As a response to the global recurrence of vegetation fires, WHO, in collaboration with UNEP and WMO has developed the WHO-UNEP-WMO Health Guidelines for Vegetation Fire Events. The guidelines are intended to develop the necessary capacity, to give WHOs support to local planning efforts in health, environment and sustainable development; to strengthen the basis for inter-sector action in sustainable development policy and planning, by providing the necessary evidence and guidance; to determine best practices and disseminate such knowledge worldwide; to strengthen the linkages between health, environment and development; to provide ongoing support in the development and implementation of the Regional and National Haze Action Plans. This paper introduces into the objectives, scope and results of the guidelines.
Smoke pollution due to vegetation fire events is an important public health issue and involves major risks for the health of the people and the environment. Vegetation fires in Asia, Latin America, Africa, and other parts of the world are recurring phenomena. They often lead to health impacts such as increased mortality, increased hospital admissions due to respiratory and cardiovascular diseases, and increased emergency room and outpatient visits. Smoke from vegetation fires sometimes even overlies urban air pollution, and exposure levels are intermediate between ambient air pollution and indoor air pollution from domestic cooking and heating.
For several months in 1997-98, the smoke disaster in Southeast Asia affected several countries including Brunei Darussalam, Indonesia, Malaysia, Singapore, Philippines, and Thailand, as well as tens of millions of people in the region. Authorities of these countries have taken measures to mitigate smoke effects on population health and to control forest fires. This was particularly the case for Indonesia, which officially requested UN assistance. The fires threatened to evolve into a more complex emergency, through the potential of causing voluntary or planned population movement (evacuation), and through effects on health, economy and security. In such an emergency the development of an early warning system would involve the multidisciplinary collaboration of scientists, technicians and administrators.
As a response to this emergency, the World Health Organization convened a meeting in October 1998 in Lima, Perú, to develop the WHO-UNEP-WMO Health Guidelines for Vegetation Fire Events (WHO/UNEP/WMO 1999a) on the basis of background papers written on the involved multidisciplinary issues by several experts. The Health Guidelines comprise three separate documents. The Health Guidelines for Vegetation Fire Events Guideline document is a comprehensive handbook with the objective of providing guidance to Governments and authorities from municipalities on the action to be taken in vegetation fire events, when large parts of the population are exposed to smoke from fires. It has to be seen as the main document that summarises the experience and knowledge laid down in the background papers. These background papers are published separately in the document Health Guidelines for Vegetation Fire Events – Background Papers (WHO/UNEP/WMO 1999b). A third document entitled Health Guidelines for Vegetation Fire Events Teachers Guide (WHO/UNEP/WMO 1999c) compiles educational materials that can be used in training courses on the Health Guidelines for Vegetation Fire Events.
The WHO-UNEP-WMO Health Guidelines for Vegetation Fire Events (hereafter referred to Health Guidelines) are intended:
To advise national and international authorities on how to develop and implement an early warning system to protect the health of the population exposed to air pollution caused by vegetation fire events.
To provide support in capacity building and in the development and implementation of the Regional, National, and Local Haze Action Plans. These plans will be integrated into national sustainable development planning efforts, as parts of the Environmental Action Plans;
To provide the necessary evidence and guidance on vegetation fires and their health impacts, to strengthen the basis for inter-sector action in sustainable development policy and planning;
To determine best practices, and disseminate such knowledge worldwide, with the objective of strengthening our understanding of the linkages between health, environment and development.
The Health Guidelines provide decisive recommendations on how to make optimal use of the vast amount of multidisciplinary information that is available worldwide. This information includes knowledge of the global, regional and national extents of vegetation fires obtained by remote sensing techniques and characterises the sources with respect to strength and pollutants. The development of an early warning system is based on ground-base monitoring, space and climate monitoring and modelling. The Health Guidelines also provide insight into the acute and chronic health effects of air pollution due to vegetation fires (“biomass burning”), advise on public advisories and mitigation measures, and provide guidance on the methodology for assessing the health impacts of vegetation fires. Important issues are the prevention of future health-affecting events through discussion of land-use and fire policies, and recommendations on scientific work to be performed in the future in order to implement the early warning system.
