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| Registros recuperados : 35 | |
| 1. |  | BERENGUER, E.; GARDNER, T. A.; FERREIRA, J. N.; ARAGÃO, L. E. O. C.; NALLY, R. M.; THOMSON, J. R.; VIEIRA, I. C. G.; BARLOW, J. Seeing the woods through the saplings: Using wood density to assess the recovery of human-modified Amazonian forests. Journal of Ecology, v. 106, n. 6, p. 2190-2203, Nov. 2018.| Biblioteca(s): Embrapa Amazônia Oriental. |
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| 2. | | BARLOW, J.; PARRY, L.; GARDNER, T. A.; FERREIRA, J. N.; ARAGÃO, L. E. O. C.; CARMENTA, R.; BERENGUER, E.; VIEIRA, I. C. G.; SOUZA, C.; COCHRANE, M. A. The critical importance of considering fire in REDD+ programs. Biological Conservation, v. 154, p. 1-8, Oct. 2012.| Biblioteca(s): Embrapa Amazônia Oriental. |
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| 3. | | FONSECA, M. G.; ANDERSON, L. O. A.; ARAI, E.; SHIMABUKURO, Y. E.; XAUD, H. A. M.; XAUD, M. R.; MADANI, N.; WAGNER, F. H.; ARAGÃO, L. E. O. C. Climatic and anthropogenic drivers of northern Amazon fires during the 2015-2016 El Niño event. Ecological Applications, v. 27, n. 8, p. 2514-2527, 2017.| Biblioteca(s): Embrapa Roraima. |
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| 4. | | MAEDA, E. E.; ARAGÃO, L. E. O. C.; BAKER, J. C. A.; BALBINO, L. C.; MOURA, Y. M. de; NOBRE, A. D.; NUNES, M. H.; SILVA JUNIOR, C. H. L.; REIS, J. C. dos. Land use still matters after deforestation. Communications Earth & Environment, v. 4, 2023. 4 p.| Biblioteca(s): Embrapa Cerrados. |
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| 5. | | HAWES, J. E.; VIEIRA, I. C. G.; MAGNAGO, L. F. S.; BERENGUER, E.; FERREIRA, J. N.; ARAGÃO, L. E. O. C.; CARDOSO, A.; LEES, A. C.; LENNOX, G. D.; TOBIAS, J. A; WALDRON, A.; BARLOW, J. A large-scale assessment of plant dispersal mode and seed traits across human-modified Amazonian forests. Journal of Ecology, v. 108, n. 4, p. 1373-1385, 2020.| Biblioteca(s): Embrapa Amazônia Oriental. |
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| 6. | | BERENGUER, E.; FERREIRA, J.; GARDNER, T. A.; ARAGÃO, L. E. O. C.; CAMARGO, P. B. de; CERRI, C. E.; DURIGAN, M.; OLIVEIRA JUNIOR, R. C. de; VIEIRA, I. C. G.; BARLOW, J. A large-scale field assessment of carbon stocks in human-modified tropical forests. Global Change Biology, v. 20, n. 12, p. 3713-3726, 2014.| Biblioteca(s): Embrapa Amazônia Oriental. |
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| 7. | | BERENGUER, E.; GARDNER, T. A.; FERREIRA, J.; ARAGÃO, L. E. O. C.; CAMARGO, P. B.; CERRI, C. E.; DURIGAN, M.; OLIVEIRA JUNIOR, R. C.; VIEIRA, I. C. G.; BARLOW, J. Developing cost-effective field assessments of carbon stocks in human-modified tropical forests. Plos One, v. 10, n. 8, e0133139, 2015.| Biblioteca(s): Embrapa Amazônia Oriental. |
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| 8. | | FERREIRA, J.; ARAGÃO, L. E. O. C.; BARLOW, J.; BARRETO, P.; BERENGUER, E.; BUSTAMANTE, M.; GARDNER, T. A.; LEES, A. C.; LIMA, A.; LOUZADA, J.; PARDINI, R.; PARRY, L.; PERES, C. A.; POMPEU, P. S.; TABARELLI, M.; ZUANON, J. Brazil's environmental leadership at risk. Science, v. 346, n. 6210, p. 706-707, Nov. 2014.| Biblioteca(s): Embrapa Amazônia Oriental. |
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| 9. | | WITHEY, K.; BERENGUER, E.; PALMEIRA, A. F.; ESPÍRITO-SANTO, F. D. B.; LENNOX, G. D.; SILVA, C. V. J.; ARAGÃO, L. E. O. C.; FERREIRA, J. N.; FRANÇA, F.; MALHI, Y.; ROSSI, L. C.; BARLOW, J. Quantifying immediate carbon emissions from El Ninõ-mediated wildfires in humid tropical forests. Philosophical Transactions of the Royal Society B, v. 373, n. 1760, p. 1-11, Nov. 2018.| Biblioteca(s): Embrapa Amazônia Oriental. |
