Impact of forest plantation on methane emissions from tropical peatland

Tropical peatlands are a known source of methane (CH4) to the atmosphere, but their contribution to atmospheric CH4 is poorly constrained. Since the 1980s, extensive areas of the peatlands in Southeast Asia have experienced land‐cover change to smallholder agriculture and forest plantations. This la...

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Veröffentlicht in:Global change biology 2020-04, Vol.26 (4), p.2477-2495
Hauptverfasser: Deshmukh, Chandra S., Julius, Dony, Evans, Chris D., Nardi, Susanto, Ari P., Page, Susan E., Gauci, Vincent, Laurén, Ari, Sabiham, Supiandi, Agus, Fahmuddin, Asyhari, Adibtya, Kurnianto, Sofyan, Suardiwerianto, Yogi, Desai, Ankur R.
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container_end_page 2495
container_issue 4
container_start_page 2477
container_title Global change biology
container_volume 26
creator Deshmukh, Chandra S.
Julius, Dony
Evans, Chris D.
Nardi
Susanto, Ari P.
Page, Susan E.
Gauci, Vincent
Laurén, Ari
Sabiham, Supiandi
Agus, Fahmuddin
Asyhari, Adibtya
Kurnianto, Sofyan
Suardiwerianto, Yogi
Desai, Ankur R.
description Tropical peatlands are a known source of methane (CH4) to the atmosphere, but their contribution to atmospheric CH4 is poorly constrained. Since the 1980s, extensive areas of the peatlands in Southeast Asia have experienced land‐cover change to smallholder agriculture and forest plantations. This land‐cover change generally involves lowering of groundwater level (GWL), as well as modification of vegetation type, both of which potentially influence CH4 emissions. We measured CH4 exchanges at the landscape scale using eddy covariance towers over two land‐cover types in tropical peatland in Sumatra, Indonesia: (a) a natural forest and (b) an Acacia crassicarpa plantation. Annual CH4 exchanges over the natural forest (9.1 ± 0.9 g CH4 m−2 year−1) were around twice as high as those of the Acacia plantation (4.7 ± 1.5 g CH4 m−2 year−1). Results highlight that tropical peatlands are significant CH4 sources, and probably have a greater impact on global atmospheric CH4 concentrations than previously thought. Observations showed a clear diurnal variation in CH4 exchange over the natural forest where the GWL was higher than 40 cm below the ground surface. The diurnal variation in CH4 exchanges was strongly correlated with associated changes in the canopy conductance to water vapor, photosynthetic photon flux density, vapor pressure deficit, and air temperature. The absence of a comparable diurnal pattern in CH4 exchange over the Acacia plantation may be the result of the GWL being consistently below the root zone. Our results, which are among the first eddy covariance CH4 exchange data reported for any tropical peatland, should help to reduce the uncertainty in the estimation of CH4 emissions from a globally important ecosystem, provide a more complete estimate of the impact of land‐cover change on tropical peat, and develop science‐based peatland management practices that help to minimize greenhouse gas emissions. We measured methane exchanges at the landscape scale using eddy covariance towers over a natural forest and an Acacia crassicarpa plantation in tropical peatland in Sumatra, Indonesia. Groundwater level (GWL) controls diurnal and seasonal variability in methane emissions. Annual methane emissions over the natural forest were around twice as high as those of the Acacia plantation. Lower methane emissions over the Acacia plantation may be attributed to lower GWL. Results highlight that tropical peatlands are significant methane sources, and probably have a gr
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Since the 1980s, extensive areas of the peatlands in Southeast Asia have experienced land‐cover change to smallholder agriculture and forest plantations. This land‐cover change generally involves lowering of groundwater level (GWL), as well as modification of vegetation type, both of which potentially influence CH4 emissions. We measured CH4 exchanges at the landscape scale using eddy covariance towers over two land‐cover types in tropical peatland in Sumatra, Indonesia: (a) a natural forest and (b) an Acacia crassicarpa plantation. Annual CH4 exchanges over the natural forest (9.1 ± 0.9 g CH4 m−2 year−1) were around twice as high as those of the Acacia plantation (4.7 ± 1.5 g CH4 m−2 year−1). Results highlight that tropical peatlands are significant CH4 sources, and probably have a greater impact on global atmospheric CH4 concentrations than previously thought. Observations showed a clear diurnal variation in CH4 exchange over the natural forest where the GWL was higher than 40 cm below the ground surface. The diurnal variation in CH4 exchanges was strongly correlated with associated changes in the canopy conductance to water vapor, photosynthetic photon flux density, vapor pressure deficit, and air temperature. The absence of a comparable diurnal pattern in CH4 exchange over the Acacia plantation may be the result of the GWL being consistently below the root zone. Our results, which are among the first eddy covariance CH4 exchange data reported for any tropical peatland, should help to reduce the uncertainty in the estimation of CH4 emissions from a globally important ecosystem, provide a more complete estimate of the impact of land‐cover change on tropical peat, and develop science‐based peatland management practices that help to minimize greenhouse gas emissions. We measured methane exchanges at the landscape scale using eddy covariance towers over a natural forest and an Acacia crassicarpa plantation in tropical peatland in Sumatra, Indonesia. Groundwater level (GWL) controls diurnal and seasonal variability in methane emissions. Annual methane emissions over the natural forest were around twice as high as those of the Acacia plantation. Lower methane emissions over the Acacia plantation may be attributed to lower GWL. 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Observations showed a clear diurnal variation in CH4 exchange over the natural forest where the GWL was higher than 40 cm below the ground surface. The diurnal variation in CH4 exchanges was strongly correlated with associated changes in the canopy conductance to water vapor, photosynthetic photon flux density, vapor pressure deficit, and air temperature. The absence of a comparable diurnal pattern in CH4 exchange over the Acacia plantation may be the result of the GWL being consistently below the root zone. Our results, which are among the first eddy covariance CH4 exchange data reported for any tropical peatland, should help to reduce the uncertainty in the estimation of CH4 emissions from a globally important ecosystem, provide a more complete estimate of the impact of land‐cover change on tropical peat, and develop science‐based peatland management practices that help to minimize greenhouse gas emissions. We measured methane exchanges at the landscape scale using eddy covariance towers over a natural forest and an Acacia crassicarpa plantation in tropical peatland in Sumatra, Indonesia. Groundwater level (GWL) controls diurnal and seasonal variability in methane emissions. Annual methane emissions over the natural forest were around twice as high as those of the Acacia plantation. Lower methane emissions over the Acacia plantation may be attributed to lower GWL. 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Julius, Dony ; Evans, Chris D. ; Nardi ; Susanto, Ari P. ; Page, Susan E. ; Gauci, Vincent ; Laurén, Ari ; Sabiham, Supiandi ; Agus, Fahmuddin ; Asyhari, Adibtya ; Kurnianto, Sofyan ; Suardiwerianto, Yogi ; Desai, Ankur R.</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c5099-33839f7b31d07e39b60e3033b471962d33a1c410ce6c84697154205869d10073</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2020</creationdate><topic>Acacia</topic><topic>Acacia crassicarpa</topic><topic>Agricultural management</topic><topic>Agriculture</topic><topic>Air pollution</topic><topic>Air temperature</topic><topic>Conductance</topic><topic>Covariance</topic><topic>Diurnal variations</topic><topic>eddy covariance measurements</topic><topic>Emission measurements</topic><topic>Emissions</topic><topic>Exchanging</topic><topic>Farm buildings</topic><topic>Flux density</topic><topic>forest plantation</topic><topic>Forests</topic><topic>Greenhouse effect</topic><topic>Greenhouse gases</topic><topic>Groundwater</topic><topic>Groundwater levels</topic><topic>Indonesia</topic><topic>Land cover</topic><topic>land‐use change</topic><topic>Methane</topic><topic>methane emissions</topic><topic>Peat</topic><topic>peatland management</topic><topic>Peatlands</topic><topic>Photosynthesis</topic><topic>Plant cover</topic><topic>Plantations</topic><topic>Primary</topic><topic>Primary s</topic><topic>Resistance</topic><topic>Root zone</topic><topic>Tropical climate</topic><topic>tropical peatlands</topic><topic>Vapor pressure</topic><topic>Vapour pressure</topic><topic>Vegetation type</topic><topic>Vortices</topic><topic>Water vapor</topic><topic>Water vapour</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Deshmukh, Chandra S.