According to the Health Guidelines, fires in forests and other vegetation produce gas and particle emissions that have impacts on the composition of the global atmosphere. These emissions interact with those from fossil-fuel combustion and other technological sources which are the major causes of urban air pollution. Smoke emissions from wildland fires cause visibility problems which may result in accidents and economic losses. Smoke generated by wildland fires may also affect human health and lead to loss of human lives. The development of policies and guidelines for reducing the health impacts of smoke from burning vegetation must be linked with policies which address the smoke problem at its source. Therefore, the Health Guidelines help to greatly reduce the burden of excess mortality and preventable disability suffered particularly by the poor. With this in mind, the Health Guidelines implement health gains that, in turn, trigger economies to grow and poverty to be cut.
The Health Guidelines emphasize that early warning systems of fire and atmospheric pollution are essential components of fire and smoke management. They may involve locally generated indicators, such as fire-weather forecasts and assessment of vegetation dryness. Advanced technologies for detection and monitoring of fires, however, rely on remotely sensed data, evaluation of synoptic weather information, modelling capabilities of fire occurrence and behaviour, and international communication systems. These data are integrated and processed with other relevant information, such as the population at risk, and disseminated in fire information systems.
The Health Guidelines are intended to ensure that the health components of Agenda 21 of the United Nations Programme of Action, following the Earth Summit in Rio de Janeiro, are adequately addressed so that health gains trigger economies to grow and, subsequently, poverty to decrease.
Emission, transport of air pollutants and exposure
The Health Guidelines have compiled the information on major fire events in the world and their health and economic effects. Wildfires (uncontrolled fires) are common in all vegetation zones. They are mostly caused by negligence and are often associated with escaped land-use fires. Biomass burning is a major contributor of toxic gaseous and particle air pollutants and occurs throughout the world. The nature of biomass burning is such that the combustion is not complete, and as a result a large number of pollutants are emitted. Among the air pollutants emitted from biomass fires are widespread pollutants such asparticulate matter, oxides of nitrogen, sulphur dioxide, and carbon monoxide. But unlike some anthropogenic sources, emissions are poorly quantified (also see Goldammer 1999).
After the emission, during transport, the air pollutants undergo transformation processes, which result in physico-chemical changes of the pollutants.
According to the Health Guidelines, comprehensive approaches to be standardized for use in dealing with potential risks to public health of emissions from vegetation fires should include:
Characterization of the magnitude and composition of the emissions and their transformations during transport;
Quantification of resulting concentrations of ambient air pollutants in populated areas;
Evaluation of likely exposure scenarios for affected populations (both indoors and outdoors);
Assessment of consequent health risks posed by such human exposures.
It is pointed out in the Health Guidelines that with respect to the exposure to smoke plumes from biomass burning and corresponding health effects, particles receive the most attention of all air pollutants that have potentially detrimental health effects. Very small airborne particles (aerodynamic diameters below 2.5 m m) are considered the most significant pollutants. These particles have a very high probability of deposition in deeper parts of the human respiratory tract, where they may lead to a range of health impacts by virtue of their physical, chemical, toxicological or carcinogenic nature (also see Ward 1999).
In view of the multidisciplinary approach of the Health Guidelines, harmonisation of the various approaches is considered a very important issue. Ground-based air quality monitoring and remote sensing through satellite imagery are necessary to assess air pollutant concentrations of smoke caused by vegetation fires. The Health Guidelines give several recommendations with respect to monitoring. Ground-based air quality monitoring should aim to provide information for public health warning and decision making on protective measures, for dispersion model inputs, verification and development, and for human health studies that evaluate effects of smoke. Air quality monitoring should be conducted on a regular basis in major urban and other populated areas likely to be impacted by biomass burning. In addition, stations should be located in rural areas, for background concentration information. Existing networks should be reviewed and the best sites for monitoring smoke and haze episodes identified. Establishment of additional monitoring stations in areas not covered by the existing networks should be considered. The location of the sites should be determined in accordance with existing guidelines. A ground-based network of air samplers is necessary to measure the concentration of aerosols for sizes under 2.5 m m in diameter (for further reference see Grant 1999; Ward 1999).
In measured compounds efforts should be made to separate the contribution of biomass burning from that of other sources. Monitoring of aerosol mass, visibility, meteorological parameters, optical depth and solar radiation are of highest priority. At selected sites, targeted chemical quantities such as carbon monoxide, ozone, nitrogen oxides, sulphur dioxide, carbon dioxide, ultraviolet radiation, aldehydes and other trace pollutants should be measured.
