Quercus suber L. Fire Responses According to Tree Characteristics and Fire Intensity in NE Spain
Autor(a) principal: | |
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Data de Publicação: | 2019 |
Outros Autores: | , , , |
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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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) instacron:ICMBIO |
instname_str |
Instituto Chico Mendes de Conservação da Biodiversidade (ICMBIO) |
instacron_str |
ICMBIO |
institution |
ICMBIO |
reponame_str |
Biodiversidade Brasileira |
collection |
Biodiversidade Brasileira |
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 |
_version_ |
1797042390954934272 |