How does Drought Impact Burned Area in Mediterranean Vegetation Communities?

Detalhes bibliográficos
Autor(a) principal: Molina-Terrén, Domingo Miguel
Data de Publicação: 2019
Outros Autores: Cardil-Forradellas, Adrian, Vega-García, Cristina, Ascoli, Davide, Silva, Carlos Alberto, Rodrigues, Marcos
Tipo de documento: Artigo
Idioma: eng
Título da fonte: Biodiversidade Brasileira
Texto Completo: https://revistaeletronica.icmbio.gov.br/BioBR/article/view/939
Resumo: Rigorous droughts cause defoliation and mortality incidents aggregating dead fuel load. In this study, we enlarge the temporal and spatial scale of investigation on how does drought influence burned area in Mediterranean vegetation communities (VCs). This work was conducted in Northeast Spain under pine stands, grasslands, woodlands, semi-deciduous scrub, and evergreen sclerophyllous-leaved shrublands. We considered wildfire perimeters burning over 10 ha (n= 592) in the period 1998-2015. 592 fires were analyzed that burned a total 173,720 ha. We addressed this research questions: (1) How does antecedent drought duration and intensity affect fire activity in these VCs? (2) How VCs interact with drought to influence burned area? (3) Are the relationships among drought, VCs and burned area stationary throughout the year? To this end, we analyzed drought versus burned area by means of multivariate factor analysis and non-parametric regression in specific plant communities through the weekly Standardized Precipitation Evapotranspiration Index. This investigation adds to better comprehend fire-drought relations mediated by VC, under a climate change. Our key outcomes were: (1) Although Pinus halepensis forests and shrublands covered 45% of the VCs area, the percentage of burned area in both VCs was 69.7% (higher than their sizes justified); (2) The highest occurrence of forest fires and the largest burned area happened under drought anomaly situations (stronger drought than the typical for those dates); (3) Drought anomalies effects were more significant in June and September than in July and August (the driest months). This is doubtless because in July and August fuels are fully available to burn.
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spelling How does Drought Impact Burned Area in Mediterranean Vegetation Communities? How does Drought Impact Burned Area in Mediterranean Vegetation Communities? Rigorous droughts cause defoliation and mortality incidents aggregating dead fuel load. In this study, we enlarge the temporal and spatial scale of investigation on how does drought influence burned area in Mediterranean vegetation communities (VCs). This work was conducted in Northeast Spain under pine stands, grasslands, woodlands, semi-deciduous scrub, and evergreen sclerophyllous-leaved shrublands. We considered wildfire perimeters burning over 10 ha (n= 592) in the period 1998-2015. 592 fires were analyzed that burned a total 173,720 ha. We addressed this research questions: (1) How does antecedent drought duration and intensity affect fire activity in these VCs? (2) How VCs interact with drought to influence burned area? (3) Are the relationships among drought, VCs and burned area stationary throughout the year? To this end, we analyzed drought versus burned area by means of multivariate factor analysis and non-parametric regression in specific plant communities through the weekly Standardized Precipitation Evapotranspiration Index. This investigation adds to better comprehend fire-drought relations mediated by VC, under a climate change. Our key outcomes were: (1) Although Pinus halepensis forests and shrublands covered 45% of the VCs area, the percentage of burned area in both VCs was 69.7% (higher than their sizes justified); (2) The highest occurrence of forest fires and the largest burned area happened under drought anomaly situations (stronger drought than the typical for those dates); (3) Drought anomalies effects were more significant in June and September than in July and August (the driest months). This is doubtless because in July and August fuels are fully available to burn. Rigorous droughts cause defoliation and mortality incidents aggregating dead fuel load. In this study, we enlarge the temporal and spatial scale of investigation on how does drought influence burned area in Mediterranean vegetation communities (VCs). This work was conducted in Northeast Spain under pine stands, grasslands, woodlands, semi-deciduous scrub, and evergreen sclerophyllous-leaved shrublands. We considered wildfire perimeters burning over 10 ha (n= 592) in the period 1998-2015. 592 fires were analyzed that burned a total 173,720 ha. We addressed this research questions: (1) How does antecedent drought duration and intensity affect fire activity in these VCs? (2) How VCs interact with drought to influence burned area? (3) Are the relationships among drought, VCs and burned area stationary throughout the year? To this end, we analyzed drought versus burned area by means of multivariate factor analysis and non-parametric regression in specific plant communities through the weekly Standardized Precipitation Evapotranspiration Index. This investigation adds to better comprehend fire-drought relations mediated by VC, under a climate change. Our key outcomes were: (1) Although Pinus halepensis forests and shrublands covered 45% of the VCs area, the percentage of burned area in both VCs was 69.7% (higher than their sizes justified); (2) The highest occurrence of forest fires and the largest burned area happened under drought anomaly situations (stronger drought than the typical for those dates); (3) Drought anomalies effects were more significant in June and September than in July and August (the driest months). This is doubtless because in July and August fuels are fully available to burn.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/93910.37002/biodiversidadebrasileira.v9i1.939Biodiversidade Brasileira ; v. 9 n. 1 (2019): Wildfire Conference: Resumos; 115Biodiversidade Brasileira ; Vol. 9 No. 1 (2019): Wildfire Conference: Resumos; 115Biodiversidade Brasileira ; Vol. 9 Núm. 1 (2019): Wildfire Conference: Resumos; 1152236-288610.37002/biodiversidadebrasileira.v9i1reponame:Biodiversidade Brasileirainstname:Instituto Chico Mendes de Conservação da Biodiversidade (ICMBIO)instacron:ICMBIOenghttps://revistaeletronica.icmbio.gov.br/BioBR/article/view/939/760Copyright (c) 2021 Biodiversidade Brasileira - BioBrasilhttps://creativecommons.org/licenses/by-nc-nd/4.0info:eu-repo/semantics/openAccessMolina-Terrén, Domingo MiguelCardil-Forradellas, AdrianVega-García, CristinaAscoli, DavideSilva, Carlos AlbertoRodrigues, Marcos2023-05-09T12:56:02Zoai:revistaeletronica.icmbio.gov.br:article/939Revistahttps://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 How does Drought Impact Burned Area in Mediterranean Vegetation Communities?
How does Drought Impact Burned Area in Mediterranean Vegetation Communities?
title How does Drought Impact Burned Area in Mediterranean Vegetation Communities?
spellingShingle How does Drought Impact Burned Area in Mediterranean Vegetation Communities?
Molina-Terrén, Domingo Miguel
title_short How does Drought Impact Burned Area in Mediterranean Vegetation Communities?
title_full How does Drought Impact Burned Area in Mediterranean Vegetation Communities?
title_fullStr How does Drought Impact Burned Area in Mediterranean Vegetation Communities?
title_full_unstemmed How does Drought Impact Burned Area in Mediterranean Vegetation Communities?
title_sort How does Drought Impact Burned Area in Mediterranean Vegetation Communities?
author Molina-Terrén, Domingo Miguel
author_facet Molina-Terrén, Domingo Miguel
Cardil-Forradellas, Adrian
Vega-García, Cristina
Ascoli, Davide
Silva, Carlos Alberto
Rodrigues, Marcos
author_role author
author2 Cardil-Forradellas, Adrian
Vega-García, Cristina
Ascoli, Davide
Silva, Carlos Alberto
Rodrigues, Marcos
author2_role author
author
author
author
author
dc.contributor.author.fl_str_mv Molina-Terrén, Domingo Miguel
Cardil-Forradellas, Adrian
Vega-García, Cristina
Ascoli, Davide
Silva, Carlos Alberto
Rodrigues, Marcos
description Rigorous droughts cause defoliation and mortality incidents aggregating dead fuel load. In this study, we enlarge the temporal and spatial scale of investigation on how does drought influence burned area in Mediterranean vegetation communities (VCs). This work was conducted in Northeast Spain under pine stands, grasslands, woodlands, semi-deciduous scrub, and evergreen sclerophyllous-leaved shrublands. We considered wildfire perimeters burning over 10 ha (n= 592) in the period 1998-2015. 592 fires were analyzed that burned a total 173,720 ha. We addressed this research questions: (1) How does antecedent drought duration and intensity affect fire activity in these VCs? (2) How VCs interact with drought to influence burned area? (3) Are the relationships among drought, VCs and burned area stationary throughout the year? To this end, we analyzed drought versus burned area by means of multivariate factor analysis and non-parametric regression in specific plant communities through the weekly Standardized Precipitation Evapotranspiration Index. This investigation adds to better comprehend fire-drought relations mediated by VC, under a climate change. Our key outcomes were: (1) Although Pinus halepensis forests and shrublands covered 45% of the VCs area, the percentage of burned area in both VCs was 69.7% (higher than their sizes justified); (2) The highest occurrence of forest fires and the largest burned area happened under drought anomaly situations (stronger drought than the typical for those dates); (3) Drought anomalies effects were more significant in June and September than in July and August (the driest months). This is doubtless because in July and August fuels are fully available to burn.
publishDate 2019
dc.date.none.fl_str_mv 2019-11-15
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dc.identifier.uri.fl_str_mv https://revistaeletronica.icmbio.gov.br/BioBR/article/view/939
10.37002/biodiversidadebrasileira.v9i1.939
url https://revistaeletronica.icmbio.gov.br/BioBR/article/view/939
identifier_str_mv 10.37002/biodiversidadebrasileira.v9i1.939
dc.language.iso.fl_str_mv eng
language eng
dc.relation.none.fl_str_mv https://revistaeletronica.icmbio.gov.br/BioBR/article/view/939/760
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; 115
Biodiversidade Brasileira ; Vol. 9 No. 1 (2019): Wildfire Conference: Resumos; 115
Biodiversidade Brasileira ; Vol. 9 Núm. 1 (2019): Wildfire Conference: Resumos; 115
2236-2886
10.37002/biodiversidadebrasileira.v9i1
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