Formulation of uniform protocols for sampling, including temporal resolution and reporting procedures, should be established. The establishment of quality assurance/quality control procedures is essential for obtaining reliable and reproducible results. National and regional databases should be established for use of data before, during and after smoke/haze episodes. These data can be used, for instance, in epidemiological studies, planning for future events and for transport modelling studies. The exchange of validated measurement data should be promoted. The different air pollution indices that are used in regional smoke and haze alerts should be harmonized.
To maximize the usefulness of data collected by different networks, participation should be encouraged in international activities such as the Global Atmosphere Watch programme of the World Meteorological Organization or the Air Management Information System of the World Health Organization.
The Health Guidelines summarise the existing knowledge on satellite imagery and future developments in the field of remote sensing. Satellite data are available for monitoring fires and smoke aerosol, e.g., at the National Aeronautics and Space Administration (NASA) or the National Oceanic and Atmospheric Administration (NOAA) of the United States. Satellite imagery provides information on the dryness of the vegetation, location and size of major fires and smoke plumes, energy released by fires, and air pollutants in the smoke plumes. Additional satellite sensors delivering better data on vegetation fires will be available within the next 1-2 years. With respect to accessibility and evaluation of these data, it is recommended that a centre of excellence in fire and smoke monitoring be established. The centre should be familiar with the technology and software for analysing satellite data. Its responsibilities would be to oversee the regional estimates of fire emissions and to validate the smoke and emission analyses of satellite data. The centre should develop new strategies for fire and smoke detection and advise the international bodies and agencies of its needs. It would also integrate ground-based, aircraft and satellite information. It would work with the regional centres in disseminating information and new technology to the regional centres, as well as co-ordinate the training of technicians to handle new satellite data and software.
It would also be important to establish an indicator for grading the severity of on-going fires. Such an indicator could combine satellite data on the number of active fires per unit area, size of the areas burning, energy released by the fires, the extent the smoke palls and the concentration of pollutants in them. Also recommended is the development of a space fire monitoring system, comprising fire detection satellites and real-time portable receiving hardware, to provide diurnal information on the location of active fires, smoke, and trace gases emitted from the fires. If possible, the information generated by this system should be provided directly from the satellite to local users in near real-time, in a simple and inexpensive manner.
On a regional level there is a need for fire activity centres. These centres would receive the regional satellite data using their own receiving stations, and integrate them both with meteorological information and with ground and aircraft monitoring efforts. The centres would use the data to monitor the development of the fires and smoke and predict the spread of the smoke. The centres are needed since the characteristics and amounty of vegetation burning change from region to region, and since direct reception of the satellite data is essential for real time operation. As there are already WMO centres or representatives with satellite and meteorological capability, they are natural candidates for the location of the regional fire activity centres.
With respect to data availability, it is recommended that NASA and NOAA of the United States and other appropriate agencies be approached to continue placing relevant data such as aerosol and vegetation indexes on the Web. There is a need to develop software packages and instruction material for using satellite data to warn of smoke impacts and to analyse smoke concentrations. Where extensive and intense fire episodes cause severe health problems the reliability of the fire emission estimates should be ensured by continuous validation, using ground based in situ and remote measurements. Such validation will enhance the use of satellite data as input to the simulation model. Once developed, the software packages would also support the determination of environmental hazards for human health.
Atmospheric transport models
With respect to the evaluation of ground-based monitoring data and satellite imagery for the purpose of early warning, the Health Guidelines recommend the use of dispersion and trajectory modeling. The distribution and concentrations of fire emissions must be calculated from atmospheric transport models. A description of the spatial and temporal distribution of fire emissions should consider the situation before, during, and after the episode. Defined goals are to be achieved in each of those three stages of the event. It is recommended that the agency capable of carrying out the complete suite of tasks associated with climate monitoring and modelling be identified in each area (further see Garstang 1999; Tapper and Hess 1999)..
