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Sensitivity of soil carbon dynamics to nitrogen and phosphorus enrichment in an alpine meadow

机译:土壤碳动力学对高山草甸氮素和磷富集的敏感性

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Anthropogenic activities and atmospheric deposition have increased the nitrogen (N) and phosphorus (P) inputs to terrestrial ecosystems, which can significantly alter ecosystem carbon cycling. To better understand the mechanisms of soil organic carbon (SOC) responding to nutrient fertilization, we measured physical fractions (by particle-size fractionation) and chemical composition (by solid-state C-13 NMR spectroscopy) of SOC, plant biomass and nutrient concentration, soil chemistry, microbial biomass and community composition after 10 years of N and P addition in an alpine meadow on the Tibetan Plateau. Our results showed that total SOC and mineral-associated organic carbon (MAOC) contents were not affected by N and P addition. However, P addition promoted particulate organic carbon (POC), which was likely attributed to hampered decomposition by lower microbial biomass (particularly fungi). In contrast, N addition did not change POC, probably because more plant biomass inputs were offset by faster decomposition of higher-quality plant litter (lower C:N ratio). Moreover, N addition rather than P addition decreased the percentage of labile functional group of O-alkyl C, whereas slightly increased alkyl-aromatic C:O-alkyl C ratio. These changes in SOC chemical composition with N inputs were likely caused by enhanced labile OM decomposition and rhizodeposit inputs. Overall, our results suggest that long-term exogenous N input could potentially accelerate SOM decomposition indicated by the chemical composition, but P input could result in inhibition of SOM decomposition and accumulation of POC stock in the alpine meadow ecosystem.
机译:人为活性和大气沉积增加了氮气(N)和磷(P)投入到陆地生态系统,这可以显着改变生态系统碳循环。为了更好地了解土壤有机碳(SoC)响应营养施肥的机制,我们测量了物理级分(通过粒度分馏)和化学成分(通过固态C-13 NMR光谱)SoC,植物生物质和营养浓度,土壤化学,微生物生物量和群落组成后10年的N和P添加到藏高原的高山草地上。我们的研究结果表明,SOC和矿物相关的有机碳(MAOC)内容物不受N和P的影响。然而,P添加促进的颗粒状有机碳(POC),其可能因降低微生物生物量(特别是真菌)而受到阻碍的分解。相比之下,不改变POC,可能是因为更多的植物生物量输入偏移更快地分解更高质量的植物垃圾(下C:N比率)。此外,N添加而不是P添加降低了O-烷基C的不稳定官能团的百分比,而略微增加的烷基芳族C:O-烷基C比。具有N个输入的SoC化学组成的这些变化可能是由增强的不稳定OM分解和无根辅助输入引起的。总体而言,我们的研究结果表明,长期外源性N输入可能会加速化学成分所示的SOM分解,但P输入可能导致高山草甸生态系统中POC存量的SOM分解和积累。

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