Wildfires
Any unplanned and uncontrolled vegetation fire that, regardless of ignition source, may negatively affect social, economic or environmental values, and require suppression response or other action according to agency policy (FAO, 2024).
Primary reference(s)
FAO. 2024. Integrated Fire Management Voluntary Guidelines: Principles and strategic actions. Second Edition 2024. Fire Management Working Paper 41. Rome. DOI: 10.4060/cd1090en. Accessed 21 January 2025.
Annotations
Additional scientific description
Unplanned and uncontrolled vegetation fires (wildfires) may be started by natural causes (lightning, occasionally by burning coal seams or volcanic activity), or-predominantly at the global level-by human activities, primarily through the burning of live or dead vegetation in natural or anthropogenically altered ecosystems (Robinne et al., 2018). These ecosystems include forests, grasslands, shrublands (bush, scrub), organic terrain (peatlands, wetlands), cultivated lands (agricultural and pasture lands, plantations, abandoned cultivated lands) and protected areas (wilderness, conservation sites).
Landscape fire attributes and descriptors include:
- Fuel type (e.g., grass, shrub, forest, peat)
- Fire type (e.g., ground, surface, crown)
- Fire behaviour and emissions (e.g., spread rate, intensity, severity, radiative power, smouldering vs. flaming combustion, gas and particle emissions)
- Temporal and spatial features (e.g., creeping fires, spotting, flashovers, short- to long-duration events; single vs. multiple fires) (GFMC, 2013).
Wildfires may also affect residential and industrial areas, peri-urban fringes, critical infrastructure and remnants of human activities (e.g., waste deposits, mine sites, contaminated lands), potentially resulting in the co-burning of hazardous or toxic substances such as toxic gases (CH0300) and heavy metals (CH0100) (GFMC, no date).
In wildfire suppression, technology has clear limitations. Containment is often subject to weather and fuel conditions. A change in weather or fuel availability is frequently necessary to halt the spread of a wildfire. Understanding these limitations is essential to ensure safe and effective response while minimising risk to firefighters and the public (UNEP, 2022).
Metrics and numeric limits
Satellite data are processed to provide information on burned areas and numbers of fires along with national and agency fire recording and reporting.
FAOSTAT offers data on burned areas and associated emissions. The burned area data derive from the Global Fire Emissions Database Version 3 (GFED3), based on MODIS Collection 5.1 (MCD45A1) (FAO, 2020).
The Global Wildfire Information System (GWIS) provides statistics on average burned area and number of fires by region and country (GWIS, 2019).
Key relevant UN convention / multilateral treaty
The only regional legal agreement currently in place is the Agreement on Transboundary Haze Pollution of the Association of Southeast Asian Nations (ASEAN, 2002).
Drivers
Unlike most geological and hydro-meteorological hazards, wildfires are primarily influenced by human actions and, to a degree, can be predicted, managed and prevented. Damaging wildfires are often symptomatic of past and present policy, planning and governance choices that have enabled ignition and fire spread across landscapes (Robinne et al., 2018).
Climate change influences wildfire behaviour through changes in weather, which affect vegetation growth and drying (rainfall, temperature, evapotranspiration). By the end of the century, the probability of extreme wildfire events is projected to increase by 31-57% (UNEP, 2022).
Vegetation stressed or killed by pests and disease may increase fuel load and ignition susceptibility. Conversely, wildfires can create vegetation stress that increases vulnerability to pest and disease outbreaks.
Fire is a natural ecological process, but changes to land use are contributing to wildfires. A significant number and area burned by human-caused fires are linked to land-use conversion and agricultural activities. Wildfires are a product of these processes and are partly a function of socio-economic decisions. Reducing the risks of wildfires requires policies and incentives that promote integrated fire management approaches. This includes land and fire management that is well designed, with a balanced combination of policies, a clear legal framework, and incentives that encourage appropriate land and fire use while meeting social, economic, health, and ecosystem needs.
Wildfire occurrence, characteristics, and impacts are closely associated with other hazards. Droughts, heatwaves, and high winds can intensify wildfire severity, size, and duration, complicating control efforts.
Impacts
Human health can be severely affected by wildfires. Certain populations are particularly vulnerable. Biomass smoke contains high levels of particulate matter and toxins. Respiratory morbidity predominates, and epidemiological studies have reported significant associations between wildfire smoke exposure and respiratory morbidity and mortality. Cardiovascular, ophthalmic, and psychiatric problems can also result (Fann et al., 2018), with links to both acute and chronic mental health conditions (Kibble et al., 2023). In addition, severe burns resulting from direct contact with the fire require care in specialised units and carry a risk of multi-organ complications. Access to affected areas and communication with populations living within them is crucial in mitigating risk (Finlay et al., 2012).
Infrastructure and services, including power, water, communication lines, roads, and railways, are often damaged by wildfires. In addition to firefighting costs, there can be very large financial costs associated with rebuilding homes, businesses, and entire communities that have been damaged or destroyed by a major fire event, as well as broader economic impacts.
The effects of wildfires on vegetation cover and soil stability may create secondary hazards or subsidiary perils, such as post-fire landslides, mudslides, flash floods, erosion, and siltation (triggered by post-fire rainfall on fire-disturbed surfaces) (Kibble et al., 2023).
Fires burning on terrain contaminated by radioactivity may lead to uncontrolled redistribution of radioactive particles. Wildfires burning into residential and industrial areas and waste deposits may generate toxic pollutants. Fires burning on terrain containing unexploded ordnance and landmines could result in injuries and fatalities (Finlay et al., 2012).