The Health Guidelines discuss the various mitigation measures that are appropriate to avoid human health effects. Mitigation measures recommended for acute events include remaining indoors, personal lifestyle modifications, use of air cleaners, use of masks and respirators, outdoor precautionary measures, evacuation to emergency shelters, and school and business activities. To enhance the protection offered by remaining indoors, individuals/building managers should take action to reduce the infiltration of outdoor air. Schools, childcare centres, retirement centres, nursing homes, hospitals and hospices should be especially urged to provide air conditioned rooms to susceptible individuals, and effective filters should be installed and maintained in these rooms. During severe smoke episodes, members of the public should be advised on lifestyle modifications, such as the reduction of physical activities and the restriction of cigarette smoking. Evaluation of the use of portable air cleaners should be conducted and appropriate advice given to the public, to assist them in purchasing models suitable for homes or offices. Advice should be given to the public on specific dust/mask respirator types and their relative utility for filtration of smoke particles, including the proper use and selection of available dust masks/respirators. Precautionary measures should be taken to safeguard the health and safety of workers who must continue to perform outdoor work. For example, employers should provide respirators to workers who must work outdoors during acute emergencies. In severe episodes, susceptible individuals should be allowed free access to air-conditioned emergency shelters (with adequate particle filtration). These could be located inside large commercial buildings, educational facilities or shopping malls.
Based on the background papers provided by several authors (Pinto and Grant 1999; Brauer 1999; Malilay 1999; Mannino 1999) the Health Guidelines summarize the existing information on the health effects of smoke generated by biomass burning (“biomass smoke”). In addition, the results of several case studies were evaluated (Levine 1999; Kunii 1999; Dawud 1999; Phonboon et al. 1999). The epidemiological studies of indoor and community exposure to biomass smoke indicate a consistent relationship between exposure and increased respiratory symptoms, increased risk of respiratory illness and decreased lung function. A limited number of studies also indicate an association between biomass smoke exposure and visits to emergency departments. Recent assessments of impacts from the 1997-98 Southeast Asian haze episode support an association with increased hospital visits. Studies of the relationship between biomass-smoke air pollution and acute mortality have not been conducted to date. However, as biomass-smoke air pollution mostly consists of fine and ultra-fine particulate matter the new air quality guidelines of the WHO for particulate matter suggest a definite impact on daily mortality, hospital admissions, emergency department visits and outpatient visits.
The health effects of long-term inhalation of smoke generated by burning of plant biomass have been documented in developing countries where women spend many hours cooking over non-vented indoor stoves (also see Brauer 1999). These studies indicate that vegetation fire smoke exposure is associated with the development of chronic lung disease in adults, although these exposures are much higher than would occur as a result of short-term exposure to air pollution associated with vegetation fires. These studies do indicate the serious consequences of exposure to high levels of smoke pollution. The limited data on biomass burning smoke and cancer do not indicate an increased risk even at very high levels of exposure. This evidence includes studies of long-term exposure to high levels of smoke from domestic cooking in developing countries. While biomass burning smoke clearly is potentially carcinogenic, it is much less so than motor vehicle exhaust.
Assessing the health effects of smoke from vegetation fires is a difficult task. Critical factors in ascertaining the health effects of air pollution include: characteristics of the pollutants, population exposure, individual exposure, susceptibility of the exposed individual, potential confounding factors, and the range of health effects being studied. The availability of data on these factors greatly affects the type of study that might be undertaken. Types of study designs in air pollution epidemiology vary widely and include: short-term controlled exposure studies (chamber studies), short-term exposure studies, and long-term exposure studies (also see Mannino 1999). The latter two designs reflect a typical epidemiological approach to the problem of air pollution exposure. Any type of study requires careful planning of the design, implementation and analysis. During an emergency there may be a need to conduct a rapid epidemiological assessment, focusing on the demographics and health concerns of people in the affected community.
An important component of a public health plan to deal with pollution-related exposure is a surveillance system for monitoring respiratory or cardiovascular diseases (also see Mannino 1999). While many countries have such a system in place for infectious diseases, very few have a similar system in place for noninfectious diseases. With the increasing numbers of computerized clinical databases, however, it may be possible to set up a surveillance system for diseases that would be affected by fire-related air pollutants. Before a fire emergency a health department could, potentially, set up a surveillance system looking for chronic cardio-respiratory diseases. If this was in place, changes in these diseases could be assessed during a fire episode. In the absence of such a surveillance system, it is unlikely that any active surveillance would provide reliable information that a public health department could act on. After a fire episode several research designs, as noted above, are available to health departments who want to determine what health effects the fire episode had and who want to use the data to shape future policy.
