Historical patterns of fire severity and forest structure and composition in a landscape structured by frequent large fires: Pumice Plateau ecoregion, Oregon, USA

Context Lack of quantitative observations of extent, frequency, and severity of large historical fires constrains awareness of departure of contemporary conditions from those that demonstrated resistance and resilience to frequent fire and recurring drought. Objectives Compare historical and contemp...

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Published in:Landscape ecology Vol. 34; no. 3; pp. 551 - 568
Main Authors: Hagmann, R. Keala, Merschel, Andrew G., Reilly, Matthew J.
Format: Journal Article
Language:English
Published: Dordrecht Springer Netherlands 01.03.2019
Springer Nature B.V
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ISSN:0921-2973, 1572-9761
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Abstract Context Lack of quantitative observations of extent, frequency, and severity of large historical fires constrains awareness of departure of contemporary conditions from those that demonstrated resistance and resilience to frequent fire and recurring drought. Objectives Compare historical and contemporary fire and forest conditions for a dry forest landscape with few barriers to fire spread. Methods Quantify differences in (1) historical (1700–1918) and contemporary (1985–2015) fire extent, fire rotation, and stand-replacing fire and (2) historical (1914–1924) and contemporary (2012) forest structure and composition. Data include 85,750-ha tree-ring reconstruction of fire frequency and extent; > 375,000-ha timber inventory following > 78,900-ha fires in 1918; and remotely-sensed maps of contemporary fire effects and forest conditions. Results Historically, fires > 20,000 ha occurred every 9.5 years; fire rotation was 14.9 years; seven fires > 40,469 ha occurred during extreme drought (PDSI < − 4.0); and stand-replacing fire occurred primarily in lodgepole ( Pinus contorta var. murrayana ). In contemporary fires, only 5% of the ecoregion burned in 30 years, and stand-replacing fire occurred primarily in ponderosa ( Pinus ponderosa ) and mixed-conifer. Historically, density of conifers > 15 cm dbh exceeded 120 trees/ha on < 5% of the area compared to 95% currently. Conclusions Frequent, large, low-severity fires historically maintained open-canopy ponderosa and mixed-conifer forests in which large fire- and drought-tolerant trees were prevalent. Stand-replacing patches in ponderosa and mixed-conifer were rare, even in fires > 40,469 ha (minimum size of contemporary “megafires”) during extreme drought. In this frequent-fire landscape, mixed-severity fire historically influenced lodgepole and adjacent forests. Lack of large, frequent, low-severity fires degrades contemporary forest ecosystems.
AbstractList ContextLack of quantitative observations of extent, frequency, and severity of large historical fires constrains awareness of departure of contemporary conditions from those that demonstrated resistance and resilience to frequent fire and recurring drought.ObjectivesCompare historical and contemporary fire and forest conditions for a dry forest landscape with few barriers to fire spread.MethodsQuantify differences in (1) historical (1700–1918) and contemporary (1985–2015) fire extent, fire rotation, and stand-replacing fire and (2) historical (1914–1924) and contemporary (2012) forest structure and composition. Data include 85,750-ha tree-ring reconstruction of fire frequency and extent; > 375,000-ha timber inventory following > 78,900-ha fires in 1918; and remotely-sensed maps of contemporary fire effects and forest conditions.ResultsHistorically, fires > 20,000 ha occurred every 9.5 years; fire rotation was 14.9 years; seven fires > 40,469 ha occurred during extreme drought (PDSI < − 4.0); and stand-replacing fire occurred primarily in lodgepole (Pinus contorta var. murrayana). In contemporary fires, only 5% of the ecoregion burned in 30 years, and stand-replacing fire occurred primarily in ponderosa (Pinus ponderosa) and mixed-conifer. Historically, density of conifers > 15 cm dbh exceeded 120 trees/ha on < 5% of the area compared to 95% currently.ConclusionsFrequent, large, low-severity fires historically maintained open-canopy ponderosa and mixed-conifer forests in which large fire- and drought-tolerant trees were prevalent. Stand-replacing patches in ponderosa and mixed-conifer were rare, even in fires > 40,469 ha (minimum size of contemporary “megafires”) during extreme drought. In this frequent-fire landscape, mixed-severity fire historically influenced lodgepole and adjacent forests. Lack of large, frequent, low-severity fires degrades contemporary forest ecosystems.
Context Lack of quantitative observations of extent, frequency, and severity of large historical fires constrains awareness of departure of contemporary conditions from those that demonstrated resistance and resilience to frequent fire and recurring drought. Objectives Compare historical and contemporary fire and forest conditions for a dry forest landscape with few barriers to fire spread. Methods Quantify differences in (1) historical (1700–1918) and contemporary (1985–2015) fire extent, fire rotation, and stand-replacing fire and (2) historical (1914–1924) and contemporary (2012) forest structure and composition. Data include 85,750-ha tree-ring reconstruction of fire frequency and extent; > 375,000-ha timber inventory following > 78,900-ha fires in 1918; and remotely-sensed maps of contemporary fire effects and forest conditions. Results Historically, fires > 20,000 ha occurred every 9.5 years; fire rotation was 14.9 years; seven fires > 40,469 ha occurred during extreme drought (PDSI < − 4.0); and stand-replacing fire occurred primarily in lodgepole ( Pinus contorta var. murrayana ). In contemporary fires, only 5% of the ecoregion burned in 30 years, and stand-replacing fire occurred primarily in ponderosa ( Pinus ponderosa ) and mixed-conifer. Historically, density of conifers > 15 cm dbh exceeded 120 trees/ha on < 5% of the area compared to 95% currently. Conclusions Frequent, large, low-severity fires historically maintained open-canopy ponderosa and mixed-conifer forests in which large fire- and drought-tolerant trees were prevalent. Stand-replacing patches in ponderosa and mixed-conifer were rare, even in fires > 40,469 ha (minimum size of contemporary “megafires”) during extreme drought. In this frequent-fire landscape, mixed-severity fire historically influenced lodgepole and adjacent forests. Lack of large, frequent, low-severity fires degrades contemporary forest ecosystems.
CONTEXT: Lack of quantitative observations of extent, frequency, and severity of large historical fires constrains awareness of departure of contemporary conditions from those that demonstrated resistance and resilience to frequent fire and recurring drought. OBJECTIVES: Compare historical and contemporary fire and forest conditions for a dry forest landscape with few barriers to fire spread. METHODS: Quantify differences in (1) historical (1700–1918) and contemporary (1985–2015) fire extent, fire rotation, and stand-replacing fire and (2) historical (1914–1924) and contemporary (2012) forest structure and composition. Data include 85,750-ha tree-ring reconstruction of fire frequency and extent; > 375,000-ha timber inventory following > 78,900-ha fires in 1918; and remotely-sensed maps of contemporary fire effects and forest conditions. RESULTS: Historically, fires > 20,000 ha occurred every 9.5 years; fire rotation was 14.9 years; seven fires > 40,469 ha occurred during extreme drought (PDSI < − 4.0); and stand-replacing fire occurred primarily in lodgepole (Pinus contorta var. murrayana). In contemporary fires, only 5% of the ecoregion burned in 30 years, and stand-replacing fire occurred primarily in ponderosa (Pinus ponderosa) and mixed-conifer. Historically, density of conifers > 15 cm dbh exceeded 120 trees/ha on < 5% of the area compared to 95% currently. CONCLUSIONS: Frequent, large, low-severity fires historically maintained open-canopy ponderosa and mixed-conifer forests in which large fire- and drought-tolerant trees were prevalent. Stand-replacing patches in ponderosa and mixed-conifer were rare, even in fires > 40,469 ha (minimum size of contemporary “megafires”) during extreme drought. In this frequent-fire landscape, mixed-severity fire historically influenced lodgepole and adjacent forests. Lack of large, frequent, low-severity fires degrades contemporary forest ecosystems.
Author Merschel, Andrew G.
Reilly, Matthew J.
