2016
DOI: 10.1007/s10021-016-9991-0
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Vegetation Type Dominates the Spatial Variability in CH4 Emissions Across Multiple Arctic Tundra Landscapes

Abstract: Methane (CH 4 ) emissions from Arctic tundra are an important feedback to global climate. Currently, modelling and predicting CH 4 fluxes at broader scales are limited by the challenge of upscaling plot-scale measurements in spatially heterogeneous landscapes, and by uncertainties regarding key controls of CH 4 emissions. In this study, CH 4 and CO 2 fluxes were measured together with a range of environmental variables and detailed vegetation analysis at four sites spanning 300 km latitude from Barrow to Ivotu… Show more

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Cited by 61 publications
(114 citation statements)
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References 60 publications
(23 reference statements)
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“…Furthermore, classifications based on landscape-level PFTs may result in higher classification errors at the tower footprint scale (~300-500 m) relative to classifications based on vegetation community type [28]. The vegetation community, chosen as the basis for our classification scheme, also better matches upscaling schemes used in local and regional carbon assessments, where land cover maps are used in conjunction with small area (e.g., 1 m chamber) flux measurements to obtain landscape level estimates of carbon exchange and greenhouse gas emissions [15]. Although the classifications resulting from this study do not directly reflect PFT types, our vegetation communities can be re-classified to PFT types for input in carbon flux models (in Section 3.2, a comparison of vegetation communities and PFTs is provided).…”
Section: Vegetation Datamentioning
confidence: 99%
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“…Furthermore, classifications based on landscape-level PFTs may result in higher classification errors at the tower footprint scale (~300-500 m) relative to classifications based on vegetation community type [28]. The vegetation community, chosen as the basis for our classification scheme, also better matches upscaling schemes used in local and regional carbon assessments, where land cover maps are used in conjunction with small area (e.g., 1 m chamber) flux measurements to obtain landscape level estimates of carbon exchange and greenhouse gas emissions [15]. Although the classifications resulting from this study do not directly reflect PFT types, our vegetation communities can be re-classified to PFT types for input in carbon flux models (in Section 3.2, a comparison of vegetation communities and PFTs is provided).…”
Section: Vegetation Datamentioning
confidence: 99%
“…Although the distribution of Arctic tundra vegetation is relatively well established at coarser scales (e.g., 1:7,500,000) and documented in databases such as the Circumpolar Arctic Vegetation Map ((CAVM team, 2003; [23]) and others [24,25], knowledge of local tundra community distributions remains ambiguous at many locations. Understanding the fine-scale spatial distribution of tundra communities, combined with improved high resolution vegetation mapping, is needed to understand relative contributions of and relationships between single vegetation community measurements of greenhouse gas fluxes (e.g.,~1 m chamber flux measurements; [15]) and those encompassing multiple vegetation communities (e.g.,~100 m eddy covariance measurements; [26]). …”
Section: Introductionmentioning
confidence: 99%
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“…Furthermore, due to CH 4 global warming potential [1,6], 2 of 21 an increase in emissions could result in additional atmospheric warming [7,8]. Current and future arctic CH 4 emissions are affected by spatially heterogeneous vegetation communities, environmental and climatic parameters and microtopographic characteristics [9][10][11]. Different vegetation communities emit CH 4 at different rates [12], therefore, plant community distributions could be used to upscale CH 4 fluxes to the landscape scale and improve emission estimates in carbon cycle [13,14] and CH 4 budget models [15].…”
Section: Introductionmentioning
confidence: 99%
“…Eddy covariance (EC) and chambers are the most common methods to measure CH 4 fluxes in the field, and both give useful information [5,9,10]), but can also result in inaccurate emission predictions [29,30]. EC towers measure trace gas fluxes with a high temporal resolution across a footprint with radii of roughly 100-300 m for a tower 1-3 m tall [31].…”
Section: Introductionmentioning
confidence: 99%