The Health Guidelines consider and summarise public policies in various countries (also see Bakar bin Jaafar 1999; Marileo 1999; Johnson 1999; Ooi et al. 1999; Phonboon 1999). In this discussion the policy objectives and policy elements referring to development, assessment and management are described. These elements are ingredients of national haze action plans. The lessons learned from the 1997-98 fires in South-East Asia are important to avoid the recurrence of such an emergency in the future. A number of topics are enumerated in the Health Guidelines that need further research.
With regards to Policy Objectives, the elements to be considered are:
To prevent and control land and forest fires;
To safeguard public health and safety in such an occurrence;
To prohibit open burning;
To introduce and implement ambient air quality guidelines and standards;
To strengthen control on emissions from mobile and stationary sources.
The elements with respect to Policy on Development are:
To set land use planning based on a sustainable development principle;
To protect communities and ecosystems at risk from fire and haze effects.
The elements with respect to Policy on Assessment include:
To monitor and report on air quality;
To develop an effective mechanism for monitoring land and forest fires;
To develop the capability for detecting and predicting forest fires and haze;
To monitor the health and environmental impacts of haze.
The Management Policies focus on the following aspects:
To provide the public and the authorities with information on air quality and action to be taken;
To advise the public on action to be taken for health protection;
To ensure medical facilities and health supplies for mitigating health impacts;
To provide support to countries in need and to promote cooperation among countries;
To minimize haze pollution from fuel burning;
To strengthen the capabilities of relevant agencies;
To strengthen interagency cooperation and support.
As the Health Guidelines stress, the success of any policy, action plan, or response mechanism will rest on the timely exchange of data, information and experiences among various national, regional, and international authorities or centres of excellence, and on their close co-operation and continuing support. Institutional arrangements at international and regional levels need to be developed and used. Early warning capability is invaluable to national authorities trying to enforce strict controls on both controlled and open burning of vegetation, crops, forest, and any form of biomass or waste (also see Goldammer 1999). During a fire, national authorities should consult competent international bodies for advice. These international bodies should investigate the feasibility of establishing an ongoing panel of experts on haze, whose members are linked via electronic media for the rapid exchange of data and information.
Among the critical components of national governments efforts to manage vegetation fires is the education of the population regarding the potential health impacts of air pollution produced in vegetation fires. These education efforts must occur both prior to, and during, fires to keep the population informed.
National Haze Action Plans
The Health Guidelines emphasise the necessity of developing National Haze Action Plans to ensure full preparedness of the population for the health impacts of vegetation fire pollution. In each country, a comprehensive National Haze Action Plan should be developed and widely publicized through the media, before the occurrence of any air pollution episode. Based on this action plan, government departments should develop operating procedures and ensure that the population will be aware of any changes made to public services and facilities in an emergency situation. Data on air pollution related illnesses from primary health care providers, hospitals, and mortality registries should be reported periodically. Special educational efforts should be developed for susceptible populations, such as asthmatics, the elderly, and children to ensure that they are adequately prepared for air pollution episodes. Health authorities, via the media, should proactively address frequently asked questions, such as the safety of food and potable water supplies exposed to smoke for prolonged periods.
Lessons learned from the 1997-98 fires
In reviewing the 1997-98 fire and smoke episodes, the Food and Agriculture Organization (FAO) of the United Nations evaluated those public policies which affect forest fires (FAO 1999). The expert consultation concluded that there is a need for reliable national, regional and global systems for fire reporting and for analysis and storage of data. Such data, and information on fire causes and socio-economic and environmental effects, are required as a sound basis for policy making. Linked to these is the requirement for international agreement on terms and definitions, as a basis for information sharing and communication. Information on resource management alternatives and their consequences is essential for involvement of all stakeholders in policy formulation and development.
No single formula can cover the wide range of ecological, socio-economic, and cultural conditions that exist between and within regions, nor cover the different objectives that different societies will decide. Certain broad principles exist, however, that are common to all situations and objectives. These principles include the following (FAO 1999):
The formulation of national and regional policies specifically addressing forest fires, as an integral component of land-use policies, where they previously did not exist.
