CH<sub>4</sub> and N<sub>2</sub>O dynamics in the boreal forest–mire ecotone

In spite of advances in greenhouse gas research, the spatiotemporal CH<sub>4</sub> and N<sub>2</sub>O dynamics of boreal landscapes remain challenging, e.g., we need clarification of whether forest–mire transitions are occasional hotspots of landscape CH<sub>4</sub&g...

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Main Authors: B. Tupek, K. Minkkinen, J. Pumpanen, T. Vesala, E. Nikinmaa
Format: Article
Language:English
Published: Copernicus Publications 2015-01-01
Series:Biogeosciences
Online Access:http://www.biogeosciences.net/12/281/2015/bg-12-281-2015.pdf
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author B. Tupek
K. Minkkinen
J. Pumpanen
T. Vesala
E. Nikinmaa
author_facet B. Tupek
K. Minkkinen
J. Pumpanen
T. Vesala
E. Nikinmaa
author_sort B. Tupek
collection DOAJ
description In spite of advances in greenhouse gas research, the spatiotemporal CH<sub>4</sub> and N<sub>2</sub>O dynamics of boreal landscapes remain challenging, e.g., we need clarification of whether forest–mire transitions are occasional hotspots of landscape CH<sub>4</sub> and N<sub>2</sub>O emissions during exceptionally high and low ground water level events. <br><br> In our study, we tested the differences and drivers of CH<sub>4</sub> and N<sub>2</sub>O dynamics of forest/mire types in field conditions along the soil moisture gradient of the forest–mire ecotone. Soils changed from Podzols to Histosols and ground water rose downslope from a depth of 10 m in upland sites to 0.1 m in mires. Yearly meteorological conditions changed from being exceptionally wet to typical and exceptionally dry for the local climate. The median fluxes measured with a static chamber technique varied from −51 to 586 μg m<sup>−2</sup> h<sup>−1</sup> for CH<sub>4</sub> and from 0 to 6 μg m<sup>−2</sup> h<sup>−1</sup> for N<sub>2</sub>O between forest and mire types throughout the entire wet–dry period. <br><br> In spite of the highly dynamic soil water fluctuations in carbon rich soils in forest–mire transitions, there were no large peak emissions in CH<sub>4</sub> and N<sub>2</sub>O fluxes and the flux rates changed minimally between years. Methane uptake was significantly lower in poorly drained transitions than in the well-drained uplands. Water-saturated mires showed large CH<sub>4</sub> emissions, which were reduced entirely during the exceptional summer drought period. Near-zero N<sub>2</sub>O fluxes did not differ significantly between the forest and mire types probably due to their low nitrification potential. When upscaling boreal landscapes, pristine forest–mire transitions should be regarded as CH<sub>4</sub> sinks and minor N<sub>2</sub>O sources instead of CH<sub>4</sub> and N<sub>2</sub>O emission hotspots.
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spelling doaj.art-af1c6cbc998449b3b0dac763edbe08992022-12-22T02:50:18ZengCopernicus PublicationsBiogeosciences1726-41701726-41892015-01-0112228129710.5194/bg-12-281-2015CH<sub>4</sub> and N<sub>2</sub>O dynamics in the boreal forest–mire ecotoneB. Tupek0K. Minkkinen1J. Pumpanen2T. Vesala3E. Nikinmaa4Department of Forest Sciences, P.O. Box 27, 00014 University of Helsinki, FinlandDepartment of Forest Sciences, P.O. Box 27, 00014 University of Helsinki, FinlandDepartment of Forest Sciences, P.O. Box 27, 00014 University of Helsinki, FinlandDepartment of Physics, P.O. Box 48, 00014 University of Helsinki, FinlandDepartment of Forest Sciences, P.O. Box 27, 00014 University of Helsinki, FinlandIn spite of advances in greenhouse gas research, the spatiotemporal CH<sub>4</sub> and N<sub>2</sub>O dynamics of boreal landscapes remain challenging, e.g., we need clarification of whether forest–mire transitions are occasional hotspots of landscape CH<sub>4</sub> and N<sub>2</sub>O emissions during exceptionally high and low ground water level events. <br><br> In our study, we tested the differences and drivers of CH<sub>4</sub> and N<sub>2</sub>O dynamics of forest/mire types in field conditions along the soil moisture gradient of the forest–mire ecotone. Soils changed from Podzols to Histosols and ground water rose downslope from a depth of 10 m in upland sites to 0.1 m in mires. Yearly meteorological conditions changed from being exceptionally wet to typical and exceptionally dry for the local climate. The median fluxes measured with a static chamber technique varied from −51 to 586 μg m<sup>−2</sup> h<sup>−1</sup> for CH<sub>4</sub> and from 0 to 6 μg m<sup>−2</sup> h<sup>−1</sup> for N<sub>2</sub>O between forest and mire types throughout the entire wet–dry period. <br><br> In spite of the highly dynamic soil water fluctuations in carbon rich soils in forest–mire transitions, there were no large peak emissions in CH<sub>4</sub> and N<sub>2</sub>O fluxes and the flux rates changed minimally between years. Methane uptake was significantly lower in poorly drained transitions than in the well-drained uplands. Water-saturated mires showed large CH<sub>4</sub> emissions, which were reduced entirely during the exceptional summer drought period. Near-zero N<sub>2</sub>O fluxes did not differ significantly between the forest and mire types probably due to their low nitrification potential. When upscaling boreal landscapes, pristine forest–mire transitions should be regarded as CH<sub>4</sub> sinks and minor N<sub>2</sub>O sources instead of CH<sub>4</sub> and N<sub>2</sub>O emission hotspots.http://www.biogeosciences.net/12/281/2015/bg-12-281-2015.pdf
spellingShingle B. Tupek
K. Minkkinen
J. Pumpanen
T. Vesala
E. Nikinmaa
CH<sub>4</sub> and N<sub>2</sub>O dynamics in the boreal forest–mire ecotone
Biogeosciences
title CH<sub>4</sub> and N<sub>2</sub>O dynamics in the boreal forest–mire ecotone
title_full CH<sub>4</sub> and N<sub>2</sub>O dynamics in the boreal forest–mire ecotone
title_fullStr CH<sub>4</sub> and N<sub>2</sub>O dynamics in the boreal forest–mire ecotone
title_full_unstemmed CH<sub>4</sub> and N<sub>2</sub>O dynamics in the boreal forest–mire ecotone
title_short CH<sub>4</sub> and N<sub>2</sub>O dynamics in the boreal forest–mire ecotone
title_sort ch sub 4 sub and n sub 2 sub o dynamics in the boreal forest mire ecotone
url http://www.biogeosciences.net/12/281/2015/bg-12-281-2015.pdf
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