A daytime fire engulfing large trees

A wildfire in California, USA on 5 September 2008

A wildfire is any uncontrolled fire in combustible vegetation that occurs in the countryside or a wilderness area.[1][2] Other names such as brush fire, bushfire, forest fire, grass fire, hill fire, peat fire, vegetation fire, veldfire and wildland fire may be used to describe the same phenomenon depending on the type of vegetation being burned. A wildfire differs from other fires by its extensive size, the speed at which it can spread out from its original source, its potential to change direction unexpectedly, and its ability to jump gaps such as roads, rivers and fire breaks.[3] Wildfires are characterized in terms of the cause of ignition, their physical properties such as speed of propagation, the combustible material present, and the effect of weather on the fire.[4]

Wildfires occur on every continent except Antarctica. Fossil records and human history contain accounts of wildfires, as wildfires can occur in periodic intervals.[5][6] Wildfires can cause extensive damage, both to property and human life, but they also have various beneficial effects on wilderness areas. Some plant species depend on the effects of fire for growth and reproduction,[5] although large wildfires may also have negative ecological effects.[4]

Strategies of wildfire prevention, detection, and suppression have varied over the years, and international wildfire management experts encourage further development of technology and research.[7] One of the more controversial techniques is controlled burning: permitting or even igniting smaller fires to minimize the amount of flammable material available for a potential wildfire.[8][9] While some wildfires burn in remote forested regions, they can cause extensive destruction of homes and other property located in the wildland-urban interface: a zone of transition between developed areas and undeveloped wilderness.[8][10]


An artificially colored satellite view of Africa, with red and yellow markers where fires have been detected. A wide red band of markers runs east-west, just south of the Sahara Desert.

The distribution of wildfires on the African continent during the year 2002.

The name wildfire was once a synonym for Greek fire but now refers to any large or destructive conflagration.[2] Wildfires differ from other fires in that they take place outdoors in areas of grassland, woodlands, bushland, scrubland, peatland, and other wooded areas that act as a source of fuel, or combustible material. Buildings may become involved if a wildfire spreads to adjacent communities. While the causes of wildfires vary and the outcomes are always unique, all wildfires can be characterized in terms of their physical properties, their fuel type, and the effect that weather has on the fire.

Wildfire behavior and severity result from the combination of factors such as available fuels, physical setting, and weather.[11][12][13] While wildfires can be large, uncontrolled disasters that burn through Template:Convert or more, they can also be as small as Template:Convert or less.[14][15][16] Although smaller events may be included in wildfire modeling, most do not earn press attention. This can be problematic because public fire policies, which relate to fires of all sizes, are influenced more by the way the media portrays catastrophic wildfires than by small fires.[17][18][19]


The four major natural causes of wildfire ignitions are lightning, volcanic eruption, sparks from rockfalls, and spontaneous combustion.[20][21] The thousands of coal seam fires that are burning around the world, such as those in Centralia, Burning Mountain, and several coal-sustained fires in China, can also flare up and ignite nearby flammable material.[22] However, many wildfires are attributed to human sources such as arson, discarded cigarettes, sparks from equipment, and power line arcs (as detected by arc mapping).[23][24] In societies experiencing shifting cultivation where land is cleared quickly and farmed until the soil loses fertility, slash and burn clearing is often considered the least expensive way to prepare land for future use.[25][26] Forested areas cleared by logging encourage the dominance of flammable grasses, and abandoned logging roads overgrown by vegetation may act as fire corridors. Annual grassland fires in Southern Vietnam can be attributed in part to the destruction of forested areas by herbicides, explosives, and mechanical land clearing and burning operations during the Vietnam War.[27]

The most common cause of wildfires varies throughout the world. In the United States, Canada, and Northwest China, for example, lightning is the major source of ignition. In other parts of the world, human involvement is a major contributor. In Mexico, Central America, South America, Africa, Southeast Asia, Fiji, and New Zealand, wildfires can be attributed to human activities such as animal husbandry, agriculture, and land-conversion burning. Human carelessness is a major cause of wildfires in China and in the Mediterranean Basin. In Australia, the source of wildfires can be traced to both lightning strikes and human activities such as machinery sparks and cast-away cigarette butts."[6]

Fuel typeModifica

Flat expanse of brown grasses and some green trees with black and some gray smoke and visible flames in the distance.

A surface fire in the western desert of Utah, U.S.

Mountainous region with blackened soil and trees due to a recent fire.

Charred landscape following a crown fire in the North Cascades, U.S.