Flexibility in policy implementation, and the capability of reviewing and revising fire-related policies
Clear and measurable policy objectives and implementation strategies are needed to minimise the many adverse effects of uncontrolled fires, and to maximise the benefits from fire prevention, or from the controlled use of fire. Such objectives and implementation strategies would provide for sustainable land use practices, compatible inter-sector policies, joint fire management responsibilities at the community level, and the participation of the private sector and non-governmental organizations. Decision makers should recognize that sustainable land management may, in many instances, be attained only through the devolution of the control of forest resources, and through the involvement of communities, adjacent to or within the forest, in all aspects of management and fire protection. Land-use policies may also have to consider the need for appropriate incentives and subsidies to promote fire prevention.
A favourable policy environment must be created for all aspects of systematic fire management (prevention, detection, suppression, prescribed fire, post-fire rehabilitation etc.) and for an appropriate balance among individual system components. Such an environment should attempt to quantify the monetary and non-market values, to emphasise the costs and benefits to society and to decision-makers.
Policies that tend to increase forest fires must consider public health effects. Policies concerned with maintaining the health of fire-adapted ecosystems may have to balance public health and forest health issues.
The Health Guidelines fully support these principles. Continued and improved collaboration and co-ordination are urged among the many organizations involved in forest fire-related activities at global and regional levels. Transboundary or regional agreements for collaboration in fire management need to be developed, with the technical and financial support of international organizations. International organizations, in close collaboration with the fire science community and end-users, are further urged to support the design and implementation of a global fire inventory or reporting system, to increase preparedness and responsiveness to fire outbreaks at national, regional and global levels. International organisations should play a catalytic role in the establishment of networks, to promote the sharing of information and technical co-operation among developing and developed countries. Sufficient resources should be allocated for these purposes.
Accumulated experience should not be neglected, and local indigenous knowledge and customs should be acquired from traditional fire related cultures as a guide for fire management practices and policies. Evaluation systems should be developed to assess fire damage and benefits, and to draw attention to the true costs and benefits of fires. Policies and techniques that aim to increase agricultural productivity, while providing and enforcing disincentives for reckless programmes, will slow forest conversion for unsustainable agriculture and will thus reduce forest fire damage.
According to the Health Guidelines, some technical aspects may support policy formulation and implementation. They include systematic or integrated fire management; institutional co-operation; restoration/rehabilitation; and technology/research/information. New technologies offer the means to introduce new and more environmentally and socially acceptable land use management policies; particular attention is drawn to “zero-burning” land clearing techniques. Fire research at national and regional levels needs to be strengthened, to support development of fire policies and fire management capabilities, especially related to investigations into socio-economic and cultural aspects of fire outbreaks. Fire research is needed into a number of topics including:
The development of dedicated space-borne remote sensing technologies for improving decision support in fire management, including technologies for fire detection and early warning;
Post-fire recovery techniques, fire effects and ecosystem recovery processes;
The impact of climate change on fire regimes and fire severity;
The implementation of a global vegetation fire inventory, and the implementation of a center to monitor, archive, and disseminate global fire information, as well as forecast fire and related hazards;
Special attention to fire-generated radioactive emissions;
The development of source information for fires in different ecosystems;
Physical/chemical factors contributing to the changes that occur over time and space during transport;
Compilation of information pertaining to levels of exposure and fire activity, in conjunction with past fire and smoke episodes;
Health impacts of air pollution due to biomass burning within the general population.
According to the WHO-UNEP-WMO Health Guidelines the situation with respect to the occurrence of forest fires, the potential health effects of smoke from vegetation fires, their mitigation and early warning of the populations are to be summarised as follows. Vegetation fires, particularly uncontrolled ones, are a substantial source of air pollution in urban and rural areas. They add to urban and indoor air pollution (from domestic wood and coal burning for cooking and heating). Inhaling the smoke from vegetation fires enhances the risk of acute respiratory infections in childhood, a major killer of young children in developing countries. The health of women is also particularly affected as women are already exposed to high levels of air pollution in the home environment and they suffer more from this additional burden of pollution caused by vegetation fires. Land clearing practices through vegetation fires add to rapid environmental changes and degradation. The use of forest fires for land clearing is also a consequence of poverty. Combating poverty is the central challenge to ensure sustainable development and healthy living conditions. As health is so dependent on environment, there is a need to address the global dimensions of the problem of forest fires.