Hagmann, R. Keala
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  givenname: Matthew J.
  surname: Reilly
  fullname: Reilly, Matthew J.
  organization: Department of Biological Sciences, Humboldt State University
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Keywords Landscape patterns of fire severity
Dry forest restoration
Megafire
Ponderosa pine
Stand-replacing fire
Lodgepole pine
Language English
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Patterson JE (1929) Pandora moth, a periodic pest of western pine forests. USDA Technical Bulletin No. 137, Washington, D.C., USA
ReillyMDunnCMeigsGSpiesTKennedyRBaileyJBriggsKContemporary patterns of fire extent and severity in forests of the Pacific Northwest, USA (1985–2010)Ecosphere20178e01695
Reynolds RT, Sánchez Meador AJ, Youtz JA, Nicolet T, Matonis MS, Jackson PL, DeLorenzo DG, Graves AD (2013) Restoring composition and structure in Southwestern frequent-fire forests: a science-based framework for improving ecosystem resiliency. RMRS-GTR-310. USDA Forest Service, Rocky Mountain Research Station, Fort Collins, CO, p 76
LevineCRCogbillCVCollinsBMLarsonAJLutzJANorthMPRestainoCMSaffordHDStephensSLBattlesJJEvaluating a new method for reconstructing forest conditions from General Land Office survey recordsEcol Appl2017271498151328370925
MerschelAGVoraRSSpiesTAConserving dry old-growth forest in Central Oregon, USAJ For201910.1093/jofore/fvy085
NorthMPStevensJTGreeneDFCoppolettaMKnappEELatimerAMRestainoCMTompkinsREWelchKRYorkRATamm review: reforestation for resilience in dry western US forestsFor Ecol Manage2019432209224
OmernikJMGriffithGEEcoregions of the conterminous United States: evolution of a hierarchical spatial frameworkEnviron Manage2014541249126625223620
Miller JM, Keen FP (1960) Biology and control of the western pine beetle: a summary of the first fifty years of research. No. 800. US Department of Agriculture
StephensSLCollinsBMFettigCJFinneyMAHoffmanCMKnappEENorthMPSaffordHWaymanRBDrought, tree mortality, and wildfire in forests adapted to frequent fireBioscience2018687788
MarlonJRBartleinPJGavinDGLongCJAndersonRSBrilesCEBrownKJColombaroliDHallettDJPowerMJLong-term perspective on wildfires in the western USAProc Natl Acad Sci USA2012109E535E5431:CAS:528:DC%2BC38XksVyhu7g%3D22334650
NorthMManaging Sierra Nevada forests. PSW-GTR-2372012AlbanyUSDA Forest Service, Pacific Southwest Research Station184
Bright GA (1912) A study of the growth of yellow pine in Oregon. Unpublished typescript report obtained from the National Archives, College Park, MD; record group 95. U.S. Department of Agriculture, Forest Service, p 106. http://fs.usda.gov/detail/umatilla/learning/history-culture
OhmannJLGregoryMJRobertsHMScale considerations for integrating forest inventory plot data and satellite image data for regional forest mappingRemote Sens Environ2014151315
Geist JM, Cochran PH (1991) Influences of volcanic ash and pumice deposition on productivity of western interior forest soils. In: Harvey AE, Neuenschwander LF (eds) Proceedings: management and productivity of western-montane forest soils, 10–12 April 1990, Boise, ID. USDA For. Serv. Gen. Tech. Rep. INT-280, Ogden, UT. pp. 82–89
Bork JL (1984) Fire history in three vegetation types on the eastern side of the Oregon Cascades. Ph.D. diss,. Oregon State University, Corvallis
WesterlingALIncreasing western US forest wildfire activity: sensitivity to changes in the timing of springPhilos Trans R Soc Lond B201610.1098/rstb.2015.0178
NorthMPStephensSLCollinsBMAgeeJKApletGFranklinJFFulePZReform forest fire managementScience2015349128012811:CAS:528:DC%2BC2MXhs1SrsLzI26383934
MerschelAGHeyerdahlEKSpiesTALoehmanRAInfluence of landscape structure, topography, and forest type on spatial variation in historical fire regimes, Central OregonUSA. Landscape Ecol2018337119511209
CarlsonGTSoil resource inventory: Winema National Forest1979Pacific Northwest RegionUSDA Forest Service
HolmesRLProgram COFECHA User’s Manual1983TucsonLaboratory of Tree-Ring Research, The University of Arizona
DeurD“A caretaker responsibility”: revisiting Klamath and Modoc traditions of plant community managementJ Ethnobiol200929296322
JohnstonJDBaileyJDDunnCJLindsayAAHistorical fire-climate relationships in contrasting interior Pacific Northwest forest typesFire Ecol2017131836
HeyerdahlEKLoehmanRAFalkDAMixed-severity fire in lodgepole pine dominated forests: are historical regimes sustainable on Oregon’s Pumice Plateau, USA?Can J For Res201444593603
HagmannRKStevensJTLydersenJMCollinsBMBattlesJJHessburgPFLevineCRMerschelAGStephensSLTaylorAHFranklinJFJohnsonDLJohnsonKNImproving the use of early timber inventories in reconstructing historical dry forests and fire in the western United StatesEcosphere20189e02232
Elliott FA (1914) State Board of Forestry Map of the State of Oregon, compiled by Theodore Rowland under the direction of F.A. Elliott, State Forester
StephensSLCollinsBMBiberEFuléPZUS federal fire and forest policy: emphasizing resilience in dry forestsEcosphere201610.1002/ecs2.1584
HessburgPFChurchillDJLarsonAJHaugoRDMillerCSpiesTANorthMPPovakNABeloteRTSingletonPHRestoring fire-prone Inland Pacific landscapes: seven core principlesLandscape Ecol20153018051835
StuartJDAgeeJKGaraRILodgepole pine regeneration in an old, self-perpetuating forest in south central OregonCan J For Res19891910961104
CowlinRWBrieglebPAMoravetsFLForest resources of the ponderosa pine region of Washington and Oregon1942Washington, DCUSDA Forest Service
JamesDGSeymourLJamesTSPopulation biology and behavior of the imperiled Philotiella leona (Lycaenidae) in South Central OregonJ Lepid Soc201468264273
Spies TA, Hessburg PF, Skinner CN, Puettmann, KJ, Reilly, MJ, Davis, RJ, Kertis, JA, Long, JW, Shaw, DC (2018) Chapter 3: Old growth, disturbance, forest succession, and management in the area of the Northwest Forest Plan. In: Spies TA, Stine PA, Gravenmier R, Long JW, Reilly MJ, tech. coords. (eds) Synthesis of science to inform land management within the Northwest Forest Plan area. PNW-GTR-966. USDA Forest Service, Pacific Northwest Research Station, Portland, OR. In: Anonymous, pp 95–243
Safford HD, Stevens JT (2017) Natural Range of Variation (NRV) for yellow pine and mixed conifer forests in the Sierra Nevada, southern Cascades, and Modoc and Inyo National Forests, California, USA. USDA Forest Service, Pacific Southwest Research Station. PSW-GTR-256, Albany, CA
LittellJSMcKenzieDWanHYCushmanSAClimate change and future wildfire in the Western United States: an ecological approach to nonstationarityEarth’s Future2018610971111
Palmer WC (1965) Meteorological Drought. Research Paper No. 45. Washington, DC: US Department of Commerce. Weather Bureau
EidenshinkJSchwindBBrewerKZhuZQuayleBHowardSA project for monitoring trends in burn severityFire Ecol20073321
ArnoSFSneckKMA method for determining fire history in coniferous forests of the mountain west1977OgdenIntermountain Forest and Range Experiment Station, USDA Forest Service
Harrington CA, comp (2003) The 1930s survey of forest resources in Washington and Oregon. Gen. Tech. Rep. PNW-GTR
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Snippet Context Lack of quantitative observations of extent, frequency, and severity of large historical fires constrains awareness of departure of contemporary...
ContextLack of quantitative observations of extent, frequency, and severity of large historical fires constrains awareness of departure of contemporary...
CONTEXT: Lack of quantitative observations of extent, frequency, and severity of large historical fires constrains awareness of departure of contemporary...
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SubjectTerms Biomedical and Life Sciences
Composition
Coniferous forests
Coniferous trees
Conifers
dendroclimatology
Drought
Drought resistance
drought tolerance
Dry forests
Ecology
ecoregions
Environmental Management
Extreme drought
fire frequency
fire severity
fire spread
Fires
Forest ecosystems
Forest fires
Forests
inventories
Landscape
Landscape Ecology
Landscape/Regional and Urban Planning
landscapes
Life Sciences
Mixed forests
Nature Conservation
Oregon
Pine trees
Pinus contorta
Pinus ponderosa
Pumice
Remote sensing
Research Article
Rotation
Sustainable Development
Terrestrial ecosystems
Timber inventory
Tree rings
Trees
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Title Historical patterns of fire severity and forest structure and composition in a landscape structured by frequent large fires: Pumice Plateau ecoregion, Oregon, USA
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