Southeast Asian forest and land fires: how can vulnerable ecosystems and peoples adapt to changing climate and fire regimes?

Southeast Asian forest and land fires: how can vulnerable ecosystems and peoples adapt to changing climate and fireregimes?

June 2007

published by iLEAPSNewsletter 4, 2007

Daniel Murdiyarso1 and Louis Lebel 2

1 Center for International Forestry Research (CIFOR), Jl. CIFOR, Situgede, Bogor, Indonesia
2 Unit for Social and Environmental Research (USER), Chiang Mai University, Chiang Mai,Thailand

Forest and land fires – both natural and human-lit – are not new to the landscapes of Southeast Asia. Today’s fire regimes are a consequence of past interactions between humans, climate and ecosystems. In many places fire is a tool for converting forests to agricultural lands and in subsequent land management [1]. But fire is also described as a problem, or even, disaster.

Carefully distinguishing among types of fires, the ecosystems in which they occur, and their relationship to spatial and temporal scales of historical fire regimes is important but does not eliminate politics. Differences in interests and perspectives affect land and forest policies in ways which can have important consequences for ecosystems and human well-being at several levels [2].

The importance of different perspectives and scale for understanding fires is illustrated sharply in situations where vulnerable ecosystems and peoples coexist with important stocks of carbon susceptible to fire. In the context of Indonesia this means managing risks of low frequency, but high impact, fires in peatlands.

Peatlands are important for the hydrology of a region as they buffer flooding as well as for conservation of biodiversity, fishing and hunting, and carbon storage. Peatlands cover more than 10% of Indonesia’s land area including many agricultural locations critical to sustaining livelihoods of vulnerable peoples. When peatlands are drained upper layers dry-out and become prone to fire. Fire policies need to give high priority to the management of vulnerable peatlands.

The large fires of 1997/1998 in Indonesia resulted from a combination of fires lit to clear and prepare land by smallholders and larger firms as well as accidental fires in forest and peat swamps. Dry weather generated by El Niño Southern Oscillation (ENSO) made conditions ideal for fire. Impacts on timber and estate crops were relatively modest; valuable investments and assets were protected. Other forest types, like logged-over forests suitable for conversion to oil palm plantations, on the other hand, were extremely “vulnerable” to being burnt.

Peat fires in Kalimantan and Sumatra made a huge contribution to trans-boundary smoke haze. Heil et al. [3] modelled dispersion of fire pollutants. They found that if peat fires are excluded then ambient air quality standards would only be exceeded close to the main fires, whereas if peat fires are included air quality standards are exceeded far away from the source as was observed. For Asia, burning of forest comprises 45% and burning of crop residues in the fields comprises 34% of vegetation burnt openly, that is, outside stoves [4].

Goldammer’s [5] study of recovery of forests after major fire is important to policy in several ways. First it underlines the need, from a biodiversity conservation perspective, to go beyond peat lands and look carefully at vulnerable dipterocarp forest ecosystems. Excessive use of fire in dipterocarp forest ecosystems is altering tree family-level composition. Second, it draws attention to the very different fire-vegetation relations in seasonally dry tropical forests and pine forests. Here outright fire suppression policies would be misplaced and likely to be detrimental to the ecosystems. Fire suppression policies may also increase the vulnerability of swidden farmers dependent on using fire to clear forests for cultivation. Fire management policies need to be adjusted to local ecological and social

Fire mitigation has largely been conducted in conjunction with building capacity in fire fighting. Prior to the large forest fires in Borneo 1982 fire fighting strategies and infrastructure were not well developed in many parts of Southeast Asia. During the past 20 years 40 international fire projects and missions costing well over US$ 30 million have been implemented, primarily in Indonesia [6]. National governments have also invested significantly in fire management and capacity building at local levels.

Science has made an important contribution to the understanding of the causes and impacts of fires, and in turn, has informed operations. Early warning systems such as the Fire Danger Rating System (FDRS) for Indonesia and Malaysia, for example, were developed jointly by scientists and government agencies [7]. Research has also highlighted alternative ways to manage land to reduce episodes of high fire-related emissions to the atmosphere [8]. These involve delays in time of burning as well as use of zero-burning methods for disposing of waste vegetation. Incentives and regulations are justified because of immediate benefits to human health at local and regional levels. In addition, where total long-term emissions of greenhouse gases could also be reduced through such efforts then this
provides additional reasons to encourage such practices.

A focus on building adaptive capacity in fire management could be an effective way to adapt to climate change. Changes in fire regimes, as a result of recurrent droughts and human interventions, mimic some of the key features of the anticipated impacts of climate change on forest and plantation ecosystems. Chokkalingham et al. [9] in particular emphasise the importance of stimulating alternative livelihood options during drought years. They also suggest that, properly guided, the private sector could play an important role through estate tree or palm crops and agroforestry systems rather than current emphasis on annual crops. Industry expertise could be a helpful ally in estimating costs of adaptation to climate change in the commercial forestry sector.

Ultimately adaptation to fire regime changes resulting from climate change would benefit from an explicitly multilevel approach that recognizes some capacities are more appropriately developed at particular levels (e.g. Adger et al. [10]). Better coordination of smoke-haze monitoring and risk management at the regional level would be useful. The vulnerable carbon-rich peatland areas would benefit from improved fire management at district or national levels.

Fire has very different meanings and policy implications when viewed as a tool for clearing, as a producer of damaging smoke, or as a source of greenhouse gas emissions. The biophysical and social implications of fires vary greatly from place to place. More attention needs to be paid to the relationships between fire regimes and vulnerable ecosystems and peoples, both under current and future climate. With improved understanding of these interactions and differences the possibility arises of moving tropical forest fire management from suppression everywhere to a more reasoned guided use.


1. Stolle F., Chomitz K.M., Lambin E.F. and Tomich T.P. 2003. Land use and vegetation fires in Jambi Province, Sumatra, Indonesia. Forest Ecology and Management 179, 277-292.

2. Murdiyarso D. and Lebel L. 2007. Local and Global Perspectives of Southeast Asian Forest and Land Fires. Journal of Mitigation and Adaptation Strategies for Global Change 12, 3-11.

3. Heil A., Langmann B. and Aldrian E. 2005. Indonesian peat and vegetation fire emissions: study on factors influencing largescale smoke haze pollution using a regional atmospheric chemistry model. Journal of Mitigation and Adaptation Strategies for Global Change 12, 113-133.

4. Streets D.G., Yarber K.F., Woo J.-H. and Carmichael G.R. 2003. Biomass burning in Asia: annual and seasonal estimates and atmospheric emissions. Global Biogeochemical Cycles 17, 1099.

5. Goldammer J.G. 2007. History of equatorial vegetation fires and fire research in Southeast Asia before the 1997-98 Episode: a reconstruction of creeping environmental changes. Journal of Mitigation and Adaptation Strategies for Global Change 12, 13-32.

6. Dennis R. 1999. A review of Fire Projects in Indonesia (1982-1998). Center for International Forestry Research, Bogor,Indonesia.

7. de Groot W.J., Field R.D., Brady M.A., Roswintiarti O. and Mohamad M. 2007. Development of the Indonesian and Malaysian fire danger rating systems. Journal of Mitigation and Adaptation Strategies for Global Change 12, 165-180.

8. Murdiyarso D., Lebel L, Gintings A.N., Tampubolon S.M.H., Heil A. and Wasson M. 2004. Policy responses to complex environmental problems: insights from a sciencepolicy activity on transboundary haze from vegetation fires in Southeast Asia. Journal of Agriculture, Ecosystems, and Environment 104, 47-56.

9. Chokkalingam U., Suyanto S., Permana R.P., Kurniawan I., Mannes J., Darmawan A., Khususyiah N. and Susanto R.H. 2007. Community fire use, resource change, and livelihood impacts: the downward spiral in the wetlands of Southern Sumatra. Journal of Mitigation and Adaptation Strategies for Global Change 12, 75-100.

10. Adger N.W., Arnell N.W and Tompkins E.L. 2005. Successful adaptation to climate change across scales. Global Environmental Change 15, 77-86

Print Friendly, PDF & Email
WP-Backgrounds Lite by InoPlugs Web Design and Juwelier Schönmann 1010 Wien