Controlled burn

A controlled or prescribed burn, also known as hazard reduction burning,[1] backfire, swailing, or a burn-off,[2] is a wildfire set intentionally for purposes of forest management, farming, prairie restoration or greenhouse gas abatement. A controlled burn may also refer to the intentional burning of slash and fuels through burn piles.[3] Fire is a natural part of both forest and grassland ecology and controlled fire can be a tool for foresters. Hazard reduction or controlled burning is conducted during the cooler months to reduce fuel buildup and decrease the likelihood of serious hotter fires.[4] Controlled burning stimulates the germination of some desirable forest trees, and reveals soil mineral layers which increases seedling vitality, thus renewing the forest. Some cones, such as those of lodgepole pine and sequoia, are serotinous, as well as many chaparral shrubs, meaning they require heat from fire to open cones to disperse seeds.

In industrialized countries, controlled burning is usually overseen by fire control authorities for regulations and permits.


There are two basic causes of wildfires. One is natural (lightning) and the other is people.[5] Controlled burns have a long history in wildland management. Pre-agricultural societies used fire to regulate both plant and animal life. Fire history studies have documented periodic wildland fires ignited by indigenous peoples in North America and Australia.[6][7]

Fires, both naturally caused and prescribed, were once part of natural landscapes in many areas. These practices ended in the early 20th century when US fire policies were enacted with the goals of suppressing all fires.[7] Since 1995, the US Forest Service has slowly incorporated burning practices into its forest management policies.[8]

Back burning

Back burning is the term given to the process of lighting vegetation in such a way that it has to burn against the prevailing wind. This produces a slower moving and more controlable fire. This process is commonly used for hazard reduction burns and the preparation of fire breaks to enable controlled/ hazard reduction burns.

Back burning involves starting small fires along a man-made or natural firebreak in front of a main fire front.[9] Back burning reduces the amount of fuel that is available to the main fire by the time that it reaches the burnt area.

Back burning is utilized in controlled burning and during wildfire events. While controlled burns utilize back burning during planned fire events to create a "black line", back burning or backfiring is also done to stop a wildfire that is already in progress. Firebreaks are also often used as an anchor point to start a line of fires along natural or manmade features such as a river, road or a bulldozed clearing.[10] It is called back burning because the small fires are designed to "burn back" towards the main fire front and are usually burning and traveling against ground level winds.

See wikt:fight fire with fire.

Forest use

Another consideration is the issue of fire prevention. In Florida, during the drought in 1995, catastrophic wildfires burned numerous homes. But forestry managers in the Florida Division of Forestry noted that the underlying problem was previous cessation of controlled burning, resulting from complaints by homeowners. Each year additional leaf litter and dropped branches increased the likelihood of a hot and uncontrollable fire.[11]

Controlled burns are sometimes ignited using a tool known as the driptorch, which allows a steady stream of flaming fuel to be directed to the ground as needed. Variations on the driptorch can be used such as the helitorch, which is mounted on a helicopter, or other improvised devices such as mounting a driptorch-like device on the side of a vehicle. A pyrotechnic device known as a fusee can be used for ignition in nearby fuels while a Very pistol can be for fuels farther away.

For the burning of slash, waste materials left over from logging, there are several types of controlled burns. Broadcast burning is the burning of scattered slash over a wide area. Pile burning is gathering up the slash into piles before burning. These burning piles may be referred to as bonfires. High temperatures can harm the soil, damaging it physically, chemically or sterilizing it. Broadcast burns tend to have lower temperatures and will not harm the soil as much as pile burning,[12] though steps can be taken to treat the soil after a burn. In lop and scatter burning, slash is left to compact over time, or is compacted with machinery. This produces a lower intensity fire, as long as the slash is not packed too tightly.[12] However, soil may be damaged if machinery is used to compress the slash.