The spread of wildfires varies based on the flammable material present and its vertical arrangement.[28] For example, fuels uphill from a fire are more readily dried and warmed by the fire than those downhill, yet burning logs can roll downhill from the fire to ignite other fuels. Fuel arrangement and density is governed in part by topography, as land shape determines factors such as available sunlight and water for plant growth. Overall, fire types can be generally characterized by their fuels as follows:[note 1]

  • Ground fires are fed by subterranean roots, duff and other buried organic matter. This fuel type is especially susceptible to ignition due to spotting. Ground fires typically burn by smoldering, and can burn slowly for days to months, such as peat fires in Kalimantan and Eastern Sumatra, Indonesia, which resulted from a riceland creation project that unintentionally drained and dried the peat.[29][30]
  • Crawling or surface fires are fueled by low-lying vegetation such as leaf and timber litter, debris, grass, and low-lying shrubbery.[31]
  • Ladder fires consume material between low-level vegetation and tree canopies, such as small trees, downed logs, and vines. Kudzu, Old World climbing fern, and other invasive plants that scale trees may also encourage ladder fires.[32]
  • Crown, canopy, or aerial fires burn suspended material at the canopy level, such as tall trees, vines, and mosses. The ignition of a crown fire, termed crowning, is dependent on the density of the suspended material, canopy height, canopy continuity, and sufficient surface and ladder fires in order to reach the tree crowns.[33] For example, ground-clearing fires lit by humans can spread into the Amazon rain forest, damaging ecosystems not particularly suited for heat or arid conditions.[34]

Physical propertiesModifica

Wildfires occur when all of the necessary elements of a fire triangle come together in a wooded area: an ignition source is brought into contact with a combustible material such as vegetation, that is subjected to sufficient heat and has an adequate supply of oxygen from the ambient air. A high moisture content usually prevents ignition and slows propagation, because higher temperatures are required to evaporate any water within the material and heat the material to its fire point.[3][13] Dense forests usually provide more shade, resulting in lower ambient temperatures and greater humidity, and are therefore less susceptible to wildfires.[35] Less dense material such as grasses and leaves are easier to ignite because they contain less water than denser material such as branches and trunks.[36] Plants continuously lose water by evapotranspiration, but water loss is usually balanced by water absorbed from the soil, humidity, or rain.[37] When this balance is not maintained, plants dry out and are therefore more flammable, often a consequence of droughts.[38][39]

A line of trees completely engulfed in flames. Towers with instrumentation are seen just beyond the fire's reach.

Experimental fire in Canada

A wildfire front is the portion sustaining continuous flaming combustion, where unburned material meets active flames, or the smoldering transition between unburned and burned material.[40] As the front approaches, the fire heats both the surrounding air and woody material through convection and thermal radiation. First, wood is dried as water is vaporized at a temperature of Template:Convert. Next, the pyrolysis of wood at Template:Convert releases flammable gases. Finally, wood can smolder at Template:Convert or, when heated sufficiently, ignite at Template:Convert.[41][42] Even before the flames of a wildfire arrive at a particular location, heat transfer from the wildfire front warms the air to Template:Convert, which pre-heats and dries flammable materials, causing materials to ignite faster and allowing the fire to spread faster.[36][43] High-temperature and long-duration surface wildfires may encourage flashover or torching: the drying of tree canopies and their subsequent ignition from below.[44]

Wildfires have a rapid forward rate of spread (FROS) when burning through dense, uninterrupted fuels.[45] They can move as fast as Template:Convert in forests and Template:Convert in grasslands.[46] Wildfires can advance tangential to the main front to form a flanking front, or burn in the opposite direction of the main front by backing.[47] They may also spread by jumping or spotting as winds and vertical convection columns carry firebrands (hot wood embers) and other burning materials through the air over roads, rivers, and other barriers that may otherwise act as firebreaks.[48][49] Torching and fires in tree canopies encourage spotting, and dry ground fuels that surround a wildfire are especially vulnerable to ignition from firebrands.[50] Spotting can create spot fires as hot embers and firebrands ignite fuels downwind from the fire. In Australian bushfires, spot fires are known to occur as far as Template:Convert from the fire front.[51]

Especially large wildfires may affect air currents in their immediate vicinities by the stack effect: air rises as it is heated, and large wildfires create powerful updrafts that will draw in new, cooler air from surrounding areas in thermal columns.[52] Great vertical differences in temperature and humidity encourage pyrocumulus clouds, strong winds, and fire whirls with the force of tornadoes at speeds of more than Template:Convert.[53][54][55] Rapid rates of spread, prolific crowning or spotting, the presence of fire whirls, and strong convection columns signify extreme conditions.[56]

Effect of weatherModifica

Heat waves, droughts, cyclical climate changes such as El Niño, and regional weather patterns such as high-pressure ridges can increase the risk and alter the behavior of wildfires dramatically.[57][58] Years of precipitation followed by warm periods can encourage more widespread fires and longer fire seasons.[59] Since the mid 1980s, earlier snowmelt and associated warming has also been associated with an increase in length and severity of the wildfire season in the Western United States.[60] However, one individual element does not always cause an increase in wildfire activity. For example, wildfires will not occur during a drought unless accompanied by other factors, such as lightning (ignition source) and strong winds (mechanism for rapid spread).[61]