Vegetation fire events are an important public health issue since they involve major risks for the health of the people and the environment. Because of their nation- and region-wide effects, vegetation fire events can evolve from a sort of “natural” disaster into a more complex emergency because of population movement, and through their effects on the economy and security of the affected countries. In view of the character of a potentially complex emergency from vegetation fire events, the development of an early warning system for such events involves the collaboration of multidisciplinary groups of scientists, technicians and administrators. The Health guidelines provide the knowledge for implementing an early warning system to protect human health from the impacts of smoke and haze from vegetation fires and, therefore, help governments to cope with the recurring events.
The Health Guidelines are intended to develop the necessary capacity not only at regional and national levels, but also at local levels. In addition, to give WHOs support to the local health, environmental and sustainable development planning efforts being undertaken. The Health Guidelines provide the necessary evidence and guidance for strengthening inter-sector action in sustainable development policy and planning. They aso determine best practices, and disseminate such knowledge worldwide. They strengthen the linkages between health, environment and development; and provide ongoing support in the development and implementation of the Regional and National Haze Action Plans, as part of Environmental Action Plans to be integrated into national sustainable development efforts.
The Health Guidelines for Vegetation Fire Events help to ensure that the health components of Agenda 21 of the United Nations Programme of Action, following the Earth Summit in Rio de Janeiro, are adequately addressed.
The Health Guideline for Vegetation Fire Events are a result of the work of two departments of the WHO: the Department of Emergency and Humanitarian Action (EHA) and the Department of Protection of the Human Environment (PHE), both in the Cluster of Sustainable Development and Healthy Environment (SDE) of the WHO. This report would not have been possible without the work of the WHO-UNEP-WMO Expert Task Force convened in Lima, Perú, in October 1998. Thanks are due to Abu Bakar bin Jaafar, Celso Bambarén, Michael Brauer (Workshop co-chair), Harold Cáceres Deza, Sergio Caporali, Hashim Daud,Yudanarso Dawud, Michael Garstang, Goh Kee Tai, Johann G. Goldammer (Chair of the Health Guidelines Workshop), Hiremagalur N. B. Gopalan, William B. Grant, Angelika Heil, Mauricio Ilabaca Marileo; Liisa Jalkanen, Roy A. Johnson, Yoram Kaufman, Etsuko Kita, Marcelo Korc, Osamu Kunii, Arlene S. Levine, Joel S. Levine (Workshop co-chair), Sze Fook Lim, Carlos A. Llerena, Josephine Malilay, David Mannino, Lidia Morawska, Daniel Murdiyarso, Ooi Peng Lim, Kanchanasak Phonboon, Joseph P. Pinto, Jean Luc Poncelet, Robert R. Romano, Alberto Setzer, Khalid Shibib, Orman Simpson, Nigel J. Tapper, J. Hernán Ulloa-Pinto, Claude de Ville de Goyet, Darold E. Ward, Paulus Angus Winarso.
Particular thanks are due to the Ministry of Health of Japan, which provided ample funding to convene the WHO-UNEP-WMO expert task force meeting in Lima, Perú, in October 1998 to produce the Health Guidelines for Vegetation Fire Events including the Guideline document, the Background Papers document and the Teachers Guide. Moreover, this funding could be used to convene two training courses on the Health Guidelines, the first one in Kuala Lumpur, Malaysia in December 1998, and the second one in Brasilia, Brazil, in May 1999.
The contributions of the United Nations Environment Programme (UNEP) and the World Meteorological Organization (WMO) in co-sponsoring the expert task force meeting on the Health Guidelines are gratefully acknowledged.
This paper does not reflect the policy of the World Health Organization. The author alone is responsible for the views expressed in this report.
Dietrich Schwela Department of Protection of the Human Environment Occupational and Environmental Health Programme World Health Organization CH 1211 Geneva 27 Switzerland
Bakar bin Jaafar A 1999 Review of government environmental & health policies, legislation and emergency response mechanisms. In: WHO-UNEP-WMO (1999b), pp. 382-403.
Brauer M 1999 Health impacts of biomass air pollution. In: WHO-UNEP-WMO (1999b), pp. 186-257.
Dawud D 1999 Smoke episodes and assessment of health impacts related to haze from forest fires: Indonesian experience. In: WHO-UNEP-WMO (1999b), pp. 317-333.
