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Multiyear greenhouse gas balances at a rewetted temperate peatland

机译:再湿润的温带泥炭地多年温室气体平衡

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摘要

Drained peat soils are a significant source of greenhouse gas (GHG) emissions to the atmosphere. Rewetting these soils is considered an important climate change mitigation tool to reduce emissions and create suitable conditions for carbon sequestration. Long-term monitoring is essential to capture interannual variations in GHG emissions and associated environmental variables and to reduce the uncertainty linked with GHG emission factor calculations. In this study, we present GHG balances: carbon dioxide (CO2), methane (CH4) and nitrous oxide (N2O) calculated for a 5-year period at a rewetted industrial cutaway peatland in Ireland (rewetted 7years prior to the start of the study); and compare the results with an adjacent drained area (2-year data set), and with ten long-term data sets from intact (i.e. undrained) peatlands in temperate and boreal regions. In the rewetted site, CO2 exchange (or net ecosystem exchange (NEE)) was strongly influenced by ecosystem respiration (R-eco) rather than gross primary production (GPP). CH4 emissions were related to soil temperature and either water table level or plant biomass. N2O emissions were not detected in either drained or rewetted sites. Rewetting reduced CO2 emissions in unvegetated areas by approximately 50%. When upscaled to the ecosystem level, the emission factors (calculated as 5-year mean of annual balances) for the rewetted site were (+/- SD) -104 +/- 80g CO2-C m(-2)yr(-1) (i.e. CO2 sink) and 9 +/- 2g CH4-C m(-2)yr(-1) (i.e. CH4 source). Nearly a decade after rewetting, the GHG balance (100-year global warming potential) had reduced noticeably (i.e. less warming) in comparison with the drained site but was still higher than comparative intact sites. Our results indicate that rewetted sites may be more sensitive to interannual changes in weather conditions than their more resilient intact counterparts and may switch from an annual CO2 sink to a source if triggered by slightly drier conditions.
机译:排干的泥炭土是大气中温室气体(GHG)排放的重要来源。重新润湿这些土壤被认为是减轻排放量并为碳固存创造合适条件的重要气候缓解工具。长期监测对于捕获温室气体排放量和相关环境变量的年际变化以及减少与温室气体排放因子计算相关的不确定性至关重要。在本研究中,我们提供了在爱尔兰经过重新湿润的工业剖面泥炭地(在研究开始前的7年进行过湿润)的5年期间计算的温室气体平衡:二氧化碳(CO2),甲烷(CH4)和一氧化二氮(N2O) );并将结果与​​邻近的排水区(2年数据集)以及来自温带和北方地区完整(即不排水)泥炭地的10个长期数据集进行比较。在经过重新处理的地点,CO2交换(或净生态系统交换(NEE))受生态系统呼吸作用(R-eco)的影响较大,而不受初级生产总值(GPP)的影响。 CH4排放与土壤温度,地下水位或植物生物量有关。在排水或重新湿润的场所均未检测到N2O排放。重新湿润可将无植被地区的二氧化碳排放量减少约50%。重新升级到生态系统水平后,重新定位地点的排放因子(按年平均5年平均值计算)为(+/- SD)-104 +/- 80g CO2-C m(-2)yr(-1 )(即CO2汇)和9 +/- 2g CH4-C m(-2)yr(-1)(即CH4源)。再湿润后近十年,与排干点相比,GHG平衡(100年的全球变暖潜能)已明显减少(即变暖减少),但仍高于完整的比较点。我们的结果表明,再湿润的地点可能比其弹性更大的完好对应地点对天气状况的年际变化更敏感,并且如果受到稍微干燥的状况的触发,则可能从年度CO2汇入源。

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