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Controlled burn

A controlled or prescribed (Rx) burn, which can include hazard reduction burning,[1] backfire, swailing or a burn-off,[2] is a fire set intentionally for purposes of forest management, fire suppression, 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.

Prescribed fire in ponderosa pine forest in eastern Washington, United States, to restore ecosystem health
Firing the woods in a South Carolina forest with a custom made driptorch mounted on an ATV. The device spits flaming fuel oil from the side, instantly igniting the leaf litter.
A prescribed burn in a Pinus nigra stand in Portugal
Near Holmen, Wisconsin
An aerial view of a controlled burn in Helderberg Nature Reserve in South Africa bordering the city of Cape Town. In South Africa controlled burns are important for maintaining the ecological health of indigenous fynbos as well as reducing the intensity of future burns.
Controlled burn in Hokkaido, Japan

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, sequoia and many chaparral shrubs are pyriscent, meaning heat from fire opens cones to disperse seeds.

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

History edit

There are two basic causes of wildfires. One is natural, mainly through lightning, and the other is human activity.[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] Native Americans frequently used fire to manage natural environments in a way that benefited humans and wildlife, starting low-intensity fires that released nutrients for plants, reduced competition, and consumed excess flammable material that otherwise would eventually fuel high-intensity, catastrophic fires.[8][9][10][11]

Fires, both naturally caused and prescribed, were once part of natural landscapes in many areas. In the US, these practices ended in the early 20th century, when federal fire policies were enacted with the goal of suppressing all fires.[7] Since 1995, the US Forest Service has slowly incorporated burning practices into its forest management policies.[12]

Fire suppression has changed the composition and ecology of North American habitats, including highly fire-dependent ecosystems such as oak savannas[13][14] and canebrakes,[15][16] which are now critically endangered habitats on the brink of extinction. In the Eastern United States, fire-sensitive trees such as the red maple are increasing in number, at the expense of fire-tolerant species like oaks.[17]

Controversies edit

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 7 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]

In the European Union, burning crop stubble after harvest is used by farmers for plant health reasons under several restrictions in cross-compliance regulations.[22]

With controlled burns, there is also a risk that the fires get out of control. For example, the Calf Canyon/Hermits Peak Fire, the largest wildfire in the history of New Mexico, was started by two distinct instances of controlled burns, which had both been set by the US Forest Service, getting out of control and merging.[23]

 
Muir burn in UK

In the north of Great Britain, large areas of grouse moors are managed by burning in a practice known as muirburn. This kills trees and grasses, preventing natural succession, and generates the mosaic of ling (heather) of different ages which allows very large populations of red grouse to be reared for shooting.[24] The peat-lands are some of the largest carbon sinks in the UK, providing an immensely important ecological service. The governments has restricted burning to the area but hunters have been continuing to set the moors ablaze, releasing a large amount of carbon into the atmosphere and destroying native habitat.[25]

The conflict of controlled burn policy in the United States has roots in historical campaigns to combat wildfires and to the eventual acceptance of fire as a necessary ecological phenomenon. Following colonization of North America, the US used fire suppression laws to eradicate the indigenous practice of prescribed fire. This was done against scientific evidence that supported prescribed burns as a natural process. At the loss to the local environment, colonies utilized fire suppression in order to benefit the logging industry.[26]

The notion of fire as a tool had somewhat evolved by the late 1970s as the National Park Service authorized and administered controlled burns.[27] Following prescribed fire reintroduction, the Yellowstone fires of 1988 occurred, 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 disposed politicians in Wyoming, Idaho, and Montana to believe that all fires represented a loss of revenue from tourism.[27][28] 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.[29]

There is still a debate amongst policy makers about how to deal with wildfires. 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.[30]

Tensions around fire prevention continue to rise due to the increasing prevalence of climate change. As drought conditions worsen, North America has been facing an abundance of destructive wildfires.[31] Since 1988, many states have made progress toward controlled burns. In 2021, California increased the amount of trained personnel to perform controlled burns and created more accessibility for landowners.[32]

