A comparison of Canadian and Russian boreal forest fire regimes
► Most large fires occur in spring in central Russia and mid-summer in western Canada. ► In Russia, large fire frequency was 10×greater and area burned was 3×greater. ► Average large fire size was 4×greater in Canada. ► C emissions rate was higher in Canada but total C emissions was 2×higher in Russ...
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description | ► Most large fires occur in spring in central Russia and mid-summer in western Canada. ► In Russia, large fire frequency was 10×greater and area burned was 3×greater. ► Average large fire size was 4×greater in Canada. ► C emissions rate was higher in Canada but total C emissions was 2×higher in Russia. ► The crown fire rate was 57% in Canada and 6% in Russia.
Boreal forest dynamics are largely driven by disturbance, and fire is a prevalent force of change across the boreal circumpolar region. North American and Eurasian boreal fire regimes are known to be very different but there are few quantitative comparison studies. Russian and Canadian boreal fire regimes are compared using fire weather, fire statistics, fire behaviour, and C emissions data from two large study areas. Fuel consumption, head fire intensity, and C emissions were modelled using fire weather data, fuels data and burned area polygons for all large (200+ha) fires that occurred in the study areas during 2001–2007. Fire behaviour and C emissions of each large fire were simulated with the Canadian Fire Effects Model (CanFIRE) using fuel type and fuel load data of the burned areas, and Canadian Forest Fire Weather Index System parameters, as interpolated to the fire from the weather station network on the average active fire date. In the Russian study area located in central Siberia, there was an annual average of 1441.9 large fires per 100Mha of forest land that burned 1.89Mha (average large fire size=1312ha, mean fire return interval=52.9years) with an average fire intensity of 4858kWm−1. In the western Canada study area, there was an annual average of 93.7 large fires per 100Mha of forest land that burned 0.56Mha of forest (average large fire size=5930ha, mean fire return interval=179.9years) with an average fire intensity of 6047kWm−1. The 2001–2007 fire size distribution and annual area burned in the Canadian study area were very similar to 1970–2009 statistics, although large fire frequency was higher and average large fire size was smaller. Similar long-term fire statistics for Russia currently do not exist for comparison. The C emissions rate (tha−1 of burned area) was 53% higher in the Canadian study area due to higher pre-burn forest floor fuel loads and higher fuel consumption by crown fires. However, the Russian study area had much higher total C emissions (per 100Mha of forest area) because of greater annual area burned. The Russian C emissions estimate in this study is likely cons |
doi_str_mv | 10.1016/j.foreco.2012.07.033 |
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Boreal forest dynamics are largely driven by disturbance, and fire is a prevalent force of change across the boreal circumpolar region. North American and Eurasian boreal fire regimes are known to be very different but there are few quantitative comparison studies. Russian and Canadian boreal fire regimes are compared using fire weather, fire statistics, fire behaviour, and C emissions data from two large study areas. Fuel consumption, head fire intensity, and C emissions were modelled using fire weather data, fuels data and burned area polygons for all large (200+ha) fires that occurred in the study areas during 2001–2007. Fire behaviour and C emissions of each large fire were simulated with the Canadian Fire Effects Model (CanFIRE) using fuel type and fuel load data of the burned areas, and Canadian Forest Fire Weather Index System parameters, as interpolated to the fire from the weather station network on the average active fire date. In the Russian study area located in central Siberia, there was an annual average of 1441.9 large fires per 100Mha of forest land that burned 1.89Mha (average large fire size=1312ha, mean fire return interval=52.9years) with an average fire intensity of 4858kWm−1. In the western Canada study area, there was an annual average of 93.7 large fires per 100Mha of forest land that burned 0.56Mha of forest (average large fire size=5930ha, mean fire return interval=179.9years) with an average fire intensity of 6047kWm−1. The 2001–2007 fire size distribution and annual area burned in the Canadian study area were very similar to 1970–2009 statistics, although large fire frequency was higher and average large fire size was smaller. Similar long-term fire statistics for Russia currently do not exist for comparison. The C emissions rate (tha−1 of burned area) was 53% higher in the Canadian study area due to higher pre-burn forest floor fuel loads and higher fuel consumption by crown fires. However, the Russian study area had much higher total C emissions (per 100Mha of forest area) because of greater annual area burned. The Russian C emissions estimate in this study is likely conservative due to low forest floor fuel load estimates in available datasets. Fire regime differences are discussed in terms of fuel, weather, and fire ecology.</description><identifier>ISSN: 0378-1127</identifier><identifier>EISSN: 1872-7042</identifier><identifier>DOI: 10.1016/j.foreco.2012.07.033</identifier><identifier>CODEN: FECMDW</identifier><language>eng</language><publisher>Kidlington: Elsevier B.V</publisher><subject>Animal and plant ecology ; Animal, plant and microbial ecology ; Biological and medical sciences ; Carbon emissions ; Climatology ; Combustion ; Emission analysis ; Fire behaviour ; Fire ecology ; Fire weather ; Fires ; Forest and land fires ; Forestry ; Forests ; Fuels ; Fundamental and applied biological sciences. Psychology ; Phytopathology. Animal pests. Plant and forest protection ; Statistics ; Synecology ; Terrestrial ecosystems ; Weather ; Weather damages. Fires</subject><ispartof>Forest ecology and management, 2013-04, Vol.294, p.23-34</ispartof><rights>2012</rights><rights>2014 INIST-CNRS</rights><lds50>peer_reviewed</lds50><woscitedreferencessubscribed>false</woscitedreferencessubscribed><citedby>FETCH-LOGICAL-c519t-3f14cbd2d05f8d890ce3bba2ffbb55a753d023bc4244bb67a4243544f51da22b3</citedby><cites>FETCH-LOGICAL-c519t-3f14cbd2d05f8d890ce3bba2ffbb55a753d023bc4244bb67a4243544f51da22b3</cites></display><links><openurl>$$Topenurl_article</openurl><openurlfulltext>$$Topenurlfull_article</openurlfulltext><thumbnail>$$Tsyndetics_thumb_exl</thumbnail><linktohtml>$$Uhttps://dx.doi.org/10.1016/j.foreco.2012.07.033$$EHTML$$P50$$Gelsevier$$H</linktohtml><link.rule.ids>309,310,314,780,784,789,790,3550,23930,23931,25140,27924,27925,45995</link.rule.ids><backlink>$$Uhttp://pascal-francis.inist.fr/vibad/index.php?action=getRecordDetail&idt=27321133$$DView record in Pascal Francis$$Hfree_for_read</backlink></links><search><creatorcontrib>de Groot, William J.</creatorcontrib><creatorcontrib>Cantin, Alan S.</creatorcontrib><creatorcontrib>Flannigan, Michael D.</creatorcontrib><creatorcontrib>Soja, Amber J.</creatorcontrib><creatorcontrib>Gowman, Lynn M.</creatorcontrib><creatorcontrib>Newbery, Alison</creatorcontrib><title>A comparison of Canadian and Russian boreal forest fire regimes</title><title>Forest ecology and management</title><description>► Most large fires occur in spring in central Russia and mid-summer in western Canada. ► In Russia, large fire frequency was 10×greater and area burned was 3×greater. ► Average large fire size was 4×greater in Canada. ► C emissions rate was higher in Canada but total C emissions was 2×higher in Russia. ► The crown fire rate was 57% in Canada and 6% in Russia.
Boreal forest dynamics are largely driven by disturbance, and fire is a prevalent force of change across the boreal circumpolar region. North American and Eurasian boreal fire regimes are known to be very different but there are few quantitative comparison studies. Russian and Canadian boreal fire regimes are compared using fire weather, fire statistics, fire behaviour, and C emissions data from two large study areas. Fuel consumption, head fire intensity, and C emissions were modelled using fire weather data, fuels data and burned area polygons for all large (200+ha) fires that occurred in the study areas during 2001–2007. Fire behaviour and C emissions of each large fire were simulated with the Canadian Fire Effects Model (CanFIRE) using fuel type and fuel load data of the burned areas, and Canadian Forest Fire Weather Index System parameters, as interpolated to the fire from the weather station network on the average active fire date. In the Russian study area located in central Siberia, there was an annual average of 1441.9 large fires per 100Mha of forest land that burned 1.89Mha (average large fire size=1312ha, mean fire return interval=52.9years) with an average fire intensity of 4858kWm−1. In the western Canada study area, there was an annual average of 93.7 large fires per 100Mha of forest land that burned 0.56Mha of forest (average large fire size=5930ha, mean fire return interval=179.9years) with an average fire intensity of 6047kWm−1. The 2001–2007 fire size distribution and annual area burned in the Canadian study area were very similar to 1970–2009 statistics, although large fire frequency was higher and average large fire size was smaller. Similar long-term fire statistics for Russia currently do not exist for comparison. The C emissions rate (tha−1 of burned area) was 53% higher in the Canadian study area due to higher pre-burn forest floor fuel loads and higher fuel consumption by crown fires. However, the Russian study area had much higher total C emissions (per 100Mha of forest area) because of greater annual area burned. The Russian C emissions estimate in this study is likely conservative due to low forest floor fuel load estimates in available datasets. Fire regime differences are discussed in terms of fuel, weather, and fire ecology.</description><subject>Animal and plant ecology</subject><subject>Animal, plant and microbial ecology</subject><subject>Biological and medical sciences</subject><subject>Carbon emissions</subject><subject>Climatology</subject><subject>Combustion</subject><subject>Emission analysis</subject><subject>Fire behaviour</subject><subject>Fire ecology</subject><subject>Fire weather</subject><subject>Fires</subject><subject>Forest and land fires</subject><subject>Forestry</subject><subject>Forests</subject><subject>Fuels</subject><subject>Fundamental and applied biological sciences. Psychology</subject><subject>Phytopathology. Animal pests. Plant and forest protection</subject><subject>Statistics</subject><subject>Synecology</subject><subject>Terrestrial ecosystems</subject><subject>Weather</subject><subject>Weather damages. 