Do Fire Retardants Affect the Recovery of the Fine Fuel of the Herbaceous Layer of an Open Savanna? A Case Study

Detalhes bibliográficos
Autor(a) principal: Cardoso Silva, Henrique
Data de Publicação: 2019
Outros Autores: Franco Rosa, Daniela, Barbosa Dantas Junior, Ademar, Musso, Carolina, Ferreira Sanchez, Luiz Gustavo, Henke Oliveira, Carlos, Sinatora Miranda, Heloisa
Tipo de documento: Artigo
Idioma: por
Título da fonte: Biodiversidade Brasileira
Texto Completo: https://revistaeletronica.icmbio.gov.br/BioBR/article/view/1064
Resumo: Wildfires burning large areas represent harm to human health, environment and the economy. Therefore, more efficient fire combat techniques are needed. The fire retardants are chemical products useful to reduce fire intensity helping in fire combat. The objective of this work was to investigate the recovery of the fine fuel of the herbaceous layer after a fire in areas with the use of fire retardants. The experiment took place in an area of open savanna, 35 km Southeast of Brasília (DF), burned one year before our experiment. In this area, eight plots (10 x 30 m) were selected to apply fire retardants (R). In the first two plots, R1 was applied, in the second two R2, and the remaining plots were used as control (C). The plots were burned independently in September 2018, the onset of the rainy season (53.2 mm before the burn). In each plot, monthly, five samples (0.25 m²) of aboveground biomass were randomly harvested. The fuel was sorted in dicots (D), graminoids (G) and palm leaves (P). The dry mass was estimated after drying (~60ºC) for 48h. Wilcoxon test (p<0.05) was used to compare the recovery of G, D and P biomass between September (before fire) and February for treated and untreated plots separately. Regarding the total biomass (T) in February, a Kruskal-Wallis test was used to compare R1, R2 and C for D, G and P. A two-way ANOVA was used to compare T among plots (R1, R2, C) and between September and February. Before the fire, T in C (T=0.33±0.03 kg/m2; G=0.13±0.01 kg/m2; D=0.12±0.04 kg/m2; P=0.07±0.06 kg/m2) was similar to R1 (T=0.53±0.06 kg/m2; G=0.24±0.06 kg/m2; D=0.23±0.05 kg/m2; P=0.06±0.06 kg/m2) and R2 (T=0.17±0.10 kg/m2; G=0.26±0.04 kg/m2; D=0.20±0.07 kg/m2; P=0.06±0.02 kg/m2). In February 2019, there was no significant differences for T, G, D, P with pre-fire values for R1 (T=0.60±0.06 kg/m2; G=0.23±0.02 kg/m2; D=0.30±0.01 kg/m2; P=0.06±0.05 kg/m2) and R2 (T=0.50±0.15 kg/m2; D=0.14±0.02 kg/m2; G=0.32±0.19 kg/m2; P=0.02±0.01 kg/m2), suggesting that R1 and R2 didn’t impair the recovery of the fine fuel in the burned plots. (FAPDF/0193.001387/2016; CNPq/442722/2018-4; Comando da Área Alfa (DF) da Marinha do Brasil) >.