Multi-hazard context
The figure below summarises common interactions between wildfires and other hazards. This information should be used with caution and not be solely relied upon in Disaster Risk Management, particularly as some interactions may not have been included. Note that hazardous events occurring together or locally in space or time may not necessarily cause, amplify, or be otherwise related to each other. Specific examples of multi-hazard context can be found in the ‘Hazard drivers’ and ‘Impacts’ sections above.
Multi-hazard diagram
Risk Management
Integrated fire management is key to adapting to current and future changes in global wildfire risk. It consists of five interlinked and often overlapping phases: review and analysis, risk reduction, readiness, response, and recovery (the 5Rs), which are applied and promoted by FAO and the World Bank in their approaches and project design. Notably, residual risks will remain, and planning for impacts and recovery is required for wildfires.
Communities must be engaged meaningfully in planning, mitigating, and reducing the hazard on their landscape to reduce wildfire risk. This requires a shift in the social approach to living with fire and being prepared. There is growing recognition of the important role that Indigenous Peoples and local knowledge holders can play in informing land management practices that assist in the prevention and mitigation of wildfires. Importantly, this must include engagement to support and integrate Indigenous, traditional, and contemporary fire management practices into policy.
An important element of integrated fire management is rebalancing investments from readiness and response towards proactive wildfire mitigation and management. Wildfire risk reduction activities represent a sound investment as they reduce the potential impacts of wildfires and, in the long term, are more cost-effective than response, recovery, and restoration following extreme events.
Almost all disastrous wildfire events are associated with anomalous meteorological or climatic conditions (Bowman et al., 2017). To mitigate or prevent wildfire disasters, fire managers require early warning of extreme fire danger conditions. This allows time to implement fire prevention, detection, and pre-suppression preparedness action plans before disaster wildfires occur. Fire Danger Rating Systems are the cornerstone of fire management decision-making and are used with forecasted meteorological data to provide early warning of wildfire potential (de Groot et al., 2014).
Monitoring
The section and the table below offer an overview of monitoring wildfires. This information can be used for forecasting within a national early warning system (EWS). Since EWS capacities and processes differ across countries, the most current and specific information regarding EWS should be obtained from the appropriate national or regional agency/authority responsible for disaster management.
| Which institution(s) produce(s) disaster risk data/information? | Weather service agencies, fire authorities, NASA FIRMS |
| How is the hazard observed/monitored/forecast? | Monitoring the weather conditions such as drought and heatwaves Monitoring the soil humidity and the vegetation conditions Surveillance of areas prone to wildfires Active fire detections: different data sources are useful in different ways for identification and response to the hazard, e.g. precision of polar-orbiting detection vs. higher frequency geostationary detection See: https://doi.org/10.1016/j.rse.2021.112694 Global active fire data: https://firms.modaps.eosdis.nasa.gov/map/ |
References
ASEAN, 2002. ASEAN Agreement on Transboundary Haze Pollution. Association of South East Asian Nations (ASEAN). Accessed 21 January 2025.
Bowman, D.M.J.S., Williamson, G.J., Abatzoglou, J.T., Kolden, C.A., Cochrane, M.A., Smith, A.M.S., 2017. Human exposure and sensitivity to globally extreme wildfire events. Nat. Ecol. Evol., 1: 0058. Human exposure and sensitivity to globally extreme wildfire events Accessed 21 January 2025.
de Groot, W.J., Flannigan, M.D., 2014. Climate change and early warning systems for wildland fire. Pages 127–151 in Reducing Disaster: Early Warning Systems for Climate Change (Z. Zommers and A. Singh, eds.) Springer, New York.
Fann, N., Alman, B., Broome, R.A., Morgan, G.G., Johnston, F.H., Pouliot, G., et al., 2018. 'The health impacts and economic value of wildland fire episodes in the US, 2008 to 2012' Science of The Total Environment: volume 610 to 611, pages 802 to 809. The health impacts and economic value of wildland fire episodes in the U.S.: 2008–2012. Accessed 21 January 2025.
FAO, 2020. FAOSTAT: Burning-Biomass. Food and Agriculture Organisation of the United Nations (FAO). Accessed 21 January 2025.
Finlay, S.E., Moffat, A., Gazzard, R., Baker, D., and Murray, V., 2012. Health Impacts of Wildfires. PLOS Currents Disasters. Edition 1. doi: 10.1371/4f959951cce2c. Accessed 21 January 2025.
GFMC, no date. Natural Hazards: Landscape Fires. BeSafetNet: EUR-OPA Major Hazards Agreements. Global Fire Monitoring Center (GFMC). Accessed 21 January 2025
GFMC, 2013. Vegetation Fires and Global Change. Challenges for Concerted International Action – A White Paper directed to the United Nations and International Organizations. Global Fire Monitoring Center (GFMC). Accessed 21 January 2025.
GWIS, 2019. Welcome to GWIS. Global Wildfire Information System (GWIS). GWIS - Welcome to GWIS. Accessed 21 January 2025.
Kibble, A., Callow, H., Harold, P., Sing, M., Cheek, E., and Harrison, H., 2023. Health Effects of Climate Change (HECC) in the UK: 2023 report; Chapter 10. Wildfires and health; UK Health Security Agency (UKHSA). Accessed 21 January 2025.
Robinne, F.-N., Burns, J., Kant, P., de Groot, B., et al., 2018. Global Fire Challenges in a Warming World. International Union of Forest Research Organizations (IUFRO). IUFRO Occasional Paper No. 32. Accessed 21 January 2025.
United Nations Environment Programme, 2022. Spreading like Wildfire – The Rising Threat of Extraordinary Landscape Fires. A UNEP Rapid Response Assessment. Nairobi. Accessed 21 January 2025.