The 1997 Southeast Asian haze was a large-scale air quality disaster which occurred during the second half of 1997, its after-effects causing widespread atmospheric visibility and health problems within Southeast Asia. The total costs of the Southeast Asian haze are estimated at nine billion dollars(US) due mainly to health care and disruption of air travel and business activities.
The influence of the 1997 fires in Kalimantan and Sumatra on ambient air quality was evident by July and peaked in September/October before weakening by November, when the delayed monsoonal rain extinguished the fires and improved air quality within the region. During the peak episode, satellite imagery (NASA/TOMS aerosol index maps) showed a haze layer which expanded over an area of more than 3 million km², covering large parts of Sumatra and Kalimantan. Its northward extension partially reached Malaysia, Singapore, Brunei and Thailand. During this period, particulate matter concentrations frequently exceeded national ambient air quality standards. Monthly mean horizontal visibility at most locations in Sumatra and Kalimantan in September was below 1 km and daily maximum visibility was frequently below 100 metres.
Causes
The 1997 Southeast Asian haze was caused mainly by slash and burn techniques adopted by farmers in Indonesia. Slash and burn has been extensively used for many years as the cheapest and easiest means to clear the lands for traditional agriculture. Fire is also used during the long fallow rotation of the so-called jungle rubber in Sumatra and Kalimantan to remove most of the biomass, including the woody parts before new plantations are re-established.
Fire may also be deliberately used as a weapon to claim property on the islands and provinces where land ownership is not clear, an action taken by both smallholders and large operators alike. After burning out its previous owner, the smallholder or large operator plants their own crops there, gaining de facto control over the disputed land.
During the fire season, dry fuels readily ignite and lead to large wild fires. These accidental fires may have the same underlying socio-economic and institutional problems. In cases like this, fire suppression can be very difficult and costly especially when they reach the highly flammable peat-swamp areas.
Effects
Particulate matter was the air pollutant that predominantly contribued to the haze and degradation in ambient air quality standards during this crisis. In all countries affected by the smoke haze, an increase of acute health outcomes was observed. Health effects; included emergency room visits due to respiratory symptoms such as asthma, upper respiratory infection, decreased lung function as well as eye and skin irritation, were caused mainly by this particulate matter. In Singapore, for instance, health surveillance showed a 30% increase in hospital attendance due to air quality related symptoms. Generally, children and the elderly, as well as those with pre-existing respiratory and cardiac diseases were the most susceptible to adverse health outcomes from the haze exposure. The smoke haze episode has added to the urban and industrial air pollution in Southeast Asia, causing it to reach alarming levels in many metropolitan areas.
By scattering and absorbing light, the fire-related particulate also resulted in reduced visibility; impairing transportation by air, land and water and seriously affecting the economies of Indonesia, Malaysia and Singapore. Among the economic sectors affected most were air, land and sea transportation, construction, tourism and agricultural industries. EEPSEA/WWF roughly estimated the economic value of the damages caused by the 1997 fires and haze. They estimated one billion US$ from haze-related damages for Indonesia only. The damages to Malaysia and Singapore are figured at 0.4 billion US$. Including the fire related damages, the total damages are estimated to amount to 4.5 billion US$. However, a variety of the damages such as decreased quality of life, loss of biodiversity and atmospheric impacts are difficult to establish.
Fire-related smoke haze episodes also reveal a social component: a large part of the population in Southeast Asia do not have the financial means to buy protective measures such as respiratory masks and air conditioning, nor are they able to refrain from outdoor work when air pollution is high.
Responses in the region
The 1997/98 smoke haze episode resulted in an intensification of regional measures towards cooperation in fire and smoke management which were initiated in the aftermath of similar episodes in 1991 and 1994. These measures include the establishment of ASEAN Haze Technical Task Force and the implementation of Regional and National Haze Action Plans. These plans define the ASEAN’s countries contributions to fire prevention, monitoring, fighting and other mitigation measures. Among others, it is also targeted to upgrade the national air quality and meteorological monitoring networks in order to strengthen the region’s early warning and monitoring system in respect to smoke haze.
This incident made evident that in addition to sound fire management, a fundamental revision of the current land conversion and fire use policies is required to prevent the reoccurrence of similar episodes. Ground-based and airborne investigations of the smoke haze indicated that fires on peat swamp vegetation made a substantial contribution to the smoke haze development. However, this vegetation is estimated to have contributed only 30% of the total area burnt. Given this apparent particular relevance of peat swamp fires to the development of transboundary smoke haze, emission reduction and control strategies will have to focus on the prevention of fires in this type of vegetation as a matter of priority.
Future land use management will also have to consider 'air use' management. The health impacts and economic damages of the 1997/98 haze demonstrated that controlling future haze events represents an influencing factor for public and economic prosperity in the Southeast Asian region.
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