<scp>CH<sub>4</sub></scp> and <scp>N<sub>2</sub>O</scp> emissions from smallholder agricultural systems on tropical peatlands in Southeast Asia
A. Jonay Jovani‐Sancho, Patrick O’Reilly, Gusti Z. Anshari, Xin Yi Chong, N.M.J. Crout, Chris Evans, Stephanie Evers, Jing Gan, Christopher Gibbins, Evi Gusmayanti, Jamaludin Jamaludin, Adi Jaya, Susan Page, Yosep Yosep, Caroline Upton, Paul Wilson, Sofie Sjögersten
Abstract
Abstract There are limited data for greenhouse gas (GHG) emissions from smallholder agricultural systems in tropical peatlands, with data for non‐CO 2 emissions from human‐influenced tropical peatlands particularly scarce. The aim of this study was to quantify soil CH 4 and N 2 O 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. CH 4 and N 2 O fluxes and environmental parameters were measured in cropland, oil palm plantation, tree plantation and forest. Annual CH 4 emissions (in kg CH 4 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 N 2 O emissions (in kg N 2 O 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 CH 4 emissions were strongly determined by water table depth (WTD) and increased exponentially when annual WTD was above −25 cm. In contrast, annual N 2 O 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 N 2 O production. The new emissions data for CH 4 and N 2 O 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 N 2 O 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.