Uses edit

 
Pile burn

Forestry edit

Controlled burning reduces fuels, may improve wildlife habitat,[33] controls competing vegetation,[34] improves short term forage for grazing, improves accessibility, helps control tree disease, and perpetuates fire dependent species.[35][36] To improve the application of prescribed burns for conservation goals, which may involve mimicking historical or natural fire regimes, scientists assess the impact of variation in fire attributes.[37] Fire frequency is the most discussed fire attribute in the scientific literature, likely because it is considered the most critical fire regime aspect.[38] Scientists less often report data concerning the effects of variation in other fire attributes (i.e., intensity, severity, patchiness, spatial scale, or phenology), even though these also likely impact conservation goals.[38]

Furthermore, low-intensity fire treatments can be administered in places where mechanized treatments such as disc harrowing cannot.[39][40] In some areas where grasses and herbaceous plants thrive, species variation and cover can drastically increase a few years after fuel treatments.[41]

Many trees depend on fire as a way to clear out other plant species and release their seeds. The giant sequoia, among other fire adapted tree species[42], depends on fire to reproduce. The cones are pyriscent so they will only open after exposed to a certain temperature. This reduces competition for the giant sequoia seedlings because the fire has cleared non fire-adapted, competing species.[43][44]

Eucalyptus regnans or mountain ash of Australia also depends on fire but in a different fashion. The plant structure shows a unique evolution with fire, quickly replacing damaged buds or stems in the case of danger. They carry their seeds in capsules which can be deposited at any time of the year. During a wildfire, 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.[45]

Agriculture edit

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.[46]

Prescribed fires are broadly used in the context of woody plant encroachment, with the aim of improving the balance of woody plants and grasses in shrublands and grasslands.[47][48][49][50]

In Northern-India, especially, In Punjab, Haryana, and Uttar Pradesh, crop residue burning is a major problem. CRB leads to degradation in environmental quality in these and neighboring states including in the capital of India, New Delhi.[51]

In East Africa, bird densities increased months after controlled burning had occurred.[52]

Grassland restoration edit

Many endangered native plants in North America are adapted to survive occasional low intensity fires.[53] Controlled burns in prairie ecosystems mimic low intensity to shift the composition of plants from non-native species to native species. These controlled burns occur during the early spring before native plants begin actively growing, when soil moisture is higher and the fuel load is low[54] to ensure that the controlled burn remains low intensity.

Greenhouse gas abatement edit

Controlled burns on Australian savannas can result in a long-term cumulative reduction in 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;[55][56] it is also known as "patch burning".

Procedure edit

 
 
Firefighters light, then extinguish a controlled burn in response to the 2020 Creek Fire in California.

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.

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,[57] 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.[57]

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.[58]

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 controllable fire. 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 man-made features such as a river, road or a bulldozed clearing.[59]

To minimise the impact of smoke, burning should be restricted to daylight hours whenever possible.[60]

In Ontario, Canada, controlled burns are regulated by the Ministry of Natural Resources and only trained personnel can plan and ignite controlled burns within Ontario's fire regions or if the Ministry of Natural Resources in involved in any aspect of planning a controlled burn.[61] The team performing the prescribed burn is divided into several roles; the Burn Boss, Communications, Suppression and Ignition.[62] The planning process begins by submitting an application to a local fire management office and after approval, applicants must submit a burn plan several weeks prior to ignition.[61]

 
Northern California fire crews start a backfire to stop the Poomacha fire from advancing westward.[63]

See also edit

References edit

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  3. ^ "Managing Brush Fires" (PDF). February 2017.
  4. ^ Guidelines for Low Intensity Bushfire Hazard Reduction Burning 2019-03-12 at the Wayback Machine Retrieved on 11-3-2009
  5. ^ Rachel G. Schneider; Deborah Breedlove. "Fire Management Study Unit" (PDF). Georgia Forestry Commission. Retrieved 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. Bibcode:1998BCons..86...83B. doi:10.1016/S0006-3207(97)00170-5.
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Further reading edit

  • Beese, W.J., Blackwell, B.A., Green, R.N. & Hawkes, B.C. (2006). "Prescribed burning impacts on some coastal British Columbia ecosystems." Information Report BC-X-403. Victoria B.C.: Natural Resources Canada, Canadian Forest Service, Pacific Forestry Centre. Retrieved from: http://hdl.handle.net/10613/2740
  • Casals P, Valor T, Besalú A, Molina-Terrén D. Understory fuel load and structure eight to nine years after prescribed burning in Mediterranean pine forests. DOI: 10.1016/j.foreco.2015.11.050
  • Valor T, González-Olabarria JR, Piqué M. Assessing the impact of prescribed burning on the growth of European pines. DOI: 10.1016/j.foreco.2015.02.002.

External links edit

controlled, burn, back, burn, redirects, here, village, scotland, backburn, canadian, group, backburner, group, controlled, burns, managed, aboriginal, australians, fire, stick, farming, confused, with, control, fire, early, humans, controlled, prescribed, bur. Back burn redirects here For the village in Scotland see Backburn For the Canadian group see Backburner hip hop group For the controlled burns managed by Aboriginal Australians see Fire stick farming Not to be confused with Control of fire by early humans A controlled or prescribed Rx burn which can include hazard reduction burning 1 backfire swailing or a burn off 2 is a fire set intentionally for purposes of forest management fire suppression 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 Prescribed fire in ponderosa pine forest in eastern Washington United States to restore ecosystem healthFiring the woods in a South Carolina forest with a custom made driptorch mounted on an ATV The device spits flaming fuel oil from the side instantly igniting the leaf litter A prescribed burn in a Pinus nigra stand in PortugalNear Holmen WisconsinAn aerial view of a controlled burn in Helderberg Nature Reserve in South Africa bordering the city of Cape Town In South Africa controlled burns are important for maintaining the ecological health of indigenous fynbos as well as reducing the intensity of future burns Controlled burn in Hokkaido JapanHazard 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 sequoia and many chaparral shrubs are pyriscent meaning heat from fire opens cones to disperse seeds In industrialized countries controlled burning regulations and permits are usually overseen by fire control authorities Contents 1 History 1 1 Controversies 2 Uses 2 1 Forestry 2 2 Agriculture 2 3 Grassland restoration 2 4 Greenhouse gas abatement 3 Procedure 4 See also 5 References 6 Further reading 7 External linksHistory editThere are two basic causes of wildfires One is natural mainly through lightning and the other is human activity 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 Native Americans frequently used fire to manage natural environments in a way that benefited humans and wildlife starting low intensity fires that released nutrients for plants reduced competition and consumed excess flammable material that otherwise would eventually fuel high intensity catastrophic fires 8 9 10 11 Fires both naturally caused and prescribed were once part of natural landscapes in many areas In the US these practices ended in the early 20th century when federal fire policies were enacted with the goal of suppressing all fires 7 Since 1995 the US Forest Service has slowly incorporated burning practices into its forest management policies 12 Fire suppression has changed the composition and ecology of North American habitats including highly fire dependent ecosystems such as oak savannas 13 14 and canebrakes 15 16 which are now critically endangered habitats on the brink of extinction In the Eastern United States fire sensitive trees such as the red maple are increasing in number at the expense of fire tolerant species like oaks 17 Controversies edit 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 7 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 In the European Union burning crop stubble after harvest is used by farmers for plant health reasons under several restrictions in cross compliance regulations 22 With controlled burns there is also a risk that the fires get out of control For example the Calf Canyon Hermits Peak Fire the largest wildfire in the history of New Mexico was started by two distinct instances of controlled burns which had both been set by the US Forest Service getting out of control and merging 23 nbsp Muir burn in UKIn the north of Great Britain large areas of grouse moors are managed by burning in a practice known as muirburn This kills trees and grasses preventing natural succession and generates the mosaic of ling heather of different ages which allows very large populations of red grouse to be reared for shooting 24 The peat lands are some of the largest carbon sinks in the UK providing an immensely important ecological service The governments has restricted burning to the area but hunters have been continuing to set the moors ablaze releasing a large amount of carbon into the atmosphere and destroying native habitat 25 The conflict of controlled burn policy in the United States has roots in historical campaigns to combat wildfires and to the eventual acceptance of fire as a necessary ecological phenomenon Following colonization of North America the US used fire suppression laws to eradicate the indigenous practice of prescribed fire This was done against scientific evidence that supported prescribed burns as a natural process At the loss to the local environment colonies utilized fire suppression in order to benefit the logging industry 26 The notion of fire as a tool had somewhat evolved by the late 1970s as the National Park Service authorized and administered controlled burns 27 Following prescribed fire reintroduction the Yellowstone fires of 1988 occurred 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 disposed politicians in Wyoming Idaho and Montana to believe that all fires represented a loss of revenue from tourism 27 28 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 29 There is still a debate amongst policy makers about how to deal with wildfires 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 30 Tensions around fire prevention continue to rise due to the increasing prevalence of climate change As drought conditions worsen North America has been facing an abundance of destructive wildfires 31 Since 1988 many states have made progress toward controlled burns In 2021 California increased the amount of trained personnel to perform controlled burns and created more accessibility for landowners 32 Uses edit nbsp Pile burnForestry edit Controlled burning reduces fuels may improve wildlife habitat 33 controls competing vegetation 34 improves short term forage for grazing improves accessibility helps control tree disease and perpetuates fire dependent species 35 36 To improve the application of prescribed burns for conservation goals which may involve mimicking historical or natural fire regimes scientists assess the impact of variation in fire attributes 37 Fire frequency is the most discussed fire attribute in the scientific literature likely because it is considered the most critical fire regime aspect 38 Scientists less often report data concerning the effects of variation in other fire attributes i e intensity severity patchiness spatial scale or phenology even though these also likely impact conservation goals 38 Furthermore low intensity fire treatments can be administered in places where mechanized treatments such as disc harrowing cannot 39 40 In some areas where grasses and herbaceous plants thrive species variation and cover can drastically increase a few years after fuel treatments 41 Many trees depend on fire as a way to clear out other plant species and release their seeds The giant sequoia among other fire adapted tree species 42 depends on fire to reproduce The cones are pyriscent so they will only open after exposed to a certain temperature This reduces competition for the giant sequoia seedlings because the fire has cleared non fire adapted competing species 43 44 Eucalyptus regnans or mountain ash of Australia also depends on fire but in a different fashion The plant structure shows a unique evolution with fire quickly replacing damaged buds or stems in the case of danger They carry their seeds in capsules which can be deposited at any time of the year During a wildfire 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 45 Agriculture edit See also Stubble burning 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 46 Prescribed fires are broadly used in the context of woody plant encroachment with the aim of improving the balance of woody plants and grasses in shrublands and grasslands 47 48 49 50 In Northern India especially In Punjab Haryana and Uttar Pradesh crop residue burning is a major problem CRB leads to degradation in environmental quality in these and neighboring states including in the capital of India New Delhi 51 In East Africa bird densities increased months after controlled burning had occurred 52 Grassland restoration edit Many endangered native plants in North America are adapted to survive occasional low intensity fires 53 Controlled burns in prairie ecosystems mimic low intensity to shift the composition of plants from non native species to native species These controlled burns occur during the early spring before native plants begin actively growing when soil moisture is higher and the fuel load is low 54 to ensure that the controlled burn remains low intensity Greenhouse gas abatement edit Controlled burns on Australian savannas can result in a long term cumulative reduction in 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 55 56 it is also known as patch burning Procedure edit nbsp nbsp Firefighters light then extinguish a controlled burn in response to the 2020 Creek Fire in California 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 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 57 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 57 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 58 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 controllable fire 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 man made features such as a river road or a bulldozed clearing 59 To minimise the impact of smoke burning should be restricted to daylight hours whenever possible 60 In Ontario Canada controlled burns are regulated by the Ministry of Natural Resources and only trained personnel can plan and ignite controlled burns within Ontario s fire regions or if the Ministry of Natural Resources in involved in any aspect of planning a controlled burn 61 The team performing the prescribed burn is divided into several roles the Burn Boss Communications Suppression and Ignition 62 The planning process begins by submitting an application to a local fire management office and after approval applicants must submit a burn plan several weeks prior to ignition 61 nbsp Northern California fire crews start a backfire to stop the Poomacha fire from advancing westward 63 See also editAgroecology Cultural burning Fire ecology Fire stick farming Native American use of fire in ecosystems Wildfire suppressionReferences edit What is Hazard Reduction www hillside rfsa org au Archived from the original on 2019 10 09 Retrieved 2009 03 10 Gage Nicola 25 August 2016 Burn off rule change upsets Adelaide Hills residents ABC News Managing Brush Fires PDF February 2017 Guidelines for Low Intensity Bushfire Hazard Reduction Burning Archived 2019 03 12 at the Wayback Machine Retrieved on 11 3 2009 Rachel G Schneider Deborah Breedlove Fire Management Study Unit PDF Georgia Forestry Commission Retrieved May 8 2016 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 Bibcode 1998BCons 86 83B doi 10 1016 S0006 3207 97 00170 5 a b 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 Chapter Introduction Fire Ecology PDF Palmer Jane 29 March 2021 Fire as Medicine Learning from Native American Fire Stewardship eos org Sten Michaela Fire Adapted Plants and Animals Rely on Wildfires for Resilient Ecosystems defenders org Hoffman Kira Christianson Amy Dickson Hoyle Sarah 31 March 2022 The right to burn barriers and opportunities for Indigenous led fire stewardship in Canada FACETS 7 January 2022 464 481 doi 10 1139 facets 2021 0062 S2CID 247891618 Scott L Stephens Lawrence W Ruth 2005 Federal Forest Fire Policy in the United States Ecological Applications 15 2 532 542 Bibcode 2005EcoAp 15 532S doi 10 1890 04 0545 Oak Savannas characteristics restoration and long term management oaksavannas org Barrens and Savannas communities of Wisconsin Cockman Crystal The loss of the great canebrakes ui charlotte edu UNC Charlotte Urban Institute Shoemaker Cory M 2018 Environmental and landscape factors affecting the continued suppression of canebrakes Arundinaria gigantea Poaceae within restorations of bottomland hardwood forests The Journal of the Torrey Botanical Society 145 2 156 152 doi 10 3159 TORREY D 17 00011 1 S2CID 90442090 Highfield Craig 21 November 2018 Foresters conflicted love for red maple highlights its various roles bayjournal com 1 Archived September 3 2006 at the Wayback Machine 2 Archived September 5 2006 at the Wayback Machine 2008 dead link Mortensen Camilla Blowing Smoke Eugene Weekly Archived from the original on 2011 09 03 Retrieved 2011 06 25 GAEC 6 Maintaining the level of organic matter in soil Guide to cross compliance in England 2016 Guidance GOV UK www gov uk 5 January 2024 Romero Simon 21 June 2022 The Government Set a Colossal Wildfire What Are Victims Owed New York Times Retrieved 8 November 2022 Shrubsole Guy Cameron Alasdair 24 February 2019 Friends of the Earth sparks moorland burning investigation Friends of the Earth Retrieved 30 October 2019 Dowler Emma Howard Crispin 2022 05 30 Satellites reveal widespread burning on England s protected peatlands despite government ban Unearthed Retrieved 2023 04 28 a href Template Cite web html title Template Cite web cite web a CS1 maint multiple names authors list link Vinyeta Kirsten 2021 10 12 Under the guise of science how the US Forest Service deployed settler colonial and racist logics to advance an unsubstantiated fire suppression agenda Environmental Sociology 8 2 134 148 doi 10 1080 23251042 2021 1987608 ISSN 2325 1042 S2CID 244604573 a b Rothman Hal K 2005 A Test of Adversity and Strength Wildland Fire in the National Park System U S National Park Service p 186 Franke Mary Ann 2000 Yellowstone in the Afterglow Lessons from the Fires pp 41 Forest Service Wilderness Fire Policy Wyden renews call for Congress to fix wildfire funding OregonLive com Retrieved 2017 12 03 Mueller Stephanie E Thode Andrea E Margolis Ellis Q Yocom Larissa L Young Jesse D Iniguez Jose M 2020 03 15 Climate relationships with increasing wildfire in the southwestern US from 1984 to 2015 Forest Ecology and Management 460 117861 doi 10 1016 j foreco 2019 117861 ISSN 0378 1127 S2CID 212684658 Bill Text AB 642 Wildfires leginfo legislature ca gov Retrieved 2023 04 28 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 Treesearch fs fed us Archived from the original on 2012 03 25 Retrieved 2011 06 25 Franklin Caroline M A Nielsen Scott E Macdonald S Ellen September 2019 Understory vascular plant responses to retention harvesting with and without prescribed fire Canadian Journal of Forest Research 49 9 1087 1100 doi 10 1139 cjfr 2018 0288 ISSN 0045 5067 Reasons For Prescribed Fire In Forest Resource Management A Guide for Prescribed Fire in Southern Forests Bugwood org 2003 03 24 Archived from the original on 2011 07 05 Retrieved 2011 06 25 Louisiana Pine Snake Pituophis ruthveni PDF Archived from the original PDF on 13 May 2006 Retrieved 15 March 2022 The suppression of natural fire events may represent the greatest threat to the Louisiana pine snake in recent years decreasing both the quantity and quality of habitat available to pine snakes The longleaf pine savannah forest evolved as a fire climax community adapted to the occurrence of frequent but low intensity ground fires Bowman D M Perry G L Higgins S I Johnson C N Fuhlendorf S D Murphy B P 2016 Pyrodiversity is the coupling of biodiversity and fire regimes in food webs Philosophical Transactions of the Royal Society B Biological Sciences 371 1696 doi 10 1098 rstb 2015 0169 PMC 4874407 PMID 27216526 a b Mason D S Lashley M A 2021 Spatial scale in prescribed fire regimes an understudied aspect in conservation with examples from the southeastern United States Fire Ecology 17 1 1 14 Bibcode 2021FiEco 17a 3M doi 10 1186 s42408 020 00087 9 Guidance for the controlled burning of heather grass and other moorland in Scotland and other moorland in Scotland Bargeron Charles T Reasons For Prescribed Fire In Forest Resource Management A Guide for Prescribed Fire in Southern Forests bugwood org Archived from the original on 2017 12 06 Retrieved 2017 12 06 Havrilla Caroline A Faist Akasha M Barger Nichole N 2017 Understory Plant Community Responses to Fuel Reduction Treatments and Seeding in an Upland Pinon Juniper Woodland Rangeland Ecology amp Management 70 5 609 620 doi 10 1016 j rama 2017 04 002 S2CID 90056096 Tianhua He December 2015 A 350 million year legacy of fire adaptation among conifers Journal of Ecology 104 via ResearchGate Shellhammer Howard S Shellhammer Thomas H October 2006 Giant Sequoia Sequoiadendron Giganteum Taxodiacea Seedling Survival and Growth in the First Four Decades Following Managed Fires Madrono 53 4 342 350 doi 10 3120 0024 9637 2006 53 342 gssgts 2 0 co 2 ISSN 0024 9637 S2CID 85700856 Giant Sequoia Ecology Chapter 5 www nps gov Retrieved 2024 02 14 Waters David A Burrows Geoffrey E Harper John D I April 2010 Eucalyptus regnans Myrtaceae A fire sensitive eucalypt with a resprouter epicormic structure American Journal of Botany 97 4 545 556 doi 10 3732 ajb 0900158 PMID 21622417 State of Oregon Smoke and Field Burning Field Burning www oregon gov Retrieved 2023 04 27 Trollope W S W January 1980 Controlling bush encroachment with fire in the savanna areas of South Africa Proceedings of the Annual Congresses of the Grassland Society of Southern Africa 15 1 173 177 doi 10 1080 00725560 1980 9648907 