Abstract

We provide the first assessment of tropical peatland depth of burn (DoB) using structure from motion (SfM) photogrammetry, applied to imagery collected using a low-cost, low-altitude unmanned aerial vehicle (UAV) system operated over a 5.2 ha tropical peatland in Jambi Province on Sumatra, Indonesia. Tropical peat soils are the result of thousands of years of dead biomass accumulation, and when burned are globally significant net sources of carbon emissions. The El Niño year of 2015 saw huge areas of Indonesia affected by tropical peatland fires, more so than any year since 1997. However, the Depth of Burn (DoB) of these 2015 fires has not been assessed, and indeed has only previously been assessed in few tropical peatland burns in Kalimantan. Therefore, DoB remains arguably the largest uncertainty when undertaking fire emissions calculations in these tropical peatland environments. We apply a SfM photogrammetric methodology to map this DoB metric, and also investigate combustion heterogeneity using orthomosaic photography collected using the UAV system. We supplement this information with pre-burn airborne light detection and ranging (LiDAR) data, reducing uncertainty by estimating pre-burn soil height more accurately than from interpolation of adjacent unburned areas alone. Our pre-and post-fire Digital Terrain Models (DTMs) show accuracies of 0.04 and 0.05 m (root-mean-square error, RMSE) respectively, compared to ground-based global navigation satellite system (GNSS) surveys. Our final DoB map of a 5.2 ha degraded peat swamp forest area neighboring Berbak National Park (Sumatra, Indonesia) shows burn depths extending from close to zero to over 1 m, with a mean (±1σ) DoB of 0.23 ± 0.19 m. This lies well within the range found by the few other studies available (on Kalimantan; none are available on Sumatra). Our combustion heterogeneity analysis suggests the deepest burns, which extend to ~1.3 m, occur around tree roots. We use these DoB data within the Intergovernmental Panel on Climate Change (IPCC) default equation for fire emissions to estimate mean carbon emissions as 134 ± 29 t·C∙ha−1 for this peatland fire, which is in an area that had not had a recorded fire previously. This is amongst the highest per unit area fuel consumption anywhere in the world for landscape fires. Our approach provides significant uncertainty reductions in such emissions calculations via the reduction in DoB uncertainty, and by using the UAV SfM approach this is accomplished at a fraction of the cost of airborne LiDAR—albeit over limited sized areas at present. Deploying this approach at locations across Indonesia, sampling a variety of fire-affected landscapes, would provide new and important DoB statistics for producing optimized carbon and greenhouse gas (GHG) emissions estimates from peatland fires.

Highlights

  • FFiirreess inintrotpriocpalicpaelatplaenadtlsaanrdesa wareell-raecowgenlils-erdecsoogunricseeodf csaoruborcneemoifssicoanrbs otontheematimssioosnpshertoe [1t,h2e], aatnmdoinsp2h0e1r5e l[e1v,2e]l,saonfdlainnd2s0c1a5pelebvuerlns ionfglainndInscdaopneesbiuarwnienrge ginreIantdlyonexesaicaerwbearteedgrbeyaatlydreoxuagcehrtbbartoeudgbhyt aondbroyutghhetsbtrroonugghEtl Noniñboy

  • We have presented a structure from motion (SfM) approach for spatially mapping peatland depth of burn (DoB), based around post-fire imagery collected via a small, affordable unmanned aerial vehicle (UAV)

  • The deepest burns occur around the roots of vegetation which is confirmed in Figure 11 and Figure S1 where the some of the highest pre-burn peaks occur in the same location at the lowest post-burn pits, and by the combustion heterogeneity analysis based on analysis of the RGB imagery collected from the UAV (Section 4.1)

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Summary

Introduction

FFiirreess inintrotpriocpalicpaelatplaenadtlsaanrdesa wareell-raecowgenlils-erdecsoogunricseeodf csaoruborcneemoifssicoanrbs otontheematimssioosnpshertoe [1t,h2e], aatnmdoinsp2h0e1r5e l[e1v,2e]l,saonfdlainnd2s0c1a5pelebvuerlns ionfglainndInscdaopneesbiuarwnienrge ginreIantdlyonexesaicaerwbearteedgrbeyaatlydreoxuagcehrtbbartoeudgbhyt aondbroyutghhetsbtrroonugghEtl Noniñboy. OTmhiesticmanesbecoduopnleedbywaisthseasstminogstphheearmicoausnsetsosfmthenertms oafl trhaedieamntitetendersgpyeceimesit[t3e]d—bbyutthise mbuorsnticnogmpmeaotn—lysodmoneetibmyems ceoausuprliendgwthitehbautrmnoedspahreeraicanadssmesusmltiepnlytsinogf tthhiesebmyitthteedesstpimecaietsed[3d]—epbthutoifsbmuronst(DcoomBm) aonndlypdreo-nfierebpyematebausulkridnegntshiteyb[u1r0n,1e1d].aDreuaeatnodthmeuhlitgiphlbyuinlkg dtheinssbityytahnedesctaimrbaotnedcodnetpentht ooff pbuearnt, a(DndoBth) eanfadcpt trhe-afitrDeopBeactabnuelxktednednstiotyte[n1s0,o1f1]c.mD,ulaentdostchaepheifgirhebfuulekl consumption per unit area in tropical peatlands is amongst the highest of any biome worldwide. 2016, 8, 1000 density and carbon content of peat, and the fact that DoB can extend to tens of cm, landscape fire fuel consumption per unit area in tropical peatlands is amongst the highest of any biome worldwide. The range in DoBs expected between different types of peatland biome and between different fires means that the carbon emission estimates derived from the burned area based approach remain rather uncertain, and whilst burned area and peat bulk density are increasingly well measured [12,13,14], few DoB estimates exist currently. The existing spatially explicit DoB measurements available, beyond a few point-based measures derived via the use of metal rods to assess subsidence after burning [1,4], have mostly been assessed using light detection and ranging (LiDAR) approaches [9,15]

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