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| 10. | | ANDERSON, L. O.; BURTON, C.; REIS, J. B. C. dos; PESSÔA, A. C. M.; BETT, P.; CARVALHO, N. S.; SILVA JUNIOR, C. H. L.; WILLIAMS, K.; SELAYA, G.; ARMENTERAS, D.; BILBAO, B. A.; XAUD, H. A. M.; RIVERA-LOMBARDI, R.; FERREIRA, J. N.; ARAGÃO, L. E. O. C.; JONES, C. D.; WILTSHIRE, A. J. An alert systemfor Seasonal Fire probability forecast for South American Protected Areas. Climate Resilience and Sustainability, p. 1-19, 2021.| Biblioteca(s): Embrapa Roraima. |
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| 11. | | ANDERSON, L. O.; BURTON, C.; REIS, J. B. C. dos; PESSÔA, A. C. M.; BETT, P.; CARVALHO, N. S.; SILVA JUNIOR, C. H. L.; WILLIAMS, K.; SELAYA, G.; ARMENTERAS, D.; BILBAO, B. A.; XAUD, H. A. M.; RIVERA-LOMBARDI, R.; FERREIRA, J. N.; ARAGÃO, L. E. O. C.; JONES, C. D.; WILTSHIRE, A. J. An alert systemfor Seasonal Fire probability forecast for South American Protected Areas. Climate Resilience and Sustainability, v. 1, n. 1, p. 1-19, Feb. 2022.| Biblioteca(s): Embrapa Amazônia Oriental. |
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| 12. | | FERREIRA, J. N.; LENNOX, G. D.; GARDNER, T. A.; THOMSON, J. R.; BERENGUER, E.; LEES, A. C.; MAC BALLY, R.; ARAGÃO, L. E. O. C.; FERRAZ, S. F. B.; LOUZADA, J.; MOURA, N. G.; OLIVEIRA, V. H. F.; PARDINI, R.; SOLAR, R. R. C.; VIEIRA, I. C. G.; BARLOW, J. Carbon-focused conservation may fail to protect the most biodiverse tropical forests. Nature Climate Change, v. 8, n. 8, p. 744-749, Aug. 2018.| Biblioteca(s): Embrapa Amazônia Oriental. |
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| 13. | | SILVA, C. V. J.; ARAGÃO, L. E. O. C.; YOUNG, P. J.; ESPIRITO-SANTO, F.; BERENGUER, E.; ANDERSON, L. O.; BRASIL, I.; PONTES-LOPES, A.; FERREIRA, J. N.; WITHEY, K.; FRANÇA, F.; GRAÇA, P. M. L. A.; KIRSTEN, L.; XAUD, H. A. M.; SALIMON, C.; SCARANELLO, M. A.; CASTRO, B.; SEIXAS, M.; FARIAS, R.; BARLOW, J. Estimating the multi-decadal carbon deficit of burned Amazonian forests. Environmental Research Letters, v. 15, Article 114023, 2020.| Biblioteca(s): Embrapa Amazônia Oriental; Embrapa Roraima. |
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| 14. | | 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. Drought-induced Amazonian wildfires instigate a decadal-scale disruption of forest carbon dynamics. Philosophical Transactions of the Royal Society B, v. 373, n. 1760, p. 1-12, Nov. 2018.| Biblioteca(s): Embrapa Amazônia Oriental; Embrapa Roraima. |
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| 15. | | STARK, S. C.; BRESHEARS, D. D.; ARAGÓN, S.; VILLEGAS, J. C.; LAW, D. J.; SMITH, M. N.; MINOR, D. M.; ASSIS, R. L. de; ALMEIDA, D. R. A. de; OLIVEIRA, G. de; SALESKA, S. R.; SWANN, A. S.; MOURA, J. M. S.; CAMARGO, J. L.; SILVA, R. da; ARAGÃO, L. E. O. C.; OLIVEIRA JUNIOR, R. C. de. Reframing tropical savannization: linking changes in canopy structure to energy balance alterations that impact climate. Ecosphere, v. 11, n. 9, e03231, 2020.| Biblioteca(s): Embrapa Amazônia Oriental. |
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| 16. | | LENNOX, G. D.; GARDNER, T. A.; THOMSON, J. R.; FERREIRA, J. N.; BERENGUER, E.; LEES, A. C.; NALLY, R. M.; ARAGÃO, L. E. O. C.; FERRAZ, S. F. B.; LOUZADA, J.; MOURA, N. G.; OLIVEIRA, V. H. F.; PARDINI, R.; SOLAR, R. R. C.; MELLO, F. Z. V. de; VIEIRA, I. C. G.; BARLOW, J. Second rate or a second chance? Assessing biomass and biodiversity recovery in regenerating Amazonian forests. Global Change Biology, v. 24, n. 12, p. 5680-5694, 2018.| Biblioteca(s): Embrapa Amazônia Oriental. |
