Quercus suber L. Fire Responses According to Tree Characteristics and Fire Intensity in NE Spain

Detalhes bibliográficos
Autor(a) principal: Molina-Terrén, Domingo Miguel
Data de Publicação: 2019
Outros Autores: Arteaga, Carles, Cardil, Adrian, Nebot, Edgar, Castellnou, Marc
Tipo de documento: Artigo
Idioma: eng
Título da fonte: Biodiversidade Brasileira
Texto Completo: https://revistaeletronica.icmbio.gov.br/BioBR/article/view/940
Resumo: Quercus suber L (QS) resprouts as a key response to fire disturbance. It is well known that the development of a thick bark, that performs a thermal insulation, is a remarkable adaptation of QS to wildland fires. We studied fire effects in QS in NE Spain. We search for what is the diameter size that ensures individuals survive and recover crown size in less than two years. Sampling was performed in 2012 in an area that offered different levels of fire behavior (i.e., low intensity and high intensity as reported by forest firefighters). Trees with old (older than 2006), major fire scars were rejected since they did not allow us to infer the fire effect from the 2006 fire properly. 240 individuals were classified into three groups: “Dead”, “BB” (lost the crown foliage but resprouting from basal buds); and “KC” (those keeping crown foliage because either not very much damaged by fire or able to sprout from most branches; i.e., stem buds). Results show that, under low intensity fires (surface fire), tree mortality is zero for trees in diameter classes (DC) above 15cm and 16% in the DC=5 & 10cm. Additionally, more than 60% in these classes (DC=5 & 10cm) do resprout from stem buds (very fast crown recovery), 93% in DC=15, and 100% in DC=20 and over. Under high intensity (crown fire), the damage is more evident and mortalities are 79% (DC=5cm), 32% (DC=10), and 8.6% (all above DC=10). The thinner individuals (DC=5cm) were mostly unable to resprout from stem buds (only 6.9% did so), although resprouted from basal buds (13.8%). Resprouting from the crown (stem buds) increased as DC increased. The effect of surface fires is minor in productive classes (i.e., DC>20cm) when addressing survival, although bark damages imply an economic loss. Therefore, a managed understory (i.e., low fuel load) has limited or zero tree mortality under an eventual fire. When highintensity fire occurs, under frequent fire recurrence, the cork oak presence will tend to disappear due to the mortality of oak juveniles (small DCs), being replaced by a scrubland..
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spelling Quercus suber L. Fire Responses According to Tree Characteristics and Fire Intensity in NE SpainQuercus Suber L. Fire Responses According to Tree Characteristics and Fire Intensity in NE SpainQuercus suber L (QS) resprouts as a key response to fire disturbance. It is well known that the development of a thick bark, that performs a thermal insulation, is a remarkable adaptation of QS to wildland fires. We studied fire effects in QS in NE Spain. We search for what is the diameter size that ensures individuals survive and recover crown size in less than two years. Sampling was performed in 2012 in an area that offered different levels of fire behavior (i.e., low intensity and high intensity as reported by forest firefighters). Trees with old (older than 2006), major fire scars were rejected since they did not allow us to infer the fire effect from the 2006 fire properly. 240 individuals were classified into three groups: “Dead”, “BB” (lost the crown foliage but resprouting from basal buds); and “KC” (those keeping crown foliage because either not very much damaged by fire or able to sprout from most branches; i.e., stem buds). Results show that, under low intensity fires (surface fire), tree mortality is zero for trees in diameter classes (DC) above 15cm and 16% in the DC=5 & 10cm. Additionally, more than 60% in these classes (DC=5 & 10cm) do resprout from stem buds (very fast crown recovery), 93% in DC=15, and 100% in DC=20 and over. Under high intensity (crown fire), the damage is more evident and mortalities are 79% (DC=5cm), 32% (DC=10), and 8.6% (all above DC=10). The thinner individuals (DC=5cm) were mostly unable to resprout from stem buds (only 6.9% did so), although resprouted from basal buds (13.8%). Resprouting from the crown (stem buds) increased as DC increased. The effect of surface fires is minor in productive classes (i.e., DC>20cm) when addressing survival, although bark damages imply an economic loss. Therefore, a