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spelling Do Fire Retardants Affect the Recovery of the Fine Fuel of the Herbaceous Layer of an Open Savanna? A Case StudyDo Fire Retardants Affect the Recovery of the Fine Fuel of the Herbaceous Layer of an Open Savanna? A Case StudyDo Fire Retardants Affect the Recovery of the Fine Fuel of the Herbaceous Layer of an Open Savanna? A Case StudyWildfires burning large areas represent harm to human health, environment and the economy. Therefore, more efficient fire combat techniques are needed. The fire retardants are chemical products useful to reduce fire intensity helping in fire combat. The objective of this work was to investigate the recovery of the fine fuel of the herbaceous layer after a fire in areas with the use of fire retardants. The experiment took place in an area of open savanna, 35 km Southeast of Brasília (DF), burned one year before our experiment. In this area, eight plots (10 x 30 m) were selected to apply fire retardants (R). In the first two plots, R1 was applied, in the second two R2, and the remaining plots were used as control (C). The plots were burned independently in September 2018, the onset of the rainy season (53.2 mm before the burn). In each plot, monthly, five samples (0.25 m²) of aboveground biomass were randomly harvested. The fuel was sorted in dicots (D), graminoids (G) and palm leaves (P). The dry mass was estimated after drying (~60ºC) for 48h. Wilcoxon test (p<0.05) was used to compare the recovery of G, D and P biomass between September (before fire) and February for treated and untreated plots separately. Regarding the total biomass (T) in February, a Kruskal-Wallis test was used to compare R1, R2 and C for D, G and P. A two-way ANOVA was used to compare T among plots (R1, R2, C) and between September and February. Before the fire, T in C (T=0.33±0.03 kg/m2; G=0.13±0.01 kg/m2; D=0.12±0.04 kg/m2; P=0.07±0.06 kg/m2) was similar to R1 (T=0.53±0.06 kg/m2; G=0.24±0.06 kg/m2; D=0.23±0.05 kg/m2; P=0.06±0.06 kg/m2) and R2 (T=0.17±0.10 kg/m2; G=0.26±0.04 kg/m2; D=0.20±0.07 kg/m2; P=0.06±0.02 kg/m2). In February 2019, there was no significant differences for T, G, D, P with pre-fire values for R1 (T=0.60±0.06 kg/m2; G=0.23±0.02 kg/m2; D=0.30±0.01 kg/m2; P=0.06±0.05 kg/m2) and R2 (T=0.50±0.15 kg/m2; D=0.14±0.02 kg/m2; G=0.32±0.19 kg/m2; P=0.02±0.01 kg/m2), suggesting that R1 and R2 didn’t impair the recovery of the fine fuel in the burned plots. (FAPDF/0193.001387/2016; CNPq/442722/2018-4; Comando da Área Alfa (DF) da Marinha do Brasil) >.Wildfires burning large areas represent harm to human health, environment and the economy. Therefore, more efficient fire combat techniques are needed. The fire retardants are chemical products useful to reduce fire intensity helping in fire combat. The objective of this work was to investigate the recovery of the fine fuel of the herbaceous layer after a fire in areas with the use of fire retardants. The experiment took place in an area of open savanna, 35 km Southeast of Brasília (DF), burned one year before our experiment. In this area, eight plots (10 x 30 m) were selected to apply fire retardants (R). In the first two plots, R1 was applied, in the second two R2, and the remaining plots were used as control (C). The plots were burned independently in September 2018, the onset of the rainy season (53.2 mm before the burn). In each plot, monthly, five samples (0.25 m²) of aboveground biomass were randomly harvested. The fuel was sorted in dicots (D), graminoids (G) and palm leaves (P). The dry mass was estimated after drying (~60ºC) for 48h. Wilcoxon test (p<0.05) was used to compare the recovery of G, D and P biomass between September (before fire) and February for treated and untreated plots separately. Regarding the total biomass (T) in February, a Kruskal-Wallis test was used to compare R1, R2 and C for D, G and P. A two-way ANOVA was used to compare T among plots (R1, R2, C) and between September and February. Before the fire, T in C (T=0.33±0.03 kg/m2; G=0.13±0.01 kg/m2; D=0.12±0.04 kg/m2; P=0.07±0.06 kg/m2) was similar to R1 (T=0.53±0.06 kg/m2; G=0.24±0.06 kg/m2; D=0.23±0.05 kg/m2; P=0.06±0.06 kg/m2) and R2 (T=0.17±0.10 kg/m2; G=0.26±0.04 