Fire Damages in East Kalimantan in 1997/98:
Relations to Land Use and Proposals for Further Action
(IFFN No. 22 – April 2000, p. 31-35)
After the severe fire episodes during the El Niño-Southern Oscillation (ENSO) events of 1982-83, 1991 and 1994 a prolonged and extremely severe fire season occurred during the last ENSO of 1997-98 in South East Asia (Goldammer et al. 1996, Goldammer 1999). The Indonesian province of East Kalimantan was the area worst affected by extended wildfires between late 1997 and May 1998. Daily satellite (NOAA AVHRR) maps provided by the Integrated Forest Fire Management (IFFM) project, a joint Technical Cooperation project between the Indonesian Ministry of Forests and Estate Crops (MoFEC) and the German Technical Cooperation Agency (GTZ), showed that the fires affected the entire Mahakam basin, its tributaries and spread as far as the Sangkulirang peninsula (Siegert and Hoffmann 1999). Many forest concessions as well as forest and industrial crop plantations were severely burned. In August 1998 the Sustainable Forest Management (SFMP) project (MoFEC/GTZ), proposed an Actions After Forest Fire in Natural Forest Concessions Program to the MoFEC. The proposal included the following five steps be implemented in fire-affected concessions operating in natural forest lands (HPH: Hak Pengusahaan Hutan):
Conduct a low-intensity fire damage inventory (separately for each fire affected forest concession)
Develop rehabilitation maps for all heavily damaged areas
Improve the fire prevention and management system of each forest concession
Shift logging activities: stop logging in unburned areas and conduct salvage felling of dead trees in burned areas (where possible)
Adjust the Annual Allowable Cut (AAC) of each fire affected natural forest concession to a sustainable level and revise the long term forest planning (RKPH) accordingly
In order to obtain a data basis for this five-step proposal IFFM and SFMP jointly conducted on request of the MoFEC a study using ERS-2 SAR (European Radar Satellite 2, Synthetic Aperture Radar sensor) spaceborne radar images to disclose the size of the fire affected area for the entire province according to all land uses. Fire damage was assessed by discriminating three damage classes which are explained in the footnote of Table 1 (Hoffmann et al. 1999a, Siegert and Hoffmann 1999, Siegert and Rücker 1999a,b). The Directorate of Forest Inventory and Land-use Planning (INTAG) and the two MoFEC- GTZ projects further agreed to develop a revised forest land-use map, exposing the actual locations and boundaries of the current forest and industrial crop utilization right holders, in East Kalimantan. The overlay of the radar survey results with the actual forest land use boundaries revealed the fire damages for each land-use type. Furthermore the data is intended to support the provincial agencies to revise the current land-use plan of East Kalimantan. It shall be used as basis for the implementation of appropriate salvage felling activities, rehabilitation measures and adjustments of the long-term forest planning in each natural forest concession. Moreover, the data will be used within the IFFM Fire Information System to point out future fire hazard and fire risk zones in East Kalimantan and hence support fire management planning, prevention work and fire suppression (Hoffmann et al. 1999b).
The results of the ERS-SAR radar inventory show that the 1997/98 fires affected a total of 5.2 million ha – corresponding to ca. 25% of the total land area of the province. Almost 2.3 million ha are located in natural forest concession areas (56 HPH and Ex-HPHs), 0.4 million ha in protected forests, and 0.9 million ha 30 HTI forest plantation enterprises (HTI: Hutan Tanaman Industri) and 0.7 million ha industrial crop plantations were affected. Almost 75% of the plantation areas (forest, oil palm, etc.), that were located within the 1997/98 fire zone, have been fire affected, a large number of them severely. This demonstrates the very high fire risk of types of all plantations. Table 1 shows an overview of the fire damage related to the current land-use system.
Fig.1. Fire damage classification of the 1997-98 fires in East Kalimantan, Indonesia, based on ERS-SAR images.
Tab.1. Overview of area burned in East Kalimantan, Indonesia, in 1997-98 related to land-use classes and damage levels (see footnote).
* The damage classes 3 and 4 represent two different conditions of severely damaged forests. Damage class 3 represents the conditions prevailing in the (peat-) swamp forests of the Middle Mahakam lake area where almost the entire area was affected by fire. The dead trees are still standing. This condition provides a high future fire risk given the high fuel loads remaining after the fires. Damage level 4 includes forest plantations, degraded forest, bush and grassland as well as farmland.
The recent loss to forest economy is immense, considering short and long term economic losses to the natural forest alone. In 1982/83 a severe fire catastrophe had already occurred in East Kalimantan, damaging 3.5 million ha of land and forest. Out of this 0.8 million ha was primary forest and 1.4 million ha was logged-over forest (Lennertz and Panzer 1983). In 1997/98 the area of the 1982/83 fire burned again to an even greater extent, particularly towards the west, north-west and south west. The long term effects due to repeated damage, the loss of natural regeneration and the need for large scale rehabilitation under the high risk of future fires by far outnumber the short term losses. Without financial support many areas will not be successfully rehabilitated. Active rehabilitation of natural forest concession areas is mainly needed in areas with a fire damage greater than 50%. It can be expected that most of the former well stocked areas with a 25-50% fire damage will recover naturally, especially if further damage through logging does not occur. This still leaves a rehabilitation area of almost 1.6 million ha in the natural forest concessions alone. Funding and investment security are the largest obstacles to be overcome before effectively starting forest rehabilitation.
After the 1997/98 fires the forest is much more susceptible to fire due to degradation and accumulation of fuel and thus now even during normal dry seasons it will be prone to fires. Furthermore, El Niño events are predicted to occur more frequently than in the past, creating conditions that could trigger even more fires in the future. Land use conflicts between the local people and concession and plantation owners, carelessness and land clearing using fire can under these conditions easily bring forest activities to an end. Already many degraded and undefined land use areas are prone to Imperata cylindrica (alang-alang) grassland cycles, where fire becomes a part of the succession cycle. Therefore fire management is a key issue in achieving the goal of sustainable forest management.
To have further action on the 1997/98 fire catastrophe and to be prepared to prevent future fire disasters the following recommendations are proposed:
Implement and control the “Actions after Forest Fires in Natural Forest Concessions”
Revise provincial land use map (RTRWP) based on the 1997/98 fire damage
Stop conversion in unburned areas and concentrate plantation activities in depleted and/or heavily burned areas
Stop illegal cutting of living trees in salvage felling areas to support natural regeneration and successful rehabilitation
Develop financial support schemes for large scale rehabilitation activities
Revise the long term planning of the fire affected natural forest concessions
Implement an integrated fire management, prevention and information system at the regional as well as on concession levels
Anja A. Hoffmann Integrated Forest Fire Management IFFMGTZ,
Jln Harmonika, Perkantoran Dinas Kehutanan
P.O. Box 1202
& Max Planck Institute for Chemistry, Biogeochemistry Department, Fire Ecology and Biomass Burning Research Group & Global Fire Monitoring Center (GFMC),
c/o Freiburg University
D-79085 Freiburg, GERMANY
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