ISSN 0072 5560 Smit Izak P J Asner Gregory P Govender Navashni Vaughn Nicholas R van Wilgen Brian W October 2016 Kardol Paul ed An examination of the potential efficacy of high intensity fires for reversing woody encroachment in savannas Journal of Applied Ecology 53 5 1623 1633 Bibcode 2016JApEc 53 1623S doi 10 1111 1365 2664 12738 ISSN 0021 8901 Twidwell Dirac Fuhlendorf Samuel D Taylor Charles A Rogers William E June 2013 Kardol Paul ed Refining thresholds in coupled fire vegetation models to improve management of encroaching woody plants in grasslands Journal of Applied Ecology 50 3 603 613 Bibcode 2013JApEc 50 603T doi 10 1111 1365 2664 12063 ISSN 0021 8901 Lohmann Dirk Tietjen Britta Blaum Niels Joubert David Francois Jeltsch Florian August 2014 Prescribed fire as a tool for managing shrub encroachment in semi arid savanna rangelands Journal of Arid Environments 107 49 56 Bibcode 2014JArEn 107 49L doi 10 1016 j jaridenv 2014 04 003 Antar Mohammed Lyu Dongmei Nazari Mahtab Shah Ateeq Zhou Xiaomin Smith Donald L 2021 Biomass for a sustainable bioeconomy An overview of world biomass production and utilization Renewable and Sustainable Energy Reviews Elsevier BV 139 110691 doi 10 1016 j rser 2020 110691 ISSN 1364 0321 S2CID 233526225 This review cites this research Jain Niveta Bhatia Arti Pathak Himanshu 2014 Emission of Air Pollutants from Crop Residue Burning in India Aerosol and Air Quality Research 14 1 422 430 doi 10 4209 aaqr 2013 01 0031 ISSN 2071 1409 Gregory Nathan C Sensenig Ryan L Wilcove David S 2010 11 11 Effects of Controlled Fire and Livestock Grazing on Bird Communities in East African Savannas Conservation Biology 24 6 1606 1616 Bibcode 2010ConBi 24 1606G doi 10 1111 j 1523 1739 2010 01533 x ISSN 0888 8892 PMID 20561002 S2CID 33746569 Prescribed Burn FAQs Tallgrass Ontario tallgrassontario org Retrieved 2024 02 07 Stubbendieck James Volesky Jerry Ortmann John 1998 Grassland Management with Prescribed Fire PDF University of Nebraska Lincoln Extension Retrieved February 7 2024 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 Russell Smith Jeremy Whitehead Peter J Cooke Peter 2009 Culture ecology and economy of fire management in Northern Australia savannas rekindling the Wurrk tradition editors Jeremy Russell Smith Peter Whitehead Peter Cooke CSIRO Publishing a b 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 Bibcode 2004ResEc 12 52K doi 10 1111 j 1061 2971 2004 00304 x S2CID 85744169 Archived from the original PDF on 2016 03 04 Retrieved 2011 06 10 Mirra Ines 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 Whelan Robert J December 2002 Managing Fire Regimes for Conservation and Property Protection an Australian Response Conservation Biology 16 6 1659 1661 Bibcode 2002ConBi 16 1659W doi 10 1046 j 1523 1739 2002 02091 x ISSN 0888 8892 S2CID 84309403 Guidelines for Low Intensity Brush Fire Hazard Reduction http www hillside rfsa org au lowintensityhrburn pdf Archived 2019 03 12 at the Wayback Machine Retrieved on May 8 2016 a b Prescribed burns ontario ca www ontario ca Retrieved 2024 02 07 Ontario Ministry of Natural Resources May 2019 Prescribed Burn Manual PDF Ministry of Natural Resources Retrieved February 7 2024 Homeland Security Budget in Brief Fiscal Year 2009 PDF United States Department of Homeland Security 2009 p 71 Retrieved 31 January 2010 Further reading editBeese W J Blackwell B A Green R N amp Hawkes B C 2006 Prescribed burning impacts on some coastal British Columbia ecosystems Information Report BC X 403 Victoria B C Natural Resources Canada Canadian Forest Service Pacific Forestry Centre Retrieved from http hdl handle net 10613 2740 Casals P Valor T Besalu A Molina Terren D Understory fuel load and structure eight to nine years after prescribed burning in Mediterranean pine forests DOI 10 1016 j foreco 2015 11 050 Valor T Gonzalez Olabarria JR Pique M Assessing the impact of prescribed burning on the growth of European pines DOI 10 1016 j foreco 2015 02 002 External links edit nbsp Wikimedia Commons has media related to Controlled burns U S National Park Service Prescribed Fire Policy Savanna Oak Foundation article on controlled burns The Nature Conservancy s Global Fire Initiative Retrieved from https en wikipedia org w index php title Controlled burn amp oldid 1207403957, wikipedia, wiki, book, books, library,

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