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| Registros recuperados : 31 | |
| 8. |  | SOUZA, J. S.; ESPÍRITO-SANTO, F. del B.; FONTES, M. A. L.; OLIVEIRA FILHO, A. T. de; BOTEZELLI, L. Análise das variações florísticas e estruturais da comunidade arbórea de um fragmento de floresta semidecídua às margens do Rio Capivari, Lavras - MG. Revista Árvore, Viçosa, v. 27, n. 2, p. 185-206, mar./abr. 2003.| Biblioteca(s): Embrapa Florestas. |
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| 9. | | ESPÍRITO-SANTO, F. D. B.; KELLER, M. M.; LINDER, E.; OLIVEIRA JUNIOR, R. C. de; PEREIRA, C.; OLIVEIRA, C. G. Gap formation and carbon cycling in the Brazilian Amazon: measurement using high-resolution optical remote sensing and studies in large forest plots. Plant Ecology & Diversity, v. 7, n. 1/2, p. 305-318, 2014.| Biblioteca(s): Embrapa Amazônia Oriental; Embrapa Territorial. |
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| 10. | | MEYER, V.; SAATCHI, S.; CLARCK, D. B.; KELLER, M.; VICENT, G.; FERRAZ, A.; ESPÍRITO-SANTO, F.; OLIVEIRA, M. V. N. d'; KAKI, D.; CHAVE, J. Canopy area of large trees explains aboveground biomass variations across neotropical forest landscapes. Biogeosciences, v. 15, n. 11, p. 3377-3390, 2018.| Biblioteca(s): Embrapa Acre. |
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| 11. | | HUNTER, M. O.; KELLER, M.; CAMARGO, P.; PALACE, M.; OLIVEIRA JUNIOR, R. C. de; ESPIRITO SANTO, F.; KEIZER, E.; LEFSKY, M.; ASNER, G. P. Forest structure at five LBA study sites. In: SCIENCE TEAM MEETING, 10., 2006, Brasília, DF. Book of Abstracts... Manaus: LBA-ECO, 2006. p. 29.| Biblioteca(s): Embrapa Amazônia Oriental. |
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| 12. | | SILVA, L. A. da; MARTINS, M. A.; ESPÍRITO SANTO, F.; OLIVEIRA, F. C.; CHAVES, F. C. M.; CHAGAS, E. C.; MARTINS, M. L.; CAMPOS, C. M. de. Essential oils of Ocimum gratissimum and Zingiber officinale as anesthetics for the South American catfish Pseudoplatystoma reticulatum. Aquaculture, art. 735595, June 2020.| Biblioteca(s): Embrapa Amazônia Ocidental. |
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| 13. | | LEFSKY, M. A.; HARDING, D. J.; KELLER, M.; COHEN, W. B.; CARABAJAL, C. C.; ESPIRITO-SANTO, F. D. B.; HUNTER, M. O.; OLIVEIRA JUNIOR, R. de. Estimates of forest canopy height and aboveground biomass using ICESat. Geophysical Research Letters, v. 32, n. 22, L22S02, Nov. 2005.| Biblioteca(s): Embrapa Amazônia Oriental. |
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| 14. | | SAATCHI, S.; MASCARO, J.; XU, L.; KELLER, M.; YANG, Y.; DUFFY, P.; ESPÍRITO-SANTO, F.; BACCINI, A.; CHAMBERS, J.; SCHIMEL, D. Seeing the forest beyond the trees. Global Ecology and Biogeography, v. 23, n. 11, p. 1-5, nov. 2014. Artigo publicado por Pesquisador Visitante da Embrapa Monitoramento por Satélite.| Biblioteca(s): Embrapa Territorial. |
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| 15. | | SMITH, C. C.; ESPÍRITO-SANTO, F. D. B.; HEALEY, J. R.; YOUNG, P. J.; LENNOX, G. D.; FERREIRA, J. N.; BARLOW, J. Secondary forests offset less than 10% of deforestation-mediated carbon emissions in the Brazilian Amazon. Global Change Biology, v. 26, n. 12, p. 7006-7020, 2020.| Biblioteca(s): Embrapa Amazônia Oriental. |
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| 16. | | GUIMARÃES, R. F.; CARVALHO JUNIOR, O. A. de; MARTINS, E. de S.; GOMES, R. A. T.; FLOSS, P. A.; ESPÍRITO SANTO, F. R. C. do; ANDRADE, A. C. de; CARVALHO, A. P. F. de. Definição de áreas para silvicultura na bacia do rio Ariranha (SC) em áreas de encosta erosionais utilizando imagens ASTER e modelo digital de terreno. In: SIMPÓSIO BRASILEIRO DE SENSORIAMENTO REMOTO, 12., 2005, Goiânia. Anais... São José dos Campos: INPE, 2005. p. 1563-1568| Biblioteca(s): Embrapa Cerrados. |