Fire intensity also increases during daytime hours. Burn rates of smoldering logs are up to five times greater during the day due to lower humidity, increased temperatures, and increased wind speeds.[62] Sunlight warms the ground during the day which creates air currents that travel uphill. At night the land cools, creating air currents that travel downhill. Wildfires are fanned by these winds and often follow the air currents over hills and through valleys.[63] Fires in Europe occur frequently during the hours of 12:00 p.m. and 2:00 p.m.[64] Wildfire suppression operations in the United States revolve around a 24-hour fire day that begins at 10:00 a.m. due to the predictable increase in intensity resulting from the daytime warmth.[65]


Two illustrations of the earth, one above the other.  The seas are dark gray in color and the continents a lighter gray. Both images have red, yellow, and white markers indicating where fires occurred during the months of August (top image) and February (bottom image) of the year 2008.

Global fires during the year 2008 for the months of August (top image) and February (bottom image), as detected by the Moderate Resolution Imaging Spectroradiometer (MODIS) on NASA's Terra satellite.

Wildfires are common in climates that are sufficiently moist to allow the growth of vegetation but feature extended dry, hot periods.[5] Such places include the vegetated areas of Australia and Southeast Asia, the veld in southern Africa, the fynbos in the Western Cape of South Africa, the forested areas of the United States and Canada, and the Mediterranean Basin. Fires can be particularly intense during days of strong winds, periods of drought, and during warm summer months.[66][67] Global warming may increase the intensity and frequency of droughts in many areas, creating more intense and frequent wildfires.[4][68][69]

Although some ecosystems rely on naturally occurring fires to regulate growth, many ecosystems suffer from too much fire, such as the chaparral in southern California and lower elevation deserts in the American Southwest. The increased fire frequency in these ordinarily fire-dependent areas has upset natural cycles, destroyed native plant communities, and encouraged the growth of fire-intolerant vegetation and non-native weeds.[70][71][72][73] Invasive species, such as Lygodium microphyllum and Bromus tectorum, can grow rapidly in areas that were damaged by fires. Because they are highly flammable, they can increase the future risk of fire, creating a positive feedback loop that increases fire frequency and further destroys native growth.[32][74]

In the Amazon Rainforest, drought, logging, cattle ranching practices, and slash-and-burn agriculture damage fire-resistant forests and promote the growth of flammable brush, creating a cycle that encourages more burning.[75] Fires in the rainforest threaten its collection of diverse species and produce large amounts of CO2.[76] Also, fires in the rainforest, along with drought and human involvement, could damage or destroy more than half of the Amazon rainforest by the year 2030.[77] Wildfires generate ash, destroy available organic nutrients, and cause an increase in water runoff, eroding away other nutrients and creating flash flood conditions.[28][78] A 2003 wildfire in the North Yorkshire Moors destroyed Template:Convert of heather and the underlying peat layers. Afterwards, wind erosion stripped the ash and the exposed soil, revealing archaeological remains dating back to 10,000 BC.[79] Wildfires can also have an effect on climate change, increasing the amount of carbon released into the atmosphere and inhibiting vegetation growth, which affects overall carbon uptake by plants.[80]

Plant adaptationModifica

Two photographs of the same section of a pine forest; both show blackened bark at least halfway up the trees. The first picture is noticeably lacking in surface vegetation, while the second shows small, green grasses on the forest floor.

Ecological succession after a wildfire in a boreal pine forest next to Hara Bog, Lahemaa National Park, Estonia. The pictures were taken one and two years after the fire.

Plants in wildfire-prone ecosystems often survive through adaptations to their local fire regime. Such adaptations include physical protection against heat, increased growth after a fire event, and flammable materials that encourage fire and may eliminate competition. For example, plants of the genus Eucalyptus contain flammable oils that encourage fire and hard sclerophyll leaves to resist heat and drought, ensuring their dominance over less fire-tolerant species.[81][82] Dense bark, shedding lower branches, and high water content in external structures may also protect trees from rising temperatures.[5] Fire-resistant seeds and reserve shoots that sprout after a fire encourage species preservation, as embodied by pioneer species. Smoke, charred wood, and heat can stimulate the germination of seeds in a process called serotiny.[83] Exposure to smoke from burning plants promotes germination in other types of plants by inducing the production of the orange butenolide.[84]

Grasslands in Western Sabah, Malaysian pine forests, and Indonesian Casuarina forests are believed to have resulted from previous periods of fire.[85] Chamise deadwood litter is low in water content and flammable, and the shrub quickly sprouts after a fire.[5] Sequoia rely on periodic fires to reduce competition, release seeds from their cones, and clear the soil and canopy for new growth.[86] Caribbean Pine in Bahamian pineyards have adapted to and rely on low-intensity, surface fires for survival and growth. An optimum fire frequency for growth is every 3 to 10 years. Too frequent fires favor herbaceous plants, and infrequent fires favor species typical of Bahamian dry forests.[87]

Atmospheric effectsModifica

A paved road with trees and grasses on the side with a large, white and dark gray smoke cloud rising in the distance.

A Pyrocumulus cloud produced by a wildfire in Yellowstone National Park

Most of the Earth's weather and air pollution reside in the troposphere, the part of the atmosphere that extends from the surface of the planet to a height of about Template:Convert. The vertical lift of a severe thunderstorm or pyrocumulonimbus can be enhanced in the area of a large wildfire, which can propel smoke, soot, and other particulate matter as high as the lower stratosphere.[88] Previously, prevailing scientific theory held that most particles in the stratosphere came from volcanoes, but smoke and other wildfire emissions have been detected from the lower stratosphere.[89] Pyrocumulus clouds can reach Template:Convert over wildfires.[90] Increased fire byproducts in the stratosphere can increase ozone concentration beyond safe levels.[91] Satellite observation of smoke plumes from wildfires revealed that the plumes could be traced intact for distances exceeding Template:Convert.[92] Computer-aided models such as CALPUFF may help predict the size and direction of wildfire-generated smoke plumes by using atmospheric dispersion modeling.[93]

Wildfires can affect climate and weather and have major impacts on atmospheric pollution.[94] Wildfire emissions contain fine particulate matter which can cause cardiovascular and respiratory problems.[95] Forest fires in Indonesia in 1997 were estimated to have released between 0.81 and 2.57 gigatonnes (0.89 and 2.83 billion short tons) of CO2 into the atmosphere, which is between 13%–40% of the annual carbon dioxide emissions from burning fossil fuels.[96][97] Atmospheric models suggest that these concentrations of sooty particles could increase absorption of incoming solar radiation during winter months by as much as 15%.[98]


In the Welsh Borders, the first evidence of wildfire is rhyniophytoid plant fossils preserved as charcoal, dating to the Silurian period (about Template:Ma). Smoldering surface fires started to occur sometime before the Early Devonian period Template:Ma. Low atmospheric oxygen during the Middle and Late Devonian was accompanied by a decrease in charcoal abundance.[99][100] Additional charcoal evidence suggests that fires continued through the Carboniferous period. Later, the overall increase of atmospheric oxygen from 13% in the Late Devonian to 30-31% by the Late Permian was accompanied by a more widespread distribution of wildfires.[101] Later, a decrease in wildfire-related charcoal deposits from the late Permian to the Triassic periods is explained by a decrease in oxygen levels.[102]

Wildfires during the Paleozoic and Mesozoic periods followed patterns similar to fires that occur in modern times. Surface fires driven by dry seasons are evident in Devonian and Carboniferous progymnosperm forests. Lepidodendron forests dating to the Carboniferous period have charred peaks, evidence of crown fires. In Jurassic gymnosperm forests, there is evidence of high frequency, light surface fires.[102] The increase of fire activity in the late Tertiary[103] is possibly due to the increase of C4-type grasses. As these grasses shifted to more mesic habitats, their high flammability increased fire frequency, promoting grasslands over woodlands.[104] However, fire-prone habitats may have contributed to the prominence of trees such as those of the genus Pinus, which have thick bark to withstand fires and employ serotiny.[105]

Human involvementModifica

The human use of fire for agricultural and hunting purposes during the Paleolithic and Mesolithic ages altered the preexisting landscapes and fire regimes. Woodlands were gradually replaced by smaller vegetation that facilitated travel, hunting, seed-gathering and planting.[106] In recorded human history, minor allusions to wildfires were mentioned in the Bible and by classical writers such as Homer. However, while ancient Hebrew, Greek, and Roman writers were aware of fires, they were not very interested in the uncultivated lands where wildfires occurred.[107][108] Wildfires were used in battles throughout human history as early thermal weapons. From the Middle ages, accounts were written of occupational burning as well as customs and laws that governed the use of fire. In Germany, regular burning was documented in 1290 in the Odenwald and in 1344 in the Black Forest.[109] In the 14th century Sardinia, firebreaks were used for wildfire protection. In Spain during the 1550s, sheep husbandry was discouraged in certain provinces by Philip II due to the harmful effects of fires used in transhumance.[107][108] As early as the 17th century, Native Americans were observed using fire for many purposes including cultivation, signaling, and warfare. Scottish botanist David Douglas noted the native use of fire for tobacco cultivation, to encourage deer into smaller areas for hunting purposes, and to improve foraging for honey and grasshoppers. Charcoal found in sedimentary deposits off the Pacific coast of Central America suggests that more burning occurred in the 50 years before the Spanish colonization of the Americas than after the colonization.[110] In the post-World War II Baltic region, socio-economic changes led more stringent air quality standards and bans on fires that eliminated traditional burning practices.[109]

Wildfires typically occurred during periods of increased temperature and drought. An increase in fire-related debris flow in alluvial fans of northeastern Yellowstone National Park was linked to the period between AD 1050 and 1200, coinciding with the Medieval Warm Period.[111] However, human influence caused an increase in fire frequency. Dendrochronological fire scar data and charcoal layer data in Finland suggests that, while many fires occurred during severe drought conditions, an increase in the number of fires during 850 BC and 1660 AD can be attributed to human influence.[112] Charcoal evidence from the Americas suggested a general decrease in wildfires between 1 AD and 1750 compared to previous years. However, a period of increased fire frequency between 1750 and 1870 was suggested by charcoal data from North America and Asia, attributed to human population growth and influences such as land clearing practices. This period was followed by an overall decrease in burning in the 20th century, linked to the expansion of agriculture, increased livestock grazing, and fire prevention efforts.[113]



1985 Smokey Bear poster with part of his admonition, "Only you can prevent forest fires".

Wildfire prevention refers to the preemptive methods of reducing the risk of fires as well as lessening its severity and spread.[114] Effective prevention techniques allow supervising agencies to manage air quality, maintain ecological balances, protect resources,[74] and to limit the effects of future uncontrolled fires.[115] North American firefighting policies may permit naturally caused fires to burn to maintain their ecological role, so long as the risks of escape into high-value areas are mitigated.[116] However, prevention policies must consider the role that humans play in wildfires, since, for example, 95% of forest fires in Europe are related to human involvement.[117] Sources of human-caused fire may include arson, accidental ignition, or the uncontrolled use of fire in land-clearing and agriculture such as the slash-and-burn farming in Southeast Asia.[118]

In the mid-19th century, explorers from the HMS Beagle observed Australian Aborigines using fire for ground clearing, hunting, and regeneration of plant food in a method later named fire-stick farming.[119] Such careful use of fire has been employed for centuries in the lands protected by Kakadu National Park to encourage biodiversity.[120] In 1937, U.S. President Franklin D. Roosevelt initiated a nationwide fire prevention campaign, highlighting the role of human carelessness in forest fires. Later posters of the program featured Uncle Sam, leaders of the Axis powers of World War II, characters from the Disney movie Bambi, and the official mascot of the U.S. Forest Service, Smokey Bear.[121]

A small fire on the slope of a hill. The hill features small, green shubbery and some trees. A person in light-colored clothing in seen in the background, some distance from the flames.

A prescribed burn in a Pinus nigra stand in Portugal

Wildfires are caused by a combination of natural factors such as topography, fuels, and weather. Other than reducing human infractions, only fuels may be altered to affect future fire risk and behavior.[28] Wildfire prevention programs around the world may employ techniques such as wildland fire use and prescribed or controlled burns.[1][122][123] Wildland fire use refers to any fire of natural causes that is monitored but allowed to burn. Controlled burns are fires ignited by government agencies under less dangerous weather conditions.[124]

Vegetation may be burned periodically to maintain high species diversity, and frequent burning of surface fuels limits fuel accumulation, thereby reducing the risk of crown fires.[125][126] Using strategic cuts of trees, fuels may also be removed by handcrews in order to clean and clear the forest, prevent fuel build-up, and create access into forested areas.[127] Chain saws and large equipment can be used to thin out ladder fuels and shred trees and vegetation to a mulch.[128] Multiple fuel treatments are often needed to influence future fire risks, and wildfire models may be used to predict and compare the benefits of different fuel treatments on future wildfire spread.[28]

However, controlled burns are reportedly "the most effective treatment for reducing a fire’s rate of spread, fireline intensity, flame length, and heat per unit of area" according to Jan Van Wagtendonk, a biologist at the Yellowstone Field Station.[129] Additionally, while fuel treatments are typically limited to smaller areas, effective fire management requires the administration of fuels across large landscapes in order to reduce future fire size and severity.[130]

Building codes in fire-prone areas typically require that structures be built of flame-resistant materials and a defensible space be maintained by clearing flammable materials within a prescribed distance from the structure.[131][132] Communities in the Philippines also maintain fire lines Template:Convert wide between the forest and their village, and patrol these lines during summer months or seasons of dry weather.[133] Fuel buildup can result in costly, devastating fires as new homes, ranches, and other development are built adjacent to wilderness areas. Continued growth in fire-prone areas and rebuilding structures destroyed by fires has been met with criticism.[134]

However, the population growth along the wildland-urban interface discourages the use of current fuel management techniques. Smoke is an irritant and attempts to thin out the fuel load is met with opposition due to desirability of forested areas, in addition to other wilderness goals such as endangered species protection and habitat preservation.[135] The ecological benefits of fire are often overridden by the economic and safety benefits of protecting structures and human life.[136] For example, while fuel treatments decrease the risk of crown fires, these techniques destroy the habitats of various plant and animal species.[137] Additionally, government policies that cover the wilderness usually differ from local and state policies that govern urban lands.[74][138]


A four-legged tower with a small enclosure at the top, next to two one-story buildings. The tower is four stories tall. Trees are at either side, and in the foreground there are rocks, some vegetation, and a rough trail.