kg/m2; D=0.20±0.07 kg/m2; P=0.06±0.02 kg/m2). In February 2019, there was no significant differences for T, G, D, P with pre-fire values for R1 (T=0.60±0.06 kg/m2; G=0.23±0.02 kg/m2; D=0.30±0.01 kg/m2; P=0.06±0.05 kg/m2) and R2 (T=0.50±0.15 kg/m2; D=0.14±0.02 kg/m2; G=0.32±0.19 kg/m2; P=0.02±0.01 kg/m2), suggesting that R1 and R2 didn’t impair the recovery of the fine fuel in the burned plots. (FAPDF/0193.001387/2016; CNPq/442722/2018-4; Comando da Área Alfa (DF) da Marinha do Brasil) >.Wildfires burning large areas represent harm to human health, environment and the economy. Therefore, more efficient fire combat techniques are needed. The fire retardants are chemical products useful to reduce fire intensity helping in fire combat. The objective of this work was to investigate the recovery of the fine fuel of the herbaceous layer after a fire in areas with the use of fire retardants. The experiment took place in an area of open savanna, 35 km Southeast of Brasília (DF), burned one year before our experiment. In this area, eight plots (10 x 30 m) were selected to apply fire retardants (R). In the first two plots, R1 was applied, in the second two R2, and the remaining plots were used as control (C). The plots were burned independently in September 2018, the onset of the rainy season (53.2 mm before the burn). In each plot, monthly, five samples (0.25 m²) of aboveground biomass were randomly harvested. The fuel was sorted in dicots (D), graminoids (G) and palm leaves (P). The dry mass was estimated after drying (~60ºC) for 48h. Wilcoxon test (p<0.05) was used to compare the recovery of G, D and P biomass between September (before fire) and February for treated and untreated plots separately. Regarding the total biomass (T) in February, a Kruskal-Wallis test was used to compare R1, R2 and C for D, G and P. A two-way ANOVA was used to compare T among plots (R1, R2, C) and between September and February. Before the fire, T in C (T=0.33±0.03 kg/m2; G=0.13±0.01 kg/m2; D=0.12±0.04 kg/m2; P=0.07±0.06 kg/m2) was similar to R1 (T=0.53±0.06 kg/m2; G=0.24±0.06 kg/m2; D=0.23±0.05 kg/m2; P=0.06±0.06 kg/m2) and R2 (T=0.17±0.10 kg/m2; G=0.26±0.04 kg/m2; D=0.20±0.07 kg/m2; P=0.06±0.02 kg/m2). In February 2019, there was no significant differences for T, G, D, P with pre-fire values for R1 (T=0.60±0.06 kg/m2; G=0.23±0.02 kg/m2; D=0.30±0.01 kg/m2; P=0.06±0.05 kg/m2) and R2 (T=0.50±0.15 kg/m2; D=0.14±0.02 kg/m2; G=0.32±0.19 kg/m2; P=0.02±0.01 kg/m2), suggesting that R1 and R2 didn’t impair the recovery of the fine fuel in the burned plots. (FAPDF/0193.001387/2016; CNPq/442722/2018-4; Comando da Área Alfa (DF) da Marinha do Brasil) >.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/106410.37002/biodiversidadebrasileira.v9i1.1064Biodiversidade Brasileira ; v. 9 n. 1 (2019): Wildfire Conference: Resumos; 165Biodiversidade Brasileira ; Vol. 9 No. 1 (2019): Wildfire Conference: Resumos; 165Biodiversidade Brasileira ; Vol. 9 Núm. 1 (2019): Wildfire Conference: Resumos; 1652236-288610.37002/biodiversidadebrasileira.v9i1reponame:Biodiversidade Brasileirainstname:Instituto Chico Mendes de Conservação da Biodiversidade (ICMBIO)instacron:ICMBIOporhttps://revistaeletronica.icmbio.gov.br/BioBR/article/view/1064/812Copyright (c) 2021 Biodiversidade Brasileira - BioBrasilhttps://creativecommons.org/licenses/by-nc-nd/4.0info:eu-repo/semantics/openAccessCardoso Silva, HenriqueFranco Rosa, DanielaBarbosa Dantas Junior, AdemarMusso, CarolinaFerreira Sanchez, Luiz GustavoHenke Oliveira, CarlosSinatora Miranda, Heloisa2023-05-09T12:56:02Zoai:revistaeletronica.icmbio.gov.br:article/1064Revistahttps://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 Do Fire Retardants Affect the Recovery of the Fine Fuel of the Herbaceous Layer of an Open Savanna? A Case Study
Do Fire Retardants Affect the Recovery of the Fine Fuel of the Herbaceous Layer of an Open Savanna? A Case Study
Do Fire Retardants Affect the Recovery of the Fine Fuel of the Herbaceous Layer of an Open Savanna? A Case Study
title Do Fire Retardants Affect the Recovery of the Fine Fuel of the Herbaceous Layer of an Open Savanna? A Case Study
spellingShingle Do Fire Retardants Affect the Recovery of the Fine Fuel of the Herbaceous Layer of an Open Savanna? A Case Study
