Abstract

Vast areas of deforested tropical peatlands do not receive noteworthy shading by vegetation, which increases the amount of solar radiation reaching the peat surface. Peat temperature dynamics and heterotrophic carbon dioxide (CO2), nitrous oxide (N2O) and methane (CH4) fluxes were monitored under four shading conditions, i.e. unshaded, 28%, 51% and 90% shading at experiment sites established on reclaimed fallow agricultural- and degraded sites in Central Kalimantan, Indonesia. Groundwater tables on the sites were at about 50 cm depth, the sites were maintained vegetation free and root ingrowth to gas flux monitoring locations was prevented. Half of the four shading areas received NPK-fertilization 50 kg ha−1 for each of N, P and K during the experiment and the other half was unfertilized. Increases in shading created a lasting decrease in peat temperatures, and decreased diurnal temperature fluctuations, in comparison to less shaded plots. The largest peat temperature difference in the topmost 50 cm peat profile was between the unshaded and 90% shaded surface, where the average temperatures at 5 cm depth differed up to 3.7 °C, and diurnal temperatures at 5 cm depth varied up to 4.2 °C in the unshaded and 0.4 °C in the 90% shaded conditions. Highest impacts on the heterotrophic CO2 fluxes caused by the treatments were on agricultural land, where 90% shading from the full exposure resulted in a 33% lower CO2 emission average on the unfertilized plots and a 66% lower emission average on the fertilized plots. Correlation between peat temperature and CO2 flux suggested an approximately 8% (unfertilized) and 25% (fertilized) emissions change for each 1 °C temperature change at 5 cm depth on the agricultural land. CO2 flux responses to the treatments remained low on degraded peatland. Fertilized conditions negatively correlated with N2O efflux with increases in temperature, suggesting a 12–36% lower efflux for each 1 °C increase in peat temperature (at 5 cm depth) at the sites. Despite the apparently similar landscapes of fallow agricultural land and degraded peatland sites, the differences in greenhouse gas dynamics are expected to be an outcome of the long-term management differences.

Highlights

  • Lowland peatlands in Southeast Asia cover 24.8 million hectares (Mha), which is 56% of the tropical and 6% of the Environ

  • We found that most greenhouse gas (GHG) species responded to treatments at the agricultural land (AL) site, which has been seasonally used for smallholder agricultural crop production, while the gaseous flux responses to treatments remained low or did not provide a clear trend at the degraded land (DL) site

  • As a response to the hypotheses made prior to our experiment we can summarize the following; firstly, land management differences can divert organic substrate- or decompositionconducting microbial community characteristics so that apparently similar site types in comparable conditions result in differing responses in GHG fluxes to peat temperatures and fertilization

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Summary

Introduction

Lowland peatlands in Southeast Asia cover 24.8 million hectares (Mha), which is 56% of the tropical and 6% of the Environ. 9 (2014) 105013 total global peatland area (Page et al 2011). Both the vegetation and especially the underlying deep peat constitute a highly concentrated labile carbon pool of global significance by enclosing a regional peat carbon store of 68.5 Gt, which is equivalent to 77% of the tropical and 11–14% of the global peat carbon store. Human-induced peat ecosystem degradation impairs the carbon storing functions of tropical peatlands, where deforestation, deep drainage and the burning of areas converted to agriculture and plantations results in large greenhouse gas (GHG) emissions (Koh et al 2011, IPCC 2014). Since 1990, one third of the total 15.5 Mha of peatland in Peninsular Malaysia and the islands of Borneo and Sumatra have been deforested and drained, while most of the remaining peat forest area has been logged intensively (Langner and Siegert 2009, Miettinen and Liew 2010). A strong interest exists in understanding the drivers and mechanisms resulting in the detected GHG losses from reclaimed tropical peatlands

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