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| 17. | | MOURA, Y. M. de; GALVÃO, L. S.; HILKER, T.; WU, J.; SALESKA, S.; AMARAL, C. H. do; NELSON, B. W.; LOPES, A. P.; WIEDEMAN, K. K.; PROHASKA, N.; OLIVEIRA JUNIOR, R. C. de; MACHADO, C. B.; ARAGÃO, L. E. O. C. Spectral analysis of amazon canopy phenology during the dry season using a tower hyperspectral camera and modis observations. ISPRS Journal of Photogrammetry and Remote Sensing, v. 131, p. 52-64, Sept. 2017.| Biblioteca(s): Embrapa Amazônia Oriental. |
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| 18. | | BERENGUER, E.; LENNOX, G. D.; FERREIRA, J. N.; MALHI, Y.; ARAGÃO, L. E. O. C.; BARRETO, J. R.; ESPÍRITO-SANTO, F. del B.; FIGUEIREDO, A. E. S.; FRANÇA, F.; GARDNER, T. A.; JOLY, C. A.; PALMEIRA, A. F.; QUESADA, C. A.; ROSSI, L. C.; SEIXAS, M. M. M. de; SMITH, C. C.; WITHEY, K.; BARLOW, J. Tracking the impacts of El Niño drought and fire in human-modified Amazonian forests. PNAS, v. 118, n. 30, e201937711, 2021.| Biblioteca(s): Embrapa Amazônia Oriental. |
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| 19. | | NUNES, C. A.; BERENGUER, E.; FRANÇA, F.; FERREIRA, J. N.; LEES, A. C.; LOUZADA, J.; SAYER, E. J.; SOLAR, R.; SMITH, C. C.; ARAGÃO, L. E. O. C.; BRAGA, D. de L.; CAMARGO, P. B. de; CERRI, C. E. P.; OLIVEIRA JUNIOR, R. C. de; DURIGAN, M.; MOURA, N.; OLIVEIRA, V. H. F.; RIBAS, C.; VAZ-DE-MELLO, F.; VIEIRA, I.; ZANETTI, R.; BARLOW, J. Linking land-use and land-cover transitions to their ecological impact in the Amazon. PNAS, v. 119, n. 27, e2202310119, 2022.| Biblioteca(s): Embrapa Amazônia Oriental. |
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| 20. | | VEDOVATO, L. B.; CARVALHO, L. C. S.; ARAGÃO, L. E. O. C.; BIRD, M.; PHILLIPS, O. L.; ALVAREZ, P.; BARLOW, J.; BARTHOLOMEW, D. C.; BERENGUER, E.; CASTRO, W.; FERREIRA, J. N.; FRANÇA, F. M.; MALHI, Y.; MARIMON, B.; MARIMON JÚNIOR, B. H.; MONTEAGUDO, A.; OLIVEIRA, E. A.; PEREIRA, L. O.; PONTES-LOPES, A.; QUESADA, C. A.; SILVA, C. V. J.; ESPEJO, J. E. S.; SILVEIRA, M.; FELDPAUSCH, T. R. Ancient fires enhance Amazon forest drought resistance. Frontiers in Forests and Global Change, v. 6, 1024101, 2023.| Biblioteca(s): Embrapa Amazônia Oriental. |
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| Registros recuperados : 35 | |
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 | Acesso ao texto completo restrito à biblioteca da Embrapa Agrobiologia. Para informações adicionais entre em contato com cnpab.biblioteca@embrapa.br. |
Registro Completo
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Biblioteca(s): |
Embrapa Agrobiologia. |
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Data corrente: |
16/12/2003 |
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Data da última atualização: |
16/12/2003 |
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Autoria: |
BODDEY, R. M.; XAVIER, D. F.; ALVES, B. J. R.; URQUIAGA, S. |
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Título: |
Brazilian agriculture: The Transition to sustainability. |
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Ano de publicação: |
2003 |
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Fonte/Imprenta: |
Journal of Crop Production, New York, v. 9, n. ½, p. 593-621, 2003. |