Dry Mountain Fire Lookout in the Ochoco National Forest, Oregon, circa 1930

Fast and effective detection is a key factor in wildfire fighting.[139] Early detection efforts were focused on early response, accurate results in both daytime and nighttime, and the ability to prioritize fire danger.[140] Fire lookout towers were used in the United States in the early 20th century and fires were reported using telephones, carrier pigeons, and heliographs.[141] Aerial and land photography using instant cameras were used in the 1950s until infrared scanning was developed for fire detection in the 1960s. However, information analysis and delivery was often delayed by limitations in communication technology. Early satellite-derived fire analyses were hand-drawn on maps at a remote site and sent via overnight mail to the fire manager. During the Yellowstone fires of 1988, a data station was established in West Yellowstone, permitting the delivery of satellite-based fire information in approximately four hours.[140]

Currently, public hotlines, fire lookouts in towers, and ground and aerial patrols can be used as a means of early detection of forest fires. However, accurate human observation may be limited by operator fatigue, time of day, time of year, and geographic location. Electronic systems have gained popularity in recent years as a possible resolution to human operator error. These systems may be semi- or fully-automated and employ systems based on the risk area and degree of human presence, as suggested by GIS data analyses. An integrated approach of multiple systems can be used to merge satellite data, aerial imagery, and personnel position via Global Positioning System (GPS) into a collective whole for near-realtime use by wireless Incident Command Centers.[142][143]

A small, high risk area that features thick vegetation, a strong human presence, or is close to a critical urban area can be monitored using a local sensor network. Detection systems may include wireless sensor networks that act as automated weather systems: detecting temperature, humidity, and smoke.[144][145][146][147] These may be battery-powered, solar-powered, or tree-rechargeable: able to recharge their battery systems using the small electrical currents in plant material.[148] Larger, medium-risk areas can be monitored by scanning towers that incorporate fixed cameras and sensors to detect smoke or additional factors such as the infrared signature of carbon dioxide produced by fires. Additional capabilities such as night vision, brightness detection, and color change detection may also be incorporated into sensor arrays.[149][150][151]

A satellite view of the Balkans and Greece. Clouds and smoke trails are seen above the Balkans and trailing south into the Ionian Sea.

Wildfires across the Balkans in late July 2007 (MODIS image)

Satellite and aerial monitoring can provide a wider view and may be sufficient to monitor very large, low risk areas. These more sophisticated systems employ GPS and aircraft-mounted infrared or high-resolution visible cameras to identify and target wildfires.[152][153] Satellite-mounted sensors such as Envisat's Advanced Along Track Scanning Radiometer and European Remote-Sensing Satellite's Along-Track Scanning Radiometer can measure infrared radiation emitted by fires, identifying hot spots greater than Template:Convert.[154][155] The National Oceanic and Atmospheric Administration's Hazard Mapping System combines remote-sensing data from satellite sources such as Geostationary Operational Environmental Satellite (GOES), Moderate-Resolution Imaging Spectroradiometer (MODIS), and Advanced Very High Resolution Radiometer (AVHRR) for detection of fire and smoke plume locations.[156][157] However, satellite detection is prone to offset errors, anywhere from Template:Convert for MODIS and AVHRR data and up to Template:Convert for GOES data.[158] Satellites in geostationary orbits may become disabled, and satellites in polar orbits are often limited by their short window of observation time. Cloud cover and image resolution and may also limit the effectiveness of satellite imagery.[159]


A three-engine red-and-white cargo plane in-flight, releasing a large quantity of water from its undercarriage storage tanks. The water trails behind the aircraft in a continuous, fan-shaped drop pattern.

Tanker 910 during a drop demonstration in December, 2006

Wildfire suppression depends on the technologies available in the area in which the wildfire occurs. In less developed nations such as Thailand, the techniques used can be as simple as throwing sand or beating the fire with sticks or palm fronds.[160] In more advanced nations, the suppression methods vary due to increased technological capacity. Silver iodide can be used to encourage snow fall,[161] while fire retardants and water can be dropped onto fires by unmanned aerial vehicles, planes, and helicopters.[162][163] Complete fire suppression is no longer an expectation, but the majority of wildfires are often extinguished before they grow out of control. While more than 99% of the 10,000 new wildfires each year are contained, escaped wildfires can cause extensive damage. Worldwide damage from wildfires is in the billions of euros annually.[164] Wildfires in Canada and the US burn an average of Template:Convert per year.[165][166]

