CH4 and N2O emissions from smallholder agricultural systems on tropical peatlands in Southeast Asia

Author:

Jovani‐Sancho Antonio Jonay12ORCID,O'Reilly Patrick34,Anshari Gusti56ORCID,Chong Xin Yi7ORCID,Crout Neil1,Evans Christopher D.2ORCID,Evers Stephanie47,Gan Jing Ye7,Gibbins Christopher N.7,Gusmayanti Evi58,Jamaludin Jamaludin9,Jaya Adi10ORCID,Page Susan3ORCID,Yosep Yosep10,Upton Caroline3,Wilson Paul1,Sjögersten Sofie1ORCID

Affiliation:

1. School of Biosciences University of Nottingham Loughborough UK

2. UK Centre for Ecology & Hydrology Bangor UK

3. School of Geography, Geology & the Environment University of Leicester Leicester UK

4. School of Biological and Environmental Sciences Liverpool John Mores University Liverpool UK

5. Magister of Environmental Science Universitas Tanjungpura Pontianak Indonesia

6. Soil Science Department Universitas Tanjungpura Pontianak Indonesia

7. School of Environmental and Geographical Sciences University of Nottingham Malaysia Semenyih Malaysia

8. Agrotechnology Department Universitas Tanjungpura Pontianak Indonesia

9. Universitas Nahdlatul Ulama, Kabupaten Kubu Raya Kalimantan Barat Indonesia

10. Faculty of Agriculture University of Palangka Raya Palangka Raya Indonesia

Abstract

AbstractThere are limited data for greenhouse gas (GHG) emissions from smallholder agricultural systems in tropical peatlands, with data for non‐CO2 emissions from human‐influenced tropical peatlands particularly scarce. The aim of this study was to quantify soil CH4 and N2O fluxes from smallholder agricultural systems on tropical peatlands in Southeast Asia and assess their environmental controls. The study was carried out in four regions in Malaysia and Indonesia. CH4 and N2O fluxes and environmental parameters were measured in cropland, oil palm plantation, tree plantation and forest. Annual CH4 emissions (in kg CH4 ha−1 year−1) were: 70.7 ± 29.5, 2.1 ± 1.2, 2.1 ± 0.6 and 6.2 ± 1.9 at the forest, tree plantation, oil palm and cropland land‐use classes, respectively. Annual N2O emissions (in kg N2O ha−1 year−1) were: 6.5 ± 2.8, 3.2 ± 1.2, 21.9 ± 11.4 and 33.6 ± 7.3 in the same order as above, respectively. Annual CH4 emissions were strongly determined by water table depth (WTD) and increased exponentially when annual WTD was above −25 cm. In contrast, annual N2O emissions were strongly correlated with mean total dissolved nitrogen (TDN) in soil water, following a sigmoidal relationship, up to an apparent threshold of 10 mg N L−1 beyond which TDN seemingly ceased to be limiting for N2O production. The new emissions data for CH4 and N2O presented here should help to develop more robust country level ‘emission factors’ for the quantification of national GHG inventory reporting. The impact of TDN on N2O emissions suggests that soil nutrient status strongly impacts emissions, and therefore, policies which reduce N‐fertilisation inputs might contribute to emissions mitigation from agricultural peat landscapes. However, the most important policy intervention for reducing emissions is one that reduces the conversion of peat swamp forest to agriculture on peatlands in the first place.

Funder

Biotechnology and Biological Sciences Research Council

Publisher

Wiley

Subject

General Environmental Science,Ecology,Environmental Chemistry,Global and Planetary Change

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