Agrinova, Alma, QC, G8B 7S8, Canada.
Glob Chang Biol. 2013 Apr;19(4):1126-40. doi: 10.1111/gcb.12125. Epub 2013 Jan 24.
Arctic soils store large amounts of labile soil organic matter (SOM) and several studies have suggested that SOM characteristics may explain variations in SOM cycling rates across Arctic landscapes and Arctic ecosystems. The objective of this study was to investigate the influence of routinely measured soil properties and SOM characteristics on soil gross N mineralization and soil GHG emissions at the landscape scale. This study was carried out in three Canadian Arctic ecosystems: Sub-Arctic (Churchill, MB), Low-Arctic (Daring Lake, NWT), and High-Arctic (Truelove Lowlands, NU). The landscapes were divided into five landform units: (1) upper slope, (2) back slope, (3) lower slope, (4) hummock, and (5) interhummock, which represented a great diversity of Static and Turbic Cryosolic soils including Brunisolic, Gleysolic, and Organic subgroups. Soil gross N mineralization was measured using the (15) N dilution technique, whereas soil GHG emissions (N2 O, CH4 , and CO2 ) were measured using a multicomponent Fourier transform infrared gas analyzer. Soil organic matter characteristics were determined by (1) water-extractable organic matter, (2) density fractionation of SOM, and (3) solid-state CPMAS (13) C nuclear magnetic resonance (NMR) spectroscopy. Results showed that gross N mineralization, N2 O, and CO2 emissions were affected by SOM quantity and SOM characteristics. Soil moisture, soil organic carbon (SOC), light fraction (LF) of SOM, and O-Alkyl-C to Aromatic-C ratio positively influenced gross N mineralization, N2 O and CO2 emissions, whereas the relative proportion of Aromatic-C negatively influenced those N and C cycling processes. Relationships between SOM characteristics and CH4 emissions were not significant throughout all Arctic ecosystems. Furthermore, results showed that lower slope and interhummock areas store relatively more labile C than upper and back slope locations. These results are particularly important because they can be used to produce better models that evaluate SOM stocks and dynamics under several climate scenarios and across Arctic landscapes and ecosystems.
北极土壤中储存着大量的活性土壤有机物质(SOM),有几项研究表明,SOM 特性可能可以解释北极景观和北极生态系统中 SOM 循环速率的变化。本研究的目的是调查常规测量的土壤特性和 SOM 特性对景观尺度上土壤总氮矿化和土壤温室气体排放的影响。本研究在加拿大三个北极生态系统中进行:亚北极(丘吉尔,MB)、低北极(达林湖,NWT)和高北极(特鲁罗夫低地,NU)。景观分为五个地貌单元:(1)上斜坡、(2)背坡、(3)下斜坡、(4)丘间和(5)丘间洼地,代表了广泛的静态和紊流冰缘土,包括 Brunisolic、Gleysolic 和有机亚组。使用(15)N 稀释技术测量土壤总氮矿化,使用多组分傅里叶变换红外气体分析仪测量土壤温室气体排放(N2O、CH4 和 CO2)。通过(1)水提取的有机物质、(2)SOM 的密度分级和(3)固态 CPMAS(13)C 核磁共振(NMR)光谱来确定土壤有机质特性。结果表明,总氮矿化、N2O 和 CO2 排放受到 SOM 数量和 SOM 特性的影响。土壤湿度、土壤有机碳(SOC)、SOM 的轻组分(LF)和 O-烷基-C 对芳族-C 的比例对总氮矿化、N2O 和 CO2 排放有积极影响,而芳族-C 的相对比例对这些氮和碳循环过程有负面影响。在整个北极生态系统中,SOM 特性与 CH4 排放之间的关系并不显著。此外,结果表明,下斜坡和丘间洼地比上斜坡和背斜坡储存了相对更多的活性 C。这些结果尤为重要,因为它们可以用于生成更好的模型,以在几种气候情景下评估北极景观和生态系统中 SOM 的储量和动态。