Above all, fighting wildfires can become deadly. A wildfire's burning front may also change direction unexpectedly and jump across fire breaks. Intense heat and smoke can lead to disorientation and loss of appreciation of the direction of the fire, which can make fires particularly dangerous. For example, during the 1949 Mann Gulch fire in Montana, USA, thirteen smokejumpers died when they lost their communication links, became disorientated, and were overtaken by the fire.[167] In the Australian February 2009 Victorian bushfires, at least 173 people died and over 2,029 homes and 3,500 structures were lost when they became engulfed by wildfire.[168]


A dark region shaped like a shield with a pointed bottom. An arrow and the text "propagation axis (wind)" indicates a bottom-to-top direction up the body of the shield shape. The shape's pointed bottom is labeled "fire start". Around the shield shape's top and thinning towards its sides, a yellow-orange region is labeled "left front", "right front", and (at the top) "head of the fire".

Fire Propagation Model

Wildfire modeling is concerned with numerical simulation of wildfires in order to comprehend and predict fire behavior.[169][170] Wildfire modeling can ultimately aid wildfire suppression, increase the safety of firefighters and the public, and minimize damage. Using computational science, wildfire modeling involves the statistical analysis of past fire events to predict spotting risks and front behavior. Various wildfire propagation models have been proposed in the past, including simple ellipses and egg- and fan-shaped models. Early attempts to determine wildfire behavior assumed terrain and vegetation uniformity. However, the exact behavior of a wildfire's front is dependent on a variety of factors, including windspeed and slope steepness. Modern growth models utilize a combination of past ellipsoidal descriptions and Huygens' Principle to simulate fire growth as a continuously expanding polygon.[171][172] Extreme value theory may also be used to predict the size of large wildfires. However, large fires that exceed suppression capabilities are often regarded as statistical outliers in standard analyses, even though fire policies are more influenced by catastrophic wildfires than by small fires.[17]

