“…Globally, approximately half the average annual flux of 2.0 Pg C yr -1 has been emitted due to fires in forest ecosystems between 1997 and 2009; 20 of these fires were from deforestation and tropical forest fires, 16 from woodland fires, and 15 from mostly extra-tropical forest fires 2001 -2009 van der Werf et al, 2010 . Although most fires in ecosystems are set by humans, a complex interaction between climate, ecosystem processes, and human activities determines fire-driven C emissions from burned areas van der Werf et al, 2010 . In tropical peatlands of Southeast Asia such as the Indonesian lowlands and Peninsular Malaysia, there are substantial fire-driven C losses in the global terrestrial C cycle Herawati and Santoso, 2011;Smith et al, 2018;Kumar et al, 2020 . For examples, the R s from burned peat surfaces increased 46 over the first nine months following a fire in the Kalimantan tropical peatland forest Astiani et al, 2018 , and a ground fire significantly stimulated R s by 17.5 for a mixed forest of sub-tropical-temperate transition zones in central China Hu et al, 2020 . Although the humid climate typical of the Asian monsoon region is relatively free from wildfire when compared to drier ecosystems in other arid or boreal ecosystems, the frequency, intensity, and size of wildfires have been increasing and is expected to increase rapidly in future given the increase in lightning strikes and seasonally extreme droughts associated with global warming Hu et al, 2017;Chen et al, 2019;Song et al, 2019. Sun et al 2014 investigated the effect of fire disturbance on R s in birch and larch forests in China, and Hu et al 2017 examined the effects of fire severity on R s in larch forests to better estimate R s in boreal ecosystems; they found that wildfires decreased R s mainly due to decreased autotrophic respiration.…”