Cardoso Silva, Henrique
title_short Do Fire Retardants Affect the Recovery of the Fine Fuel of the Herbaceous Layer of an Open Savanna? A Case Study
title_full Do Fire Retardants Affect the Recovery of the Fine Fuel of the Herbaceous Layer of an Open Savanna? A Case Study
title_fullStr Do Fire Retardants Affect the Recovery of the Fine Fuel of the Herbaceous Layer of an Open Savanna? A Case Study
title_full_unstemmed Do Fire Retardants Affect the Recovery of the Fine Fuel of the Herbaceous Layer of an Open Savanna? A Case Study
title_sort Do Fire Retardants Affect the Recovery of the Fine Fuel of the Herbaceous Layer of an Open Savanna? A Case Study
author Cardoso Silva, Henrique
author_facet Cardoso Silva, Henrique
Franco Rosa, Daniela
Barbosa Dantas Junior, Ademar
Musso, Carolina
Ferreira Sanchez, Luiz Gustavo
Henke Oliveira, Carlos
Sinatora Miranda, Heloisa
author_role author
author2 Franco Rosa, Daniela
Barbosa Dantas Junior, Ademar
Musso, Carolina
Ferreira Sanchez, Luiz Gustavo
Henke Oliveira, Carlos
Sinatora Miranda, Heloisa
author2_role author
author
author
author
author
author
dc.contributor.author.fl_str_mv Cardoso Silva, Henrique
Franco Rosa, Daniela
Barbosa Dantas Junior, Ademar
Musso, Carolina
Ferreira Sanchez, Luiz Gustavo
Henke Oliveira, Carlos
Sinatora Miranda, Heloisa
description Wildfires burning large areas represent harm to human health, environment and the economy. Therefore, more efficient fire combat techniques are needed. The fire retardants are chemical products useful to reduce fire intensity helping in fire combat. The objective of this work was to investigate the recovery of the fine fuel of the herbaceous layer after a fire in areas with the use of fire retardants. The experiment took place in an area of open savanna, 35 km Southeast of Brasília (DF), burned one year before our experiment. In this area, eight plots (10 x 30 m) were selected to apply fire retardants (R). In the first two plots, R1 was applied, in the second two R2, and the remaining plots were used as control (C). The plots were burned independently in September 2018, the onset of the rainy season (53.2 mm before the burn). In each plot, monthly, five samples (0.25 m²) of aboveground biomass were randomly harvested. The fuel was sorted in dicots (D), graminoids (G) and palm leaves (P). The dry mass was estimated after drying (~60ºC) for 48h. Wilcoxon test (p<0.05) was used to compare the recovery of G, D and P biomass between September (before fire) and February for treated and untreated plots separately. Regarding the total biomass (T) in February, a Kruskal-Wallis test was used to compare R1, R2 and C for D, G and P. A two-way ANOVA was used to compare T among plots (R1, R2, C) and between September and February. Before the fire, T in C (T=0.33±0.03 kg/m2; G=0.13±0.01 kg/m2; D=0.12±0.04 kg/m2; P=0.07±0.06 kg/m2) was similar to R1 (T=0.53±0.06 kg/m2; G=0.24±0.06 kg/m2; D=0.23±0.05 kg/m2; P=0.06±0.06 kg/m2) and R2 (T=0.17±0.10 kg/m2; G=0.26±0.04 kg/m2; D=0.20±0.07 kg/m2; P=0.06±0.02 kg/m2). In February 2019, there was no significant differences for T, G, D, P with pre-fire values for R1 (T=0.60±0.06 kg/m2; G=0.23±0.02 kg/m2; D=0.30±0.01 kg/m2; P=0.06±0.05 kg/m2) and R2 (T=0.50±0.15 kg/m2; D=0.14±0.02 kg/m2; G=0.32±0.19 kg/m2; P=0.02±0.01 kg/m2), suggesting that R1 and R2 didn’t impair the recovery of the fine fuel in the burned plots. (FAPDF/0193.001387/2016; CNPq/442722/2018-4; Comando da Área Alfa (DF) da Marinha do Brasil) >.
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/1064
10.37002/biodiversidadebrasileira.v9i1.1064
url https://revistaeletronica.icmbio.gov.br/BioBR/article/view/1064
identifier_str_mv 10.37002/biodiversidadebrasileira.v9i1.1064
dc.language.iso.fl_str_mv por
language por
dc.relation.none.fl_str_mv https://revistaeletronica.icmbio.gov.br/BioBR/article/view/1064/812
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; 165
Biodiversidade Brasileira ; Vol. 9 No. 1 (2019): Wildfire Conference: Resumos; 165
Biodiversidade Brasileira ; Vol. 9 Núm. 1 (2019): Wildfire Conference: Resumos; 165
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
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