See alsoModifica


  1. This section is a composite of several references. Refer to:


  1. 1,0 1,1 Federal Fire and Aviation Operations Action Plan, 4.
  2. 2,0 2,1 Template:Vancite book
  3. 3,0 3,1 Template:Vancite web
  4. 4,0 4,1 4,2 Template:Vancite journal
  5. 5,0 5,1 5,2 5,3 5,4 Template:Vancite web
  6. 6,0 6,1 Template:Vancite web
  7. Template:Vancite web
  8. 8,0 8,1 Interagency Strategy for the Implementation of the Federal Wildland Fire Policy, entire text
  9. National Wildfire Coordinating Group Communicator's Guide For Wildland Fire Management, entire text
  10. Template:Vancite web
  11. Graham, et al., 12, 36
  12. National Wildfire Coordinating Group Communicator's Guide For Wildland Fire Management, 4-6.
  13. 13,0 13,1 Template:Vancite web
  14. Template:Vancite web
  15. Template:Vancite web
  16. Glossary of Wildland Fire Terminology, 156
  17. 17,0 17,1 Alvarado, et al., 66-68
  18. Template:Vancite web
  19. Olson, et al., 2-3
  20. Template:Vancite web
  21. Template:Vancite journal
  22. Template:Vancite journal
  23. Template:Vancite book
  24. Template:Vancite web
  25. Template:Vancite web
  26. Karki, 7.
  27. Karki, 4.
  28. 28,0 28,1 28,2 28,3 Graham, et al., iv.
  29. Graham, et al., 9, 13
  30. Template:Vancite web
  31. Graham, et al ., iv, 10, 14
  32. 32,0 32,1 Template:Vancite web
  33. Graham, et al., iv, 8, 11, 15.
  34. Template:Vancite web
  35. Graham, et al., 12.
  36. 36,0 36,1 National Wildfire Coordinating Group Communicator's Guide For Wildland Fire Management, 3.
  37. Template:Vancite web
  38. Template:Vancite web
  39. Template:Vancite web
  40. Glossary of Wildland Fire Terminology, 74.
  41. de Sousa Costa and Sandberg, 229-230.
  42. Template:Vancite web
  43. Template:Vancite web
  44. Graham, et al., 10-11.
  45. Template:Vancite web
  46. Billing, 5-6
  47. Graham, et al., 12
  48. Template:Vancite web
  49. Graham, et al., 16.
  50. Graham, et al., 9, 16.
  51. Billing, 5
  52. National Wildfire Coordinating Group Communicator's Guide For Wildland Fire Management, 4.
  53. Graham, et al., 16-17.
  54. Olson, et al., 2
  55. Template:Vancite web
  56. Glossary of Wildland Fire Terminology, 69.
  57. Template:Vancite web
  58. McKenzie, et. al., 893
  59. Graham, et al., 2
  60. Template:Vancite journal
  61. McKenzie, et. al., 894
  62. de Souza Costa and Sandberg, 228
  63. National Wildfire Coordinating Group Communicator's Guide For Wildland Fire Management, 5.
  64. San-Miguel-Ayanz, et al., 364.
  65. Glossary of Wildland Fire Terminology, 73.
  66. Template:Vancite web
  67. Template:Vancite web
  68. Template:Vancite web
  69. Interagency Strategy for the Implementation of the Federal Wildland Fire Policy, 3, 37.
  70. Graham, et al., 3.
  71. Template:Vancite journal
  72. Template:Vancite conference
  73. 74,0 74,1 74,2 van Wagtendonk (2007), 14.
  74. Nepstad, 4, 8-11
  75. Template:Vancite web
  76. Nepstad, 4
  77. Template:Vancite web
  78. Template:Vancite journal
  79. Template:Vancite journal
  80. Template:Vancite web
  81. Fire. The Australian Experience, 5.
  82. Template:Vancite journal
  83. Template:Vancite journal
  84. Karki, 3.
  85. Template:Vancite web
  86. Template:Vancite web
  87. Template:Vancite web
  88. Template:Vancite conference
  89. Graham, et al., 17
  90. Template:Vancite web
  91. Template:Vancite web
  92. Template:Vancite web
  93. Template:Vancite journal
  94. Template:Vancite web
  95. Template:Vancite journal
  96. Template:Vancite web
  97. Template:Vancite conference
  98. Template:Cite doi
  99. Template:Cite jstor
  100. Template:Cite pmc
  101. 102,0 102,1 Pausas and Keeley, 594
  102. Historically, the Cenozoic has been divided up into the Quaternary and Tertiary sub-eras, as well as the Neogene and Paleogene periods. The 2009 version of the ICS time chart recognizes a slightly extended Quaternary as well as the Paleogene and a truncated Neogene, the Tertiary having been demoted to informal status (Taken from Template:Tl).
  103. Pausas and Keeley, 595
  104. Pausas and Keeley, 596
  105. Pausas and Keeley, 597
  106. 107,0 107,1 Template:Vancite journal
  107. 108,0 108,1 Rackham, 229-230
  108. 109,0 109,1 Template:Vancite conference
  109. * Template:Vancite journal
  110. Template:Vancite journal
  111. Pitkänen, et. al., 15-16 and 27-30
  112. Template:Vancite journal University of Oregon Summary, accessed 2 Feb 2010
  113. Karki, 6.
  114. van Wagtendonk (1996), 1156.
  115. Interagency Strategy for the Implementation of the Federal Wildland Fire Policy, 42.
  116. San-Miguel-Ayanz, et al., 361.
  117. Karki, 7, 11-19.
  118. Fire. The Australian Experience, 7.
  119. Karki, 27.
  120. Template:Vancite web
  121. Template:Vancite web
  122. Template:Vancite journal
  123. Template:Vancite web
  124. Fire. The Australian Experience, 5-6.
  125. Graham, et al., 15.
  126. Peuch, 3.
  127. Template:Vancite web
  128. van Wagtendonk (1996), 1164
  129. Graham, et. al., 32-33.
  130. Template:Vancite web
  131. Template:Vancite web
  132. Karki, 14.
  133. Template:Vancite web
  134. Are Big Fires Inevitable? A Report on the National Bushfire Forum, 15.
  135. Template:Vancite web
  136. McKenzie, et al., 899
  137. Interagency Strategy for the Implementation of the Federal Wildland Fire Policy, 38-40.
  138. San-Miguel-Ayanz, et al., 362.
  139. 140,0 140,1 Template:Vancite journal
  140. Template:Vancite web
  141. Template:Vancite web
  142. "Evaluation of three wildfire smoke detection systems", 4
  143. Template:Vancite web
  144. Template:Vancite journal
  145. Template:Vancite web
  146. Template:Vancite web
  147. Template:Vancite web
  148. "Evaluation of three wildfire smoke detection systems", 6
  149. Template:Vancite web
  150. San-Miguel-Ayanz, et al., 366-369, 373-375.
  151. Template:Vancite web
  152. Template:Vancite web
  153. Template:Vancite web
  154. Template:Vancite web
  155. Template:Vancite web
  156. Template:Vancite journal
  157. Template:Vancite web
  158. Template:Vancite journal
  159. Karki, 16
  160. Template:Vancite web
  161. Template:Vancite web
  162. Plucinski, et al., 6
  163. Automatic remote surveillance system for the prevention of forest fires, 2
  164. Template:Vancite web
  165. Template:Vancite web
  166. Template:Vancite web
  167. Template:Vancite web
  168. Template:Vancite web
  169. Template:Vancite web
  170. G.D. Richards, “An Elliptical Growth Model of Forest Fire Fronts and Its Numerical Solution”, Int. J. Numer. Meth. Eng.,. 30:1163-1179, 1990.
  171. Finney, 1-3.


External linksModifica

I contenuti della comunità sono disponibili sotto la licenza CC-BY-SA a meno che non sia diversamente specificato.