Controlled burning reduces fuels, may improve wildlife habitat,[13] controls competing vegetation, improves short term forage for grazing, improves accessibility, helps control tree disease, and perpetuates fire dependent species.[14] In mature longleaf pine forest, it helps maintain habitat for endangered red-cockaded woodpeckers in their sandhill and flatwoods habitats.[15] Fire is also felt to be a crucial element of the recovery of the threatened Louisiana pine snake in the longleaf pine forests of central Louisiana and eastern Texas.[16] However, many scientists disagree with such a simplistic approach, and indicate that each forest must be assessed on its own merit.

In the wild, many trees depend on fire as a successful way to clear out competition and release their seeds. In particular, the giant sequoia depends on fire to reproduce: the cones of the tree open after a fire releases their seeds, the fire having cleared all competing vegetation. Due to fire suppression efforts during the early and mid 20th century, low-intensity fires no longer occurred naturally in many groves, and still do not occur in some groves today. The suppression of fires also led to ground fuel build-up and the dense growth which posed the risk of catastrophic wildfires. It wasn't until the 1970s that the National Park Service began systematic fires for the purpose of new seed growth. Eucalyptus regnans or mountain ash of Australia also depends on fire but in a different fashion. They carry their seeds in capsules which can deposit at any time of the year. Being flammable, during a fire the capsules drop nearly all of their seeds and the fire consumes the eucalypt adults, but most of the seeds survive using the ash as a source of nutrients; at their rate of growth, they quickly dominate the land and a new eucalyptus forest grows.[17]

Agricultural use

In addition to forest management, controlled burning is also used in agriculture. In the developing world, this is often referred to as slash and burn. In industrialized nations, it is seen as one component of shifting cultivation, as a part of field preparation for planting. Often called field burning, this technique is used to clear the land of any existing crop residue as well as kill weeds and weed seeds. Field burning is less expensive than most other methods such as herbicides or tillage, but because it produces smoke and other fire-related pollutants, its use is not popular in agricultural areas bounded by residential housing.

In the United States, field burning is a legislative and regulatory issue at both the federal and state levels of government.


In Oregon, field burning has been widely used by grass seed farmers as a method for clearing fields for the next round of planting, as well as revitalizing serotinous grasses that require fire in order to grow seed again. The Oregon Department of Environmental Quality began requiring a permit for farmers to burn their fields in 1981, but the requirements became stricter in 1988 following a multi-car collision[18] in which smoke from field burning near Albany, Oregon, obscured the vision of drivers on Interstate 5, leading to a 23-car collision in which 5 people died and 37 were injured.[19] This resulted in more scrutiny of field burning and proposals to ban field burning in the state altogether.[20][21][22]

In the European Union burning crop stubble after harvest is used by farmers for plant health reasons under several restrictions in the cross compliance regulations.[23]

Political history

The conflict of controlled burn policy in the United States has roots in the historical campaigns to combat wildfires and to the eventual acceptance of fire as a necessary ecological phenomenon. The notion of fire as a tool had somewhat evolved by the late 1970s as the National Park Service authorized and administered controlled burns.[24] While the methodology was still relatively emergent the Yellowstone fires of 1988 struck, which significantly politicized fire management. The ensuing media coverage was a spectacle that was vulnerable to misinformation. Reports drastically inflated the scale of the fires which stigmatized politicians in Wyoming, Idaho, and Montana to believe that all fires represented a loss of revenue from tourism.[24] Partially as a result of millions of dollars lost in estimates, stricter data recording was enforced and thresholds were established for determining which fires must be suppressed.[25] Paramount to the new action plans is the suppression of fires that threaten the loss of human life with leniency toward areas of historic, scientific, or special ecological interest.[26] Since 1988, many states have made progress toward controlled burns but with a proclivity toward forgetfulness between fire events. Senators Ron Wyden and Mike Crapo of Oregon and Idaho have been moving to reduce the shifting of capital from fire prevention to fire suppression following the harsh fires of 2017 in both states.[27]