managed understory (i.e., low fuel load) has limited or zero tree mortality under an eventual fire. When highintensity fire occurs, under frequent fire recurrence, the cork oak presence will tend to disappear due to the mortality of oak juveniles (small DCs), being replaced by a scrubland..Quercus suber L (QS) resprouts as a key response to fire disturbance. It is well known that the development of a thick bark, that performs a thermal insulation, is a remarkable adaptation of QS to wildland fires. We studied fire effects in QS in NE Spain. We search for what is the diameter size that ensures individuals survive and recover crown size in less than two years. Sampling was performed in 2012 in an area that offered different levels of fire behavior (i.e., low intensity and high intensity as reported by forest firefighters). Trees with old (older than 2006), major fire scars were rejected since they did not allow us to infer the fire effect from the 2006 fire properly. 240 individuals were classified into three groups: “Dead”, “BB” (lost the crown foliage but resprouting from basal buds); and “KC” (those keeping crown foliage because either not very much damaged by fire or able to sprout from most branches; i.e., stem buds). Results show that, under low intensity fires (surface fire), tree mortality is zero for trees in diameter classes (DC) above 15cm and 16% in the DC=5 & 10cm. Additionally, more than 60% in these classes (DC=5 & 10cm) do resprout from stem buds (very fast crown recovery), 93% in DC=15, and 100% in DC=20 and over. Under high intensity (crown fire), the damage is more evident and mortalities are 79% (DC=5cm), 32% (DC=10), and 8.6% (all above DC=10). The thinner individuals (DC=5cm) were mostly unable to resprout from stem buds (only 6.9% did so), although resprouted from basal buds (13.8%). Resprouting from the crown (stem buds) increased as DC increased. The effect of surface fires is minor in productive classes (i.e., DC>20cm) when addressing survival, although bark damages imply an economic loss. Therefore, a managed understory (i.e., low fuel load) has limited or zero tree mortality under an eventual fire. When highintensity fire occurs, under frequent fire recurrence, the cork oak presence will tend to disappear due to the mortality of oak juveniles (small DCs), being replaced by a scrubland..Instituto Chico Mendes de Conservação da Biodiversidade (ICMBio)2019-11-15info:eu-repo/semantics/articleinfo:eu-repo/semantics/publishedVersionapplication/pdfhttps://revistaeletronica.icmbio.gov.br/BioBR/article/view/94010.37002/biodiversidadebrasileira.v9i1.940Biodiversidade Brasileira ; v. 9 n. 1 (2019): Wildfire Conference: Resumos; 62Biodiversidade Brasileira ; Vol. 9 No. 1 (2019): Wildfire Conference: Resumos; 62Biodiversidade Brasileira ; Vol. 9 Núm. 1 (2019): Wildfire Conference: Resumos; 622236-288610.37002/biodiversidadebrasileira.v9i1reponame:Biodiversidade Brasileirainstname:Instituto Chico Mendes de Conservação da Biodiversidade (ICMBIO)instacron:ICMBIOenghttps://revistaeletronica.icmbio.gov.br/BioBR/article/view/940/707Copyright (c) 2021 Biodiversidade Brasileira - BioBrasilhttps://creativecommons.org/licenses/by-nc-nd/4.0info:eu-repo/semantics/openAccessMolina-Terrén, Domingo MiguelArteaga, CarlesCardil, AdrianNebot, EdgarCastellnou, Marc2023-05-09T12:56:02Zoai:revistaeletronica.icmbio.gov.br:article/940Revistahttps://revistaeletronica.icmbio.gov.br/BioBRPUBhttps://revistaeletronica.icmbio.gov.br/BioBR/oaifernanda.oliveto@icmbio.gov.br || katia.ribeiro@icmbio.gov.br2236-28862236-2886opendoar:2023-05-09T12:56:02Biodiversidade Brasileira - Instituto Chico Mendes de Conservação da Biodiversidade (ICMBIO)false
dc.title.none.fl_str_mv Quercus suber L. Fire Responses According to Tree Characteristics and Fire Intensity in NE Spain
Quercus Suber L. Fire Responses According to Tree Characteristics and Fire Intensity in NE Spain
title Quercus suber L. Fire Responses According to Tree Characteristics and Fire Intensity in NE Spain
spellingShingle Quercus suber L. Fire Responses According to Tree Characteristics and Fire Intensity in NE Spain
Molina-Terrén, Domingo Miguel
title_short Quercus suber L. Fire Responses According to Tree Characteristics and Fire Intensity in NE Spain
title_full Quercus suber L. Fire Responses According to Tree Characteristics and Fire Intensity in NE Spain
title_fullStr Quercus suber L. Fire Responses According to Tree Characteristics and Fire Intensity in NE Spain
title_full_unstemmed Quercus suber L. Fire Responses According to Tree Characteristics and Fire Intensity in NE Spain
title_sort Quercus suber L. Fire Responses According to Tree Characteristics and Fire Intensity in NE Spain
author Molina-Terrén, Domingo Miguel
author_facet Molina-Terrén, Domingo Miguel
Arteaga, Carles
Cardil, Adrian
Nebot, Edgar
Castellnou, Marc
author_role author
author2 Arteaga, Carles
Cardil, Adrian
Nebot, Edgar
Castellnou, Marc
author2_role author
author
author
author
dc.contributor.author.fl_str_mv Molina-Terrén, Domingo Miguel
Arteaga, Carles
Cardil, Adrian
Nebot, Edgar
Castellnou, Marc
description Quercus suber L (QS) resprouts as a key response to fire disturbance. It is well known that the development of a thick bark, that performs a thermal insulation, is a remarkable adaptation of QS to wildland fires. We studied fire effects in QS in NE Spain. We search for what is the diameter size that ensures individuals survive and recover crown size in less than two years. Sampling was performed in 2012 in an area that offered different levels of fire behavior (i.e., low intensity and high intensity as reported by forest firefighters). Trees with old (older than 2006), major fire scars were rejected since they did not allow us to infer the fire effect from the 2006 fire properly. 240 individuals were classified into three groups: “Dead”, “BB” (lost the crown foliage but resprouting from basal buds); and “KC” (those keeping crown foliage because either not very much damaged by fire or able to sprout from most branches; i.e., stem buds). Results show that, under low intensity fires (surface fire), tree mortality is zero for trees in diameter classes (DC) above 15cm and 16% in the DC=5 & 10cm. Additionally, more than 60% in these classes (DC=5 & 10cm) do resprout from stem buds (very fast crown recovery), 93% in DC=15, and 100% in DC=20 and over. Under high intensity (crown fire), the damage is more evident and mortalities are 79% (DC=5cm), 32% (DC=10), and 8.6% (all above DC=10). The thinner individuals (DC=5cm) were mostly unable to resprout from stem buds (only 6.9% did so), although resprouted from basal buds (13.8%). Resprouting from the crown (stem buds) increased as DC increased. The effect of surface fires is minor in productive classes (i.e., DC>20cm) when addressing survival, although bark damages imply an economic loss. Therefore, a managed understory (i.e., low fuel load) has limited or zero tree mortality under an eventual fire. When highintensity fire occurs, under frequent fire recurrence, the cork oak presence will tend to disappear due to the mortality of oak juveniles (small DCs), being replaced by a scrubland..
publishDate 2019
dc.date.none.fl_str_mv 2019-11-15
dc.type.driver.fl_str_mv info:eu-repo/semantics/article
info:eu-repo/semantics/publishedVersion
format article
status_str publishedVersion
dc.identifier.uri.fl_str_mv https://revistaeletronica.icmbio.gov.br/BioBR/article/view/940
10.37002/biodiversidadebrasileira.v9i1.940
url https://revistaeletronica.icmbio.gov.br/BioBR/article/view/940
identifier_str_mv 10.37002/biodiversidadebrasileira.v9i1.940
dc.language.iso.fl_str_mv eng
language eng
dc.relation.none.fl_str_mv https://revistaeletronica.icmbio.gov.br/BioBR/article/view/940/707
dc.rights.driver.fl_str_mv Copyright (c) 2021 Biodiversidade Brasileira - BioBrasil
https://creativecommons.org/licenses/by-nc-nd/4.0
info:eu-repo/semantics/openAccess
rights_invalid_str_mv Copyright (c) 2021 Biodiversidade Brasileira - BioBrasil
https://creativecommons.org/licenses/by-nc-nd/4.0
eu_rights_str_mv openAccess
dc.format.none.fl_str_mv application/pdf
dc.publisher.none.fl_str_mv Instituto Chico Mendes de Conservação da Biodiversidade (ICMBio)
publisher.none.fl_str_mv Instituto Chico Mendes de Conservação da Biodiversidade (ICMBio)
dc.source.none.fl_str_mv Biodiversidade Brasileira ; v. 9 n. 1 (2019): Wildfire Conference: Resumos; 62
Biodiversidade Brasileira ; Vol. 9 No. 1 (2019): Wildfire Conference: Resumos; 62
Biodiversidade Brasileira ; Vol. 9 Núm. 1 (2019): Wildfire Conference: Resumos; 62
2236-2886
10.37002/biodiversidadebrasileira.v9i1
reponame:Biodiversidade Brasileira
instname:Instituto Chico Mendes de Conservação da Biodiversidade (ICMBIO)
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repository.name.fl_str_mv Biodiversidade Brasileira - Instituto Chico Mendes de Conservação da Biodiversidade (ICMBIO)
repository.mail.fl_str_mv fernanda.oliveto@icmbio.gov.br || katia.ribeiro@icmbio.gov.br
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