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Idioma: |
Inglês |
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Conteúdo: |
Brazil has a total area of 85() million ha. of which 90% is within thc tropics. Historically. the system of exploitation of the land for agriculture and forestry was based on land clcarjl1g, cultivation for some years and then moving on to new areas. This process often left degraded areas behind, especially in the mountainous areas of the country. With modem agricultural technology, crops can be successfully grown in virtually any region of the country. The current challenge for Brazil is to feed its population and provide agricultural surpluses for lhe growing ex- port markets, while preserving its rich and biologically-diverse native vegetation which still covers almost half of lhe country. The objective or this review is to trace the history or agricultural activity in this country, and to assess the sustainability of lhe cropping and pasture systems which today occupy lhe largest areas. At present approximately 50 million ha are under annual and perennial crops, while almost twice this area is under pastures. These pastures. predominately Brachiaria spp., arc mostly in a degraded stale due to lack or fertilization and over grazing. The various options available 10 recover these pastures or convert these areas for sustainable cropping are explained. In recent years, increasing proportions of soybean, wheat, and com are produced under zero tillage which favors lhe conservation of soil organic matter. This not only radically reduces lhe risk of erosion but also increases lhe capacity of the soils to relain nutrients and water. Small holders who represent a considerable fraction of Brazil's food crop production, generally do not have access to fertilizers or other agricultural chemicals. They obtain very low yields and their farming practices exhaust lhe soil of nutrients. The Brazilian sugarcane industry is the largest in the world and recent changes in the management of this crop and its impact upon sustainability issues are also discussed. Brazil also has vast areas of degraded pastures and abandoned hillsides that can be used for agricultural expansion. This would prevent further destruction of native vegetation and its accompanying biological diversity for agriculture. MenosBrazil has a total area of 85() million ha. of which 90% is within thc tropics. Historically. the system of exploitation of the land for agriculture and forestry was based on land clcarjl1g, cultivation for some years and then moving on to new areas. This process often left degraded areas behind, especially in the mountainous areas of the country. With modem agricultural technology, crops can be successfully grown in virtually any region of the country. The current challenge for Brazil is to feed its population and provide agricultural surpluses for lhe growing ex- port markets, while preserving its rich and biologically-diverse native vegetation which still covers almost half of lhe country. The objective or this review is to trace the history or agricultural activity in this country, and to assess the sustainability of lhe cropping and pasture systems which today occupy lhe largest areas. At present approximately 50 million ha are under annual and perennial crops, while almost twice this area is under pastures. These pastures. predominately Brachiaria spp., arc mostly in a degraded stale due to lack or fertilization and over grazing. The various options available 10 recover these pastures or convert these areas for sustainable cropping are explained. In recent years, increasing proportions of soybean, wheat, and com are produced under zero tillage which favors lhe conservation of soil organic matter. This not only radically reduces lhe risk of erosion but also increases ... Mostrar Tudo |
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Palavras-Chave: |
Cana-de-açúcar; Coffee; Direct sowing; Soybean; Zero tillage. |
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Thesagro: |
Café; Pastagem; Plantio Direto; Soja. |
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Thesaurus NAL: |
sugarcane; tropical pastures. |
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Categoria do assunto: |
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Marc: |
LEADER 02951naa a2200289 a 4500
001 1625019
005 2003-12-16
008 2003 bl --- 0-- u #d
100 1 $aBODDEY, R. M.
245 $aBrazilian agriculture$bThe Transition to sustainability.
260 $c2003
520 $aBrazil has a total area of 85() million ha. of which 90% is within thc tropics. Historically. the system of exploitation of the land for agriculture and forestry was based on land clcarjl1g, cultivation for some years and then moving on to new areas. This process often left degraded areas behind, especially in the mountainous areas of the country. With modem agricultural technology, crops can be successfully grown in virtually any region of the country. The current challenge for Brazil is to feed its population and provide agricultural surpluses for lhe growing ex- port markets, while preserving its rich and biologically-diverse native vegetation which still covers almost half of lhe country. The objective or this review is to trace the history or agricultural activity in this country, and to assess the sustainability of lhe cropping and pasture systems which today occupy lhe largest areas. At present approximately 50 million ha are under annual and perennial crops, while almost twice this area is under pastures. These pastures. predominately Brachiaria spp., arc mostly in a degraded stale due to lack or fertilization and over grazing. The various options available 10 recover these pastures or convert these areas for sustainable cropping are explained. In recent years, increasing proportions of soybean, wheat, and com are produced under zero tillage which favors lhe conservation of soil organic matter. This not only radically reduces lhe risk of erosion but also increases lhe capacity of the soils to relain nutrients and water. Small holders who represent a considerable fraction of Brazil's food crop production, generally do not have access to fertilizers or other agricultural chemicals. They obtain very low yields and their farming practices exhaust lhe soil of nutrients. The Brazilian sugarcane industry is the largest in the world and recent changes in the management of this crop and its impact upon sustainability issues are also discussed. Brazil also has vast areas of degraded pastures and abandoned hillsides that can be used for agricultural expansion. This would prevent further destruction of native vegetation and its accompanying biological diversity for agriculture.
650 $asugarcane
650 $atropical pastures
650 $aCafé
650 $aPastagem
650 $aPlantio Direto
650 $aSoja
653 $aCana-de-açúcar
653 $aCoffee
653 $aDirect sowing
653 $aSoybean
653 $aZero tillage
700 1 $aXAVIER, D. F.
700 1 $aALVES, B. J. R.
700 1 $aURQUIAGA, S.
773 $tJournal of Crop Production, New York$gv. 9, n. ½, p. 593-621, 2003.
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