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4. | | PEREIRA, A. A.; BARROS, D. A. de; ACERBI JUNIOR, F. W.; PEREIRA, J. A. A.; REIS, A. A. dos. Análise da distribuição espacial de áreas queimadas através da função K de Ripley. Scientia Forestalis, Piracicaba, v. 41, n. 100, p. 445-455, dez. 2013. Biblioteca(s): Embrapa Florestas. |
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6. | | PROTÁSIO, T. de P.; COUTO, A. M.; REIS, A. A. dos; TRUGILHO, P. F.; GODINHO, T. P. Potencial siderúrgico e energético do carvão vegetal de clones de Eucalyptus spp. aos 42 meses de idade. Pesquisa Florestal Brasileira, Colombo, v. 33, n. 74, p. 137-149, abr./jun. 2013. Biblioteca(s): Embrapa Florestas. |
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7. | | GUEDES, I. C. de L.; MELLO, J. M. de; SILVEIRA, E. M. de O.; MELLO, C. R. de; REIS, A. A. dos; GOMIDE, L. R. Continuidade espacial de características dendrométricas em povoamentos clonais de eucalyptus sp. avaliada ao longo do tempo. Revista Cerne, Lavras, v. 21, n. 4, p. 527-534, out./dez. 2015. Biblioteca(s): Embrapa Florestas. |
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8. | | REIS, A. A. dos; MELLO, J. M. de; RAIMUNDO, M. R.; ACERBI JUNIOR, F. W.; OLIVEIRA, M. S. de; DINIZ, J. M. F. de S. Estratificação de um povoamento de eucalipto por interpoladores geoestatísticos e sensoriamento remoto. Pesquisa Agropecuária Brasileira, Brasília, DF, v. 51, n. 10, p. 1751-1761, out. 2016. Título em inglês: Stratification of an eucalyptus plantation through geostatistical interpolators and remote sensing. Biblioteca(s): Embrapa Unidades Centrais. |
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10. | | REIS, A. A. dos; PROTÁSIO, T. de P.; MELO, I. C. N. A. de; TRUGILHO, P. F.; CARNEIRO, A. de C. O. Composição da madeira e do carvão vegetal de Eucalyptus urophylla em diferentes locais de plantio. Pesquisa Florestal Brasileira, Colombo, v. 32, n. 71, p. 277-290, jul./set. 2012. Biblioteca(s): Embrapa Florestas. |
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11. | | BATISTA, A. P. B.; MELLO, J. M. de; RAIMUNDO, M. R.; SCOLFORO, H. F.; REIS, A. A. dos; SCOLFORO, J. R. S. Species richness and diversity in shrub savanna using ordinary kriging. Pesquisa Agropecuária Brasileira, Brasília, DF, v. 51, n. 8, p. 958-966, ago. 2016. Título em português: Riqueza e diversidade de espécies em um fragmento de campo cerrado por meio de krigagem ordinária. Biblioteca(s): Embrapa Unidades Centrais. |
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12. | | SILVA, S. T. da; MELLO, J. M. de; ARCEBI JUNIOR, F. W.; REIS, A. A. dos; RAIMUNDO, M. R.; SILVA, I. L. G.; SCOLFORO, J. R. S. Uso de imagens de sensoriamento remoto para estratificação do cerrado em inventários florestais. Pesquisa Florestal Brasileira, Colombo, v. 34, n. 80, p. 337-343, out./dez. 2014. Biblioteca(s): Embrapa Florestas. |
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13. | | PEREIRA, F. R. da S.; REIS, A. A. dos; FREITAS, R. G.; OLIVEIRA, S. R. de M.; AMARAL, L. R. do; FIGUEIREDO, G. K. D. A.; ANTUNES, J. F. G.; LAMPARELLI, R. A. C.; MORO, E.; MAGALHÃES, P. S. G. Imputation of missing parts in UAV orthomosaics using PlanetScope and Sentinel-2 data: a case study in a grass-dominated área. International Journal of Geo-Information, v. 12, n. 2, 41, Feb. 2023. Biblioteca(s): Embrapa Agricultura Digital. |
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14. | | REIS, A. A. dos; WERNER, J. P. S.; SILVA, B. C. da; ANTUNES, J. F. G.; ESQUERDO, J. C. D. M.; FIGUEIREDO, G. K. D. A.; COUTINHO, A. C.; LAMPARELLI, R. A. C.; MAGALHÃES, P. S. G. Can canopy height of mixed pastures in integrated crop-livestock systems be estimated using planetscope imagery? In: WORLD CONGRESS ON INTEGRATED CROP-LIVESTOCK-FORESTRY SYSTEMS, 2., 2021. Proceedings reference. Brasília, DF: Embrapa, 2021. p. 658-663. WCCLF 2021. Evento online. Biblioteca(s): Embrapa Agricultura Digital. |
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15. | | ALMEIDA, H. S. L.; REIS, A. A. dos; WERNER, J. P. S.; ANTUNES, J. F. G.; ZHONG, L.; FIGUEIREDO, G. K. D. A.; ESQUERDO, J. C. D. M.; COUTINHO, A. C.; LAMPARELLI, R. A. C.; MAGALHÃES, P. S. G. Deep neural networks for mapping integrated crop-livestock systems using PlanetScope time series. IEEE INTERNATIONAL GEