB并增加SOC。在连续草地内,C添加单独增加NECB但未导致SoC的相应增加。然而,残留保留和粪便加入作为增加SoC的良好实践,这项研究表明,将它们与偶尔耕作相结合,特别是在管理草原上,可以提高土壤中的SoC储存速度。

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