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Subsidence and carbon dioxide emissions in a smallholder peatland mosaic in Sumatra, Indonesia
Most attention in quantifying carbon dioxide (CO(2)) emissions from tropical peatlands has been on large-scale plantations (industrial timber, oil palm (Elaeis guinensis)), differing in drainage and land-use practices from those of smallholder farms. We measured subsidence and changes in bulk densit...
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Formato: | Online Artículo Texto |
Lenguaje: | English |
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Springer Netherlands
2018
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Materias: | |
Acceso en línea: | https://www.ncbi.nlm.nih.gov/pmc/articles/PMC6320748/ https://www.ncbi.nlm.nih.gov/pubmed/30662320 http://dx.doi.org/10.1007/s11027-018-9803-2 |
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author | Khasanah, Ni’matul van Noordwijk, Meine |
author_facet | Khasanah, Ni’matul van Noordwijk, Meine |
author_sort | Khasanah, Ni’matul |
collection | PubMed |
description | Most attention in quantifying carbon dioxide (CO(2)) emissions from tropical peatlands has been on large-scale plantations (industrial timber, oil palm (Elaeis guinensis)), differing in drainage and land-use practices from those of smallholder farms. We measured subsidence and changes in bulk density and carbon organic content to calculate CO(2) emissions over 2.5 years in a remnant logged-over forest and four dominant smallholder land-use types in Tanjung Jabung Barat District, Jambi Province, Sumatra, Indonesia: (1) simple rubber (Hevea brasiliensis) agroforest (> 30 years), (2) mixed coconut (Cocos nucifera) and coffee gardens (Coffea liberica) (> 40 years), (3) mixed betel nut (Areca catechu) and coffee gardens (> 20 years), and (4) oil palm plantation (1 year). We quantified changes in microtopography for each site for greater accuracy of subsidence estimates and tested the effects of nitrogen and phosphorus application. All sites had a fibric type of peat with depths of 50 to > 100 cm. A recently established oil palm had the highest rate of peat subsidence and emission (4.7 cm year(−1) or 121 Mg CO(2) ha(−1) year(−1)) while the remnant forest had the lowest (1.8 cm year(−1) or 40 Mg CO(2) ha(−1) year(−1)). Other land-use types subsided by 2–3 cm year(−1), emitting 70–85 Mg CO(2) ha(−1) year(−1). Fertilizer application did not have a consistent effect on inferred emissions. Additional emissions in the first years after drainage, despite groundwater tables of 40 cm, were of the order of belowground biomass of peat forest. Despite maintaining higher water tables, smallholder landscapes have CO(2) emissions close to, but above, current IPCC defaults. |
format | Online Article Text |
id | pubmed-6320748 |
institution | National Center for Biotechnology Information |
language | English |
publishDate | 2018 |
publisher | Springer Netherlands |
record_format | MEDLINE/PubMed |
spelling | pubmed-63207482019-01-17 Subsidence and carbon dioxide emissions in a smallholder peatland mosaic in Sumatra, Indonesia Khasanah, Ni’matul van Noordwijk, Meine Mitig Adapt Strateg Glob Chang Original Article Most attention in quantifying carbon dioxide (CO(2)) emissions from tropical peatlands has been on large-scale plantations (industrial timber, oil palm (Elaeis guinensis)), differing in drainage and land-use practices from those of smallholder farms. We measured subsidence and changes in bulk density and carbon organic content to calculate CO(2) emissions over 2.5 years in a remnant logged-over forest and four dominant smallholder land-use types in Tanjung Jabung Barat District, Jambi Province, Sumatra, Indonesia: (1) simple rubber (Hevea brasiliensis) agroforest (> 30 years), (2) mixed coconut (Cocos nucifera) and coffee gardens (Coffea liberica) (> 40 years), (3) mixed betel nut (Areca catechu) and coffee gardens (> 20 years), and (4) oil palm plantation (1 year). We quantified changes in microtopography for each site for greater accuracy of subsidence estimates and tested the effects of nitrogen and phosphorus application. All sites had a fibric type of peat with depths of 50 to > 100 cm. A recently established oil palm had the highest rate of peat subsidence and emission (4.7 cm year(−1) or 121 Mg CO(2) ha(−1) year(−1)) while the remnant forest had the lowest (1.8 cm year(−1) or 40 Mg CO(2) ha(−1) year(−1)). Other land-use types subsided by 2–3 cm year(−1), emitting 70–85 Mg CO(2) ha(−1) year(−1). Fertilizer application did not have a consistent effect on inferred emissions. Additional emissions in the first years after drainage, despite groundwater tables of 40 cm, were of the order of belowground biomass of peat forest. Despite maintaining higher water tables, smallholder landscapes have CO(2) emissions close to, but above, current IPCC defaults. Springer Netherlands 2018-03-21 2019 /pmc/articles/PMC6320748/ /pubmed/30662320 http://dx.doi.org/10.1007/s11027-018-9803-2 Text en © The Author(s) 2018 Open Access This article is distributed under the terms of the Creative Commons Attribution 4.0 International License (http://creativecommons.org/licenses/by/4.0/), which permits unrestricted use, distribution, and reproduction in any medium, provided you give appropriate credit to the original author(s) and the source, provide a link to the Creative Commons license, and indicate if changes were made. |
spellingShingle | Original Article Khasanah, Ni’matul van Noordwijk, Meine Subsidence and carbon dioxide emissions in a smallholder peatland mosaic in Sumatra, Indonesia |
title | Subsidence and carbon dioxide emissions in a smallholder peatland mosaic in Sumatra, Indonesia |
title_full | Subsidence and carbon dioxide emissions in a smallholder peatland mosaic in Sumatra, Indonesia |
title_fullStr | Subsidence and carbon dioxide emissions in a smallholder peatland mosaic in Sumatra, Indonesia |
title_full_unstemmed | Subsidence and carbon dioxide emissions in a smallholder peatland mosaic in Sumatra, Indonesia |
title_short | Subsidence and carbon dioxide emissions in a smallholder peatland mosaic in Sumatra, Indonesia |
title_sort | subsidence and carbon dioxide emissions in a smallholder peatland mosaic in sumatra, indonesia |
topic | Original Article |
url | https://www.ncbi.nlm.nih.gov/pmc/articles/PMC6320748/ https://www.ncbi.nlm.nih.gov/pubmed/30662320 http://dx.doi.org/10.1007/s11027-018-9803-2 |
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