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Psychology</topic><topic>Phytopathology. Animal pests. Plant and forest protection</topic><topic>Statistics</topic><topic>Synecology</topic><topic>Terrestrial ecosystems</topic><topic>Weather</topic><topic>Weather damages. Fires</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>de Groot, William J.</creatorcontrib><creatorcontrib>Cantin, Alan S.</creatorcontrib><creatorcontrib>Flannigan, Michael D.</creatorcontrib><creatorcontrib>Soja, Amber J.</creatorcontrib><creatorcontrib>Gowman, Lynn M.</creatorcontrib><creatorcontrib>Newbery, Alison</creatorcontrib><collection>Pascal-Francis</collection><collection>CrossRef</collection><collection>Ecology Abstracts</collection><collection>Environment Abstracts</collection><collection>Sustainability Science Abstracts</collection><collection>Environmental Sciences and Pollution Management</collection><collection>Technology Research Database</collection><collection>Engineering Research Database</collection><collection>Civil Engineering Abstracts</collection><jtitle>Forest ecology and management</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>de Groot, William J.</au><au>Cantin, Alan S.</au><au>Flannigan, Michael D.</au><au>Soja, Amber J.</au><au>Gowman, Lynn M.</au><au>Newbery, Alison</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>A comparison of Canadian and Russian boreal forest fire regimes</atitle><jtitle>Forest ecology and management</jtitle><date>2013-04-15</date><risdate>2013</risdate><volume>294</volume><spage>23</spage><epage>34</epage><pages>23-34</pages><issn>0378-1127</issn><eissn>1872-7042</eissn><coden>FECMDW</coden><abstract>► Most large fires occur in spring in central Russia and mid-summer in western Canada. ► In Russia, large fire frequency was 10×greater and area burned was 3×greater. ► Average large fire size was 4×greater in Canada. ► C emissions rate was higher in Canada but total C emissions was 2×higher in Russia. ► The crown fire rate was 57% in Canada and 6% in Russia.
Boreal forest dynamics are largely driven by disturbance, and fire is a prevalent force of change across the boreal circumpolar region. North American and Eurasian boreal fire regimes are known to be very different but there are few quantitative comparison studies. Russian and Canadian boreal fire regimes are compared using fire weather, fire statistics, fire behaviour, and C emissions data from two large study areas. Fuel consumption, head fire intensity, and C emissions were modelled using fire weather data, fuels data and burned area polygons for all large (200+ha) fires that occurred in the study areas during 2001–2007. Fire behaviour and C emissions of each large fire were simulated with the Canadian Fire Effects Model (CanFIRE) using fuel type and fuel load data of the burned areas, and Canadian Forest Fire Weather Index System parameters, as interpolated to the fire from the weather station network on the average active fire date. In the Russian study area located in central Siberia, there was an annual average of 1441.9 large fires per 100Mha of forest land that burned 1.89Mha (average large fire size=1312ha, mean fire return interval=52.9years) with an average fire intensity of 4858kWm−1. In the western Canada study area, there was an annual average of 93.7 large fires per 100Mha of forest land that burned 0.56Mha of forest (average large fire size=5930ha, mean fire return interval=179.9years) with an average fire intensity of 6047kWm−1. The 2001–2007 fire size distribution and annual area burned in the Canadian study area were very similar to 1970–2009 statistics, although large fire frequency was higher and average large fire size was smaller. Similar long-term fire statistics for Russia currently do not exist for comparison. The C emissions rate (tha−1 of burned area) was 53% higher in the Canadian study area due to higher pre-burn forest floor fuel loads and higher fuel consumption by crown fires. However, the Russian study area had much higher total C emissions (per 100Mha of forest area) because of greater annual area burned. The Russian C emissions estimate in this study is likely conservative due to low forest floor fuel load estimates in available datasets. Fire regime differences are discussed in terms of fuel, weather, and fire ecology.</abstract><cop>Kidlington</cop><pub>Elsevier B.V</pub><doi>10.1016/j.foreco.2012.07.033</doi><tpages>12</tpages></addata></record> |
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subjects | Animal and plant ecology Animal, plant and microbial ecology Biological and medical sciences Carbon emissions Climatology Combustion Emission analysis Fire behaviour Fire ecology Fire weather Fires Forest and land fires Forestry Forests Fuels Fundamental and applied biological sciences. Psychology Phytopathology. Animal pests. Plant and forest protection Statistics Synecology Terrestrial ecosystems Weather Weather damages. Fires |
title | A comparison of Canadian and Russian boreal forest fire regimes |
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