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| 17. | | FERREIRA, J. N.; LENNOX, G. D.; BERENGUER, E.; FERREIRA, M. do S. G.; SCHWARTZ, G.; MELO, L. de O.; REIS JUNIOR, D. N.; NASCIMENTO, R. O.; FERREIRA, F. N.; ESPIRITO-SANTO, F.; SMITH, C. C.; BARLOW, J. Assessing the growth and climate sensitivity of secondary forests in highly deforested Amazonian landscapes. Ecology, v. 101, n. 3, e02954, Mar. 2020.| Biblioteca(s): Embrapa Amazônia Oriental. |
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| 18. | | MOURA, Y. M. de; BALZTER, H.; GALVÃO, L. S.; DALAGNOL, R.; ESPÍRITO-SANTO, F.; SANTOS, E. G.; GARCIA, M.; BISPO, P. da C.; OLIVEIRA JUNIOR, R. C. de; SHIMABUKURO, Y. E. Carbon dynamics in a human-modified tropical forest: a case study using multi-temporal LiDAR Data. Remote Sensing, v. 12, n. 3, Article 430, 2020.| Biblioteca(s): Embrapa Amazônia Oriental. |
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| 19. | | ALMEIDA, R. G. dos S.; MARTINS, M. A.; OLIVEIRA, F. C.; ESPIRITO SANTO, F.; CALVES, G. S.; PILARSKI, F.; CHAGAS, E. C.; FERNANDES, C. E.; MARTINS, M. L.; CAMPOS, C. M. de. Dietary supplementation of ginger (Zingiber officinale) essential oil exhibits positive immunomodulatory effects on the Neotropical catfish Pseudoplatystoma reticulatum without negative effects on fish liver histomorphometry. Latin American Journal of Aquatic Research, v. 49, n. 4, p. 595-607, 2021.| Biblioteca(s): Embrapa Amazônia Ocidental. |
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| 20. | | SHIMABUKURO, Y. E.; DUARTE, V.; MOREIRA, M. A.; ARAI, E.; RUDORFF, B. F. T.; ANDERSON, L. O.; ESPIRITO SANTO, F. D. B.; FREITAS, R. M. de; AULICINO, L. C. M.; MAURANO, L. E. P.; ARAGÃO, J. R. L. de. Detecção de áreas desflorestadas em tempo real: conceitos básicos, desenvolvimento e aplicação do projeto deter. São José dos Campos: INPE, 2005. 1 CD-ROM. (INPE-12288-RPE/796).| Biblioteca(s): Embrapa Agropecuária Oeste. |
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| Registros recuperados : 31 | |
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 | Acesso ao texto completo restrito à biblioteca da Embrapa Amazônia Oriental. Para informações adicionais entre em contato com cpatu.biblioteca@embrapa.br. |
Registro Completo
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Biblioteca(s): |
Embrapa Amazônia Oriental; Embrapa Roraima. |
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Data corrente: |
12/03/2019 |
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Data da última atualização: |
27/12/2019 |
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Tipo da produção científica: |
Artigo em Periódico Indexado |
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Circulação/Nível: |
A - 1 |
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Autoria: |
SILVA, C. V. J.; ARAGÃO, L. E. O. C.; BARLOW, J.; ESPIRITO-SANTO, F.; YOUNG, P. J.; ANDERSON, L. O.; BERENGUER, E.; BRASIL, I.; BROWN, I. F.; CASTRO, B.; FARIAS, R.; FERREIRA, J. N.; FRANÇA, F.; GRAÇA, P. M. L. A.; KIRSTEN, L.; LOPES, A. P.; SALIMON, C.; SCARANELLO, M. A.; SEIXAS, M.; SOUZA, F. C.; XAUD, H. A. M. |
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Afiliação: |
Camila V. J. Silva, Lancaster University / INPE; Luiz E. O. C. Aragão, INPE / University of Exeter; Jos Barlow, Lancaster University; Fernando Espirito-Santo, University of Leicester, University Road; Paul J. Young, Lancaster University; Liana O. Anderson, CEMADEN / University of Oxford; Erika Berenguer, CEMADEN / University of Oxford; Izaias Brasil, UFAC; I. Foster Brown, UFAC / Woods Hole Research Center; Bruno Castro, Instituto Centro de Vida; Renato Farias, Instituto Centro de Vida; JOICE NUNES FERREIRA, CPATU; Filipe França, Lancaster University / CPATU; Paulo M. L. A. Graça, INPA; Letícia Kirsten, INPA; Aline P. Lopes, INPE; Cleber Salimon, Universidade Estadual da Paraíba; Marcos Augusto Scaranello, Instituto Centro de Vida / CNPTIA; Marina Seixas, COLABORADORA CPATU; Fernanda C. Souza, University of Leeds; HARON ABRAHIM MAGALHAES XAUD, CPAF-RR. |
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Título: |
Drought-induced Amazonian wildfires instigate a decadal-scale disruption of forest carbon dynamics. |
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Ano de publicação: |
2018 |
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Fonte/Imprenta: |
Philosophical Transactions of the Royal Society B, v. 373, n. 1760, p. 1-12, Nov. 2018. |
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DOI: |
10.1098/rstb.2018.0043 |
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Idioma: |
Inglês |
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Conteúdo: |
Drought-induced wildfires have increased in frequency and extent over the tropics. Yet, the long-term (greater than 10 years) responses of Amazonian lowland forests to fire disturbance are poorly known. To understand post-fire forest biomass dynamics, and to assess the time required for fire-affected forests to recover to pre-disturbance levels, we combined 16 single with 182 multiple forest census into a unique large-scale and long-term dataset across the Brazilian Amazonia. We quantified biomass, mortality and wood productivity of burned plots along a chronosequence of up to 31 years post-fire and compared to surrounding unburned plots measured simultaneously. Stem mortality and growth were assessed among functional groups. At the plot level, we found that fire-affected forests have biomass levels 24.8 ± 6.9% below the biomass value of unburned control plots after 31 years. This lower biomass state results from the elevated levels of biomass loss through mortality, which is not sufficiently compensated for by wood productivity (incremental growth + recruitment). At the stem level, we found major changes in mortality and growth rates up to 11 years post-fire. The post-fire stem mortality rates exceeded unburned control plots by 680% (i.e. greater than 40 cm diameter at breast height (DBH); 5?8 years since last fire) and 315% (i.e. greater than 0.7 g cm−3 wood density; 0.75?4 years since last fire). Our findings indicate that wildfires in humid tropical forests can significantly reduce forest biomass for decades by enhancing mortality rates of all trees, including large and high wood density trees, which store the largest amount of biomass in old-growth forests. This assessment of stem dynamics, therefore, demonstrates that wildfires slow down or stall the post-fire recovery of Amazonian forests. MenosDrought-induced wildfires have increased in frequency and extent over the tropics. Yet, the long-term (greater than 10 years) responses of Amazonian lowland forests to fire disturbance are poorly known. To understand post-fire forest biomass dynamics, and to assess the time required for fire-affected forests to recover to pre-disturbance levels, we combined 16 single with 182 multiple forest census into a unique large-scale and long-term dataset across the Brazilian Amazonia. We quantified biomass, mortality and wood productivity of burned plots along a chronosequence of up to 31 years post-fire and compared to surrounding unburned plots measured simultaneously. Stem mortality and growth were assessed among functional groups. At the plot level, we found that fire-affected forests have biomass levels 24.8 ± 6.9% below the biomass value of unburned control plots after 31 years. This lower biomass state results from the elevated