</creatorcontrib><creatorcontrib>Julius, Dony</creatorcontrib><creatorcontrib>Evans, Chris D.</creatorcontrib><creatorcontrib>Nardi</creatorcontrib><creatorcontrib>Susanto, Ari P.</creatorcontrib><creatorcontrib>Page, Susan E.</creatorcontrib><creatorcontrib>Gauci, Vincent</creatorcontrib><creatorcontrib>Laurén, Ari</creatorcontrib><creatorcontrib>Sabiham, Supiandi</creatorcontrib><creatorcontrib>Agus, Fahmuddin</creatorcontrib><creatorcontrib>Asyhari, Adibtya</creatorcontrib><creatorcontrib>Kurnianto, Sofyan</creatorcontrib><creatorcontrib>Suardiwerianto, Yogi</creatorcontrib><creatorcontrib>Desai, Ankur R.</creatorcontrib><collection>Wiley Online Library Open Access</collection><collection>PubMed</collection><collection>CrossRef</collection><collection>Ecology Abstracts</collection><collection>Water Resources Abstracts</collection><collection>Environmental Sciences and Pollution Management</collection><collection>ASFA: Aquatic Sciences and Fisheries Abstracts</collection><collection>Aquatic Science &amp; 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Since the 1980s, extensive areas of the peatlands in Southeast Asia have experienced land‐cover change to smallholder agriculture and forest plantations. This land‐cover change generally involves lowering of groundwater level (GWL), as well as modification of vegetation type, both of which potentially influence CH4 emissions. We measured CH4 exchanges at the landscape scale using eddy covariance towers over two land‐cover types in tropical peatland in Sumatra, Indonesia: (a) a natural forest and (b) an Acacia crassicarpa plantation. Annual CH4 exchanges over the natural forest (9.1 ± 0.9 g CH4 m−2 year−1) were around twice as high as those of the Acacia plantation (4.7 ± 1.5 g CH4 m−2 year−1). Results highlight that tropical peatlands are significant CH4 sources, and probably have a greater impact on global atmospheric CH4 concentrations than previously thought. Observations showed a clear diurnal variation in CH4 exchange over the natural forest where the GWL was higher than 40 cm below the ground surface. The diurnal variation in CH4 exchanges was strongly correlated with associated changes in the canopy conductance to water vapor, photosynthetic photon flux density, vapor pressure deficit, and air temperature. The absence of a comparable diurnal pattern in CH4 exchange over the Acacia plantation may be the result of the GWL being consistently below the root zone. Our results, which are among the first eddy covariance CH4 exchange data reported for any tropical peatland, should help to reduce the uncertainty in the estimation of CH4 emissions from a globally important ecosystem, provide a more complete estimate of the impact of land‐cover change on tropical peat, and develop science‐based peatland management practices that help to minimize greenhouse gas emissions. We measured methane exchanges at the landscape scale using eddy covariance towers over a natural forest and an Acacia crassicarpa plantation in tropical peatland in Sumatra, Indonesia. Groundwater level (GWL) controls diurnal and seasonal variability in methane emissions. Annual methane emissions over the natural forest were around twice as high as those of the Acacia plantation. Lower methane emissions over the Acacia plantation may be attributed to lower GWL. Results highlight that tropical peatlands are significant methane sources, and probably have a greater impact on global atmospheric methane concentrations than previously thought.</abstract><cop>England</cop><pub>Blackwell Publishing Ltd</pub><pmid>31991028</pmid><doi>10.1111/gcb.15019</doi><tpages>19</tpages><orcidid>https://orcid.org/0000-0003-2660-4315</orcidid><orcidid>https://orcid.org/0000-0002-7052-354X</orcidid><oa>free_for_read</oa></addata></record>
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subjects Acacia
Acacia crassicarpa
Agricultural management
Agriculture
Air pollution
Air temperature
Conductance
Covariance
Diurnal variations
eddy covariance measurements
Emission measurements
Emissions
Exchanging
Farm buildings
Flux density
forest plantation
Forests
Greenhouse effect
Greenhouse gases
Groundwater
Groundwater levels
Indonesia
Land cover
land‐use change
Methane
methane emissions
Peat
peatland management
Peatlands
Photosynthesis
Plant cover
Plantations
Primary
Primary s
Resistance
Root zone
Tropical climate
tropical peatlands
Vapor pressure
Vapour pressure
Vegetation type
Vortices
Water vapor
Water vapour
title Impact of forest plantation on methane emissions from tropical peatland
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