FAO 1999 Meeting on Public Policies Affecting Forest Fires, Rome, 28-30 October 1998. FAO Forestry Paper 138. Food and Agriculture Organization of the United Nations, Rome, Italy.
Garstang M 1999 The role of the atmosphere in fire occurrence and the distribution of fire products. In: WHO-UNEP-WMO (1999b), pp. 102-122.
Goldammer JG 1999 Early warning systems for the prediction of an appropriate response to wildfires and related environmental hazards. In: WHO-UNEP-WMO (1999b), pp. 9-70.
Grant WB 1999 Analytical methods for monitoring smokes and aerosols from forest fires: Review, summary and interpretation of use of data by health agencies in emergency response planning. In: WHO-UNEP-WMO (1999b), pp. 87-101.
Johnson RA 1999 Guidance on measures in forest fire emergency cases. In: WHO-UNEP-WMO (1999b), pp. 412-466.
Kunii O 1999 Basic fact-determining downwind exposures and their associated health effects, assessment of health effects in practice: a case study in the 1997 forest fires in Indonesia. In: WHO-UNEP-WMO (1999b), pp. 299- 316.
Levine JS Gaseous and particulate emissions released to the atmosphere from vegetation fires. In: WHO-UNEP-WMO (1999b), pp. 284-298.
Malilay J 1999 A review of factors affecting the human health impacts of air pollutants from forest fires. In: WHO-UNEP-WMO (1999b), pp. 258-274.
Mannino DM 1999 Guidance on methodology for assessment of forest fire induced health effects. In: WHO-UNEP-WMO (1999b), pp. 275-283.
Marileo MI 1999 Role of the forest fire emergency standards. In: WHO-UNEP-WMO (1999b), pp. 404-411.
Ooi PL, Hakeem A, Goh KT, Brauer M 1999 Public information and mitigation measures for a haze episode: the Singapore experience. In: WHO-UNEP-WMO (1999b), pp. 467-485.
Phonboo K 1999 Application of appropriate short-term air quality guidelines. In: WHO-UNEP-WMO (1999b), pp. 486-492.
Phonboon K, Paisarn-uchapong O, Kanatharana P, Agsorn S 1999 Smoke episodes emissions characterization and assessment of health risks related to downwind air quality case study, Thailand. In: WHO-UNEP-WMO (1999b), pp. 334-381.
Pinto JP, Grant LD 1999 Approaches to monitoring of air pollutants and evaluation of health impacts produced by biomass burning. In: WHO-UNEP-WMO (1999b), pp. 149-185.
Tapper NJ, Hess GD 1999 Forest fire emissions dispersion modelling for emergency response planning: determination of critical model inputs and processes. In: WHO-UNEP-WMO (1999b), pp. 123-148.
Ward DE 1999 Smoke from wildland fires. In: WHO-UNEP-WMO (1999b), pp. 71-86.
Publications of the Guidelines:
WHO/UNEP/WMO 1999a Health Guidelines for Vegetation Fire Events Guideline document. D. Schwela, J.G. Goldammer, L. Morawska, O. Simpson (Eds.) United Nations Environment Programme, Nairobi, World Health Organization, Geneva, World Meteorological Organization, Geneva, Institute of Environmental Epidemiology, WHO Collaborating Centre for Environmental Epidemiology, Ministry of the Environment, Singapore (ISBN 981-04-1460-9)
WHO/UNEP/WMO 1999b Health Guidelines for Vegetation Fire Events – Background Papers.
Kee-Tai-Goh, D. Schwela, J.G. Goldammer, O. Simpson (Eds.) United Nations Environment Programme, Nairobi, World Health Organization, Geneva, World Meteorological Organization, Geneva, Institute of Environmental Epidemiology, WHO Collaborating Centre for Environmental Epidemiology, Ministry of the Environment, Singapore (ISBN 981-04-1460-9)
WHO/UNEP/WMO 1999c Health Guidelines for Vegetation Fire Events Teachers Guide. D. Schwela, L. Morawska, Abu Bakar bin Jaafar (Eds.) United Nations Environment Programme, Nairobi, World Health Organization, Geneva, World Meteorological Organization, Geneva, Institute of Environmental Epidemiology, WHO Collaborating Centre for Environmental Epidemiology, Ministry of the Environment, Singapore (ISBN 981-04-1460-9)
The Guidelines, the Background Papers and the Teacher’s Guide are also available on the internet: