Carbon Emissions From Oil Palm Plantations on Peat Soil

Southeast Asian peatlands have undergone recent land use change with an increase in industrial agricultural plantations, including oil palm. Cultivating peatlands requires creating drainage ditches and other surface microforms (i.e., harvest paths, frond piles, cover plants, and next to the palm). H...

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Main Authors: Frances Claire Manning, Lip Khoon Kho, Timothy Charles Hill, Thomas Cornulier, Yit Arn Teh
Format: Article
Language:English
Published: Frontiers Media S.A. 2019-08-01
Series:Frontiers in Forests and Global Change
Subjects:
Online Access:https://www.frontiersin.org/article/10.3389/ffgc.2019.00037/full
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spelling doaj-3686cd68f7c94a1daf7f5fdf9b51f2b82020-11-25T02:36:59ZengFrontiers Media S.A.Frontiers in Forests and Global Change2624-893X2019-08-01210.3389/ffgc.2019.00037453615Carbon Emissions From Oil Palm Plantations on Peat SoilFrances Claire Manning0Lip Khoon Kho1Timothy Charles Hill2Thomas Cornulier3Yit Arn Teh4Yit Arn Teh5Institute of Biological and Environmental Sciences, University of Aberdeen, Aberdeen, United KingdomBiological Research Division, Tropical Peat Research Institute, Malaysian Palm Oil Board, Kajang, MalaysiaDepartment of Geography, College of Life and Environmental Sciences, University of Exeter, Exeter, United KingdomInstitute of Biological and Environmental Sciences, University of Aberdeen, Aberdeen, United KingdomInstitute of Biological and Environmental Sciences, University of Aberdeen, Aberdeen, United KingdomSchool of Natural and Environmental Sciences, Newcastle University, Newcastle upon Tyne, United KingdomSoutheast Asian peatlands have undergone recent land use change with an increase in industrial agricultural plantations, including oil palm. Cultivating peatlands requires creating drainage ditches and other surface microforms (i.e., harvest paths, frond piles, cover plants, and next to the palm). However, it is currently unclear how these management actions affect rates of carbon losses from the peat. Here we report carbon fluxes from each of the different surface microforms measured monthly (soil CO2 [total soil respiration—Rtot] and stem CH4) and bimonthly (soil CH4, drain CO2 and drain CH4). We calculated annual carbon fluxes and partitioned heterotrophic (Rh) and root-rhizosphere respiration by sampling rhizosphere and root-free soil. Linear mixed effect models were used to determine which environmental factors best-predicted carbon fluxes, and to develop recommendations for management solutions that could reduce carbon losses. Carbon fluxes varied significantly between the different microforms; the greatest CO2 fluxes were measured next to the palm and the greatest CH4 fluxes were measured from the drainage ditches. Annual estimates of Rtot, Rh and drain CO2 were 22.08 ± 0.50, 17.75 ± 1.54, and 1.5 ± 0.10 Mg CO2-C ha−1 yr−1, respectively. Rh varied between the two plantations: Sebungan averaged 11.43 ± 1.37 Mg CO2-C ha−1 yr−1 and Sabaju averaged 24.08 ± 1.42 Mg CO2-C ha−1 yr−1. Net ecosystem CH4 fluxes averaged 61.02 ± 17.78 kg CH4-C ha−1 yr−1–similar to unmanaged swamp forests. The two plantations did not vary in overall CH4 flux, but did vary in transport pathway. CH4 fluxes from the soil, drains and stems followed a ratio of 50:50:0 from Sabaju (water table depth [WTD]: −0.49 ± 0.004 m) and 11:98:0 from Sebungan (WTD: −0.77 ± 0.007 m). Rh dominated the peat carbon losses. WTD controlled variation in Rh from Sebungan where the WTD was deeper. Air and soil temperature controlled variation in Sabaju, with greater fluxes from the harvest path, attributed to the absence of shade. These results suggest that shading the soil (e.g., through addition of frond piles) and raising the water table may be the most effective ways to reduce peat carbon loss from drained peat soils.https://www.frontiersin.org/article/10.3389/ffgc.2019.00037/fulloil palmpeatpeat oxidationheterotrophic respirationmethane
collection DOAJ
language English
format Article
sources DOAJ
author Frances Claire Manning
Lip Khoon Kho
Timothy Charles Hill
Thomas Cornulier
Yit Arn Teh
Yit Arn Teh
spellingShingle Frances Claire Manning
Lip Khoon Kho
Timothy Charles Hill
Thomas Cornulier
Yit Arn Teh
Yit Arn Teh
Carbon Emissions From Oil Palm Plantations on Peat Soil
Frontiers in Forests and Global Change
oil palm
peat
peat oxidation
heterotrophic respiration
methane
author_facet Frances Claire Manning
Lip Khoon Kho
Timothy Charles Hill
Thomas Cornulier
Yit Arn Teh
Yit Arn Teh
author_sort Frances Claire Manning
title Carbon Emissions From Oil Palm Plantations on Peat Soil
title_short Carbon Emissions From Oil Palm Plantations on Peat Soil
title_full Carbon Emissions From Oil Palm Plantations on Peat Soil
title_fullStr Carbon Emissions From Oil Palm Plantations on Peat Soil
title_full_unstemmed Carbon Emissions From Oil Palm Plantations on Peat Soil
title_sort carbon emissions from oil palm plantations on peat soil
publisher Frontiers Media S.A.
series Frontiers in Forests and Global Change
issn 2624-893X
publishDate 2019-08-01
description Southeast Asian peatlands have undergone recent land use change with an increase in industrial agricultural plantations, including oil palm. Cultivating peatlands requires creating drainage ditches and other surface microforms (i.e., harvest paths, frond piles, cover plants, and next to the palm). However, it is currently unclear how these management actions affect rates of carbon losses from the peat. Here we report carbon fluxes from each of the different surface microforms measured monthly (soil CO2 [total soil respiration—Rtot] and stem CH4) and bimonthly (soil CH4, drain CO2 and drain CH4). We calculated annual carbon fluxes and partitioned heterotrophic (Rh) and root-rhizosphere respiration by sampling rhizosphere and root-free soil. Linear mixed effect models were used to determine which environmental factors best-predicted carbon fluxes, and to develop recommendations for management solutions that could reduce carbon losses. Carbon fluxes varied significantly between the different microforms; the greatest CO2 fluxes were measured next to the palm and the greatest CH4 fluxes were measured from the drainage ditches. Annual estimates of Rtot, Rh and drain CO2 were 22.08 ± 0.50, 17.75 ± 1.54, and 1.5 ± 0.10 Mg CO2-C ha−1 yr−1, respectively. Rh varied between the two plantations: Sebungan averaged 11.43 ± 1.37 Mg CO2-C ha−1 yr−1 and Sabaju averaged 24.08 ± 1.42 Mg CO2-C ha−1 yr−1. Net ecosystem CH4 fluxes averaged 61.02 ± 17.78 kg CH4-C ha−1 yr−1–similar to unmanaged swamp forests. The two plantations did not vary in overall CH4 flux, but did vary in transport pathway. CH4 fluxes from the soil, drains and stems followed a ratio of 50:50:0 from Sabaju (water table depth [WTD]: −0.49 ± 0.004 m) and 11:98:0 from Sebungan (WTD: −0.77 ± 0.007 m). Rh dominated the peat carbon losses. WTD controlled variation in Rh from Sebungan where the WTD was deeper. Air and soil temperature controlled variation in Sabaju, with greater fluxes from the harvest path, attributed to the absence of shade. These results suggest that shading the soil (e.g., through addition of frond piles) and raising the water table may be the most effective ways to reduce peat carbon loss from drained peat soils.
topic oil palm
peat
peat oxidation
heterotrophic respiration
methane
url https://www.frontiersin.org/article/10.3389/ffgc.2019.00037/full
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