levels of biomass loss through mortality, which is not sufficiently compensated for by wood productivity (incremental growth + recruitment). At the stem level, we found major changes in mortality and growth rates up to 11 years post-fire. The post-fire stem mortality rates exceeded unburned control plots by 680% (i.e. greater than 40 cm diameter at breast height (DBH); 5?8 years since last fire) and 315% (i.e. greater than 0.7 g cm−3 wood density; 0.75?4 years since last fire). Our findings indicate that wildfires in humid tropical forests can sig... Mostrar Tudo |
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Palavras-Chave: |
Dinâmica do carbono. |
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Thesagro: |
Floresta Tropical; Incêndio Florestal; Seca. |
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Categoria do assunto: |
K Ciência Florestal e Produtos de Origem Vegetal |
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Marc: |
LEADER 03043naa a2200421 a 4500
001 2106971
005 2019-12-27
008 2018 bl uuuu u00u1 u #d
024 7 $a10.1098/rstb.2018.0043$2DOI
100 1 $aSILVA, C. V. J.
245 $aDrought-induced Amazonian wildfires instigate a decadal-scale disruption of forest carbon dynamics.$h[electronic resource]
260 $c2018
520 $aDrought-induced wildfires have increased in frequency and extent over the tropics. Yet, the long-term (greater than 10 years) responses of Amazonian lowland forests to fire disturbance are poorly known. To understand post-fire forest biomass dynamics, and to assess the time required for fire-affected forests to recover to pre-disturbance levels, we combined 16 single with 182 multiple forest census into a unique large-scale and long-term dataset across the Brazilian Amazonia. We quantified biomass, mortality and wood productivity of burned plots along a chronosequence of up to 31 years post-fire and compared to surrounding unburned plots measured simultaneously. Stem mortality and growth were assessed among functional groups. At the plot level, we found that fire-affected forests have biomass levels 24.8 ± 6.9% below the biomass value of unburned control plots after 31 years. This lower biomass state results from the elevated levels of biomass loss through mortality, which is not sufficiently compensated for by wood productivity (incremental growth + recruitment). At the stem level, we found major changes in mortality and growth rates up to 11 years post-fire. The post-fire stem mortality rates exceeded unburned control plots by 680% (i.e. greater than 40 cm diameter at breast height (DBH); 5?8 years since last fire) and 315% (i.e. greater than 0.7 g cm−3 wood density; 0.75?4 years since last fire). Our findings indicate that wildfires in humid tropical forests can significantly reduce forest biomass for decades by enhancing mortality rates of all trees, including large and high wood density trees, which store the largest amount of biomass in old-growth forests. This assessment of stem dynamics, therefore, demonstrates that wildfires slow down or stall the post-fire recovery of Amazonian forests.
650 $aFloresta Tropical
650 $aIncêndio Florestal
650 $aSeca
653 $aDinâmica do carbono
700 1 $aARAGÃO, L. E. O. C.
700 1 $aBARLOW, J.
700 1 $aESPIRITO-SANTO, F.
700 1 $aYOUNG, P. J.
700 1 $aANDERSON, L. O.
700 1 $aBERENGUER, E.
700 1 $aBRASIL, I.
700 1 $aBROWN, I. F.
700 1 $aCASTRO, B.
700 1 $aFARIAS, R.
700 1 $aFERREIRA, J. N.
700 1 $aFRANÇA, F.
700 1 $aGRAÇA, P. M. L. A.
700 1 $aKIRSTEN, L.
700 1 $aLOPES, A. P.
700 1 $aSALIMON, C.
700 1 $aSCARANELLO, M. A.
700 1 $aSEIXAS, M.
700 1 $aSOUZA, F. C.
700 1 $aXAUD, H. A. M.
773 $tPhilosophical Transactions of the Royal Society B$gv. 373, n. 1760, p. 1-12, Nov. 2018.
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