Depending on the context and goals of a prescribed fire, additional planning may be necessary. While the most common driver of fuel treatment is the prevention of loss of human life, certain parameters can also be changed to promote biodiversity and to rearrange stand ages appropriately. The risk of fatal fires can also be reduced proactively by reducing ground fuels before they can create a fuel ladder and begin an active crown fire. Predictions show thinned forests lead to mitigated fire intensity and flame length compared to untouched or fire-proofed areas.[28] Furthermore, low-intensity fire treatments can be administered in places where mechanized treatments such as disc harrowing cannot.[29] In the interests of conservation, electing for a mixed mosaic of unburnt islands within the targeted area maintains biodiversity and provides cover for wildlife. Because of this, some suggest fuel reductions of about 75% to be sufficient, though each burn plan should have its own target set by ecological and management goals.[30] In some areas where grasses and herbaceous plants thrive, species variation and cover can drastically increase a few years after fuel treatments.[31]

Heathland use

The controlled burning or swailing of heathland is used in the United Kingdom and other countries as a conservation tool. In Scotland it is known as muirburn.[29] Often it is used as a tool for creating fire breaks to reduce the risk of dangerous outbreaks but is also an important mechanism for preventing succession to woodier vegetation and plays an important role in the life cycle of heather species. Red grouse eat heather shoots and as grouse shooting has long been an expensive sport the landowners need to ensure a good crop of grouse so each year parts of the moor are burned of old heather to cause fresh shoots.[32][33]

Greenhouse gas abatement

Controlled burns on Australian savannas can result in an overall reduction of greenhouse gas emissions. One working example is the West Arnhem Fire Management Agreement, started to bring "strategic fire management across 28,000 square kilometres (11,000 sq mi) of Western Arnhem Land" to partially offset greenhouse gas emissions from a liquefied natural gas plant in Darwin, Australia. Deliberately starting controlled burns early in the dry season results in a mosaic of burnt and unburnt country which reduces the area of stronger, late dry season fires.[35] Also known as "patch burning". To minimise the impact of smoke, burning should be restricted to daylight hours whenever possible.[36]

See also


  1. "What is Hazard Reduction".
  2. Gage, Nicola (25 August 2016). "Burn-off rule change upsets Adelaide Hills residents". ABC News.
  3. "Managing Brush Fires" (PDF).
  4. Guidelines for Low Intensity Bushfire Hazard Redustion Burning Retrieved on 11-3-2009
  5. Fire Management Study Unit accessed May 8, 2016
  6. R.A. Bradstock; M. Bedward; B.J. Kenny; J. Scott (1998). "Spatially-explicit simulation of the effect of prescribed burning on fire regimes and plant extinctions in shrublands typical of south-eastern Australia". Biological Conservation. 86 (1): 83–95. doi:10.1016/S0006-3207(97)00170-5.
  7. Scott L. Stephens; Robert E. Martin; Nicholas E. Clinton (2007). "Prehistoric fire area and emissions from California's forests, woodlands, shrublands, and grasslands". Forest Ecology and Management. 251 (3): 205–216. doi:10.1016/j.foreco.2007.06.005.
  8. Scott L. Stephens; Lawrence W. Ruth (2005). "Federal Forest-Fire Policy in the United States". Ecological Society of America: Ecological Applications. 15 (2): 532–542. doi:10.1890/04-0545.
  9. What is Hazard Reduction? Retrieved on 10-3-2009
  10. "Explainer: back burning and fuel reduction". The Conversation. The Conversation Trust (UK) Limited. 8 August 2014. Retrieved 5 January 2016.
  11. Sah, Jay P.; Ross, Michael S.; Snyder, James R.; Koptur, Suzanne; Cooley, Hillary C. (2006). "Fuel loads, fire regimes, and post-fire fuel dynamics in Florida Keys pine forests" (PDF). International Journal of Wildland Fire. 15 (4): 463–478. CiteSeerX doi:10.1071/wf05100. Archived from the original (PDF) on 2011-12-11. Retrieved 2011-06-10.
  12. Julie E. Korb; Nancy C. Johnson; W. W. Covington (March 2004). "Slash Pile Burning Effects on Soil Biotic and Chemical Properties and Plant Establishment: Recommendations for Amelioration" (PDF). Restoration Ecology. 12 (1): 52–62. doi:10.1111/j.1061-2971.2004.00304.x.
  13. Palmer, W. E.; Engstrom, R. T.; Brennan, L. A. (2011-06-16). "Whither wildlife without fire?". Transactions of the 63Rd North American Wildlife and Natural Resources Conference; 1998 March 20-25; Orlando, Fl. Washington, Dc: Wildlife Management Institute: 402-414. Retrieved 2011-06-25.
  14. "Reasons For Prescribed Fire In Forest Resource Management - A Guide for Prescribed Fire in Southern Forests". 2003-03-24. Retrieved 2011-06-25.
  15. "Red-cockaded Woodpecker" (PDF). Retrieved 2011-06-25.
  17. "The Private Life of Plants". Internet Archive.
  18. Archived September 3, 2006, at the Wayback Machine
  19. Archived September 5, 2006, at the Wayback Machine
  20. 2008
  21. Mortensen, Camilla. "Blowing Smoke". Eugene Weekly. Archived from the original on 2011-09-03. Retrieved 2011-06-25.
  22. Retrieved January 20, 2007. Missing or empty |title= (help)
  23. "GAEC 6: Maintaining the level of organic matter in soil - Guide to cross compliance in England: 2016 - Guidance - GOV.UK".
  24. Rothman, Hal K. (2005). A Test of Adversity and Strength: Wildland Fire in the National Park System. U.S. National Park Service. p. 186.
  25. Franke, Mary Ann (2000). Yellowstone in the Afterglow: Lessons from the Fires. p. 41.
  26. "Forest Service Wilderness Fire Policy".
  27. "Wyden renews call for Congress to fix wildfire funding". Retrieved 2017-12-03.
  28. Mirra, Inês M.; Oliveira, Tiago M.; Barros, Ana M.G.; Fernandes, Paulo M. (2017). "Fuel dynamics following fire hazard reduction treatments in blue gum ( Eucalyptus globulus ) plantations in Portugal". Forest Ecology and Management. 398: 185–195. doi:10.1016/j.foreco.2017.05.016.
  29. "Guidance for the controlled burning of heather, grass and other moorland, in Scotland and other moorland, in Scotland".
  30., Charles T. Bargeron. "Reasons For Prescribed Fire In Forest Resource Management - A Guide for Prescribed Fire in Southern Forests". Retrieved 2017-12-06.
  31. Havrilla, Caroline A.; Faist, Akasha M.; Barger, Nichole N. (2017). "Understory Plant Community Responses to Fuel-Reduction Treatments and Seeding in an Upland Piñon-Juniper Woodland". Rangeland Ecology & Management. 70 (5): 609–620. doi:10.1016/j.rama.2017.04.002.
  32. "Archived copy". Archived from the original on 2012-04-25. Retrieved 2012-07-16.CS1 maint: archived copy as title (link)
  33. "UK: The Role of Fire in the Ecology of Heathland in Southern Britain (IFFN No. 18 - January 1998)". Archived from the original on 2011-07-16. Retrieved 2011-06-25.
  34. "Homeland Security Budget-in-Brief Fiscal Year 2009" (PDF). United States Department of Homeland Security. 2009. p. 71. Retrieved 31 January 2010.
  35. "West Arnhem Land Fire Abatement Project". Tropical Savannas CRC, Savanna Information. Tropical Savannas Cooperative Research Centre. Archived from the original on 2012-11-27. Retrieved 2007-10-08.
  36. Guidelines for Low Intensity Brush Fire Hazard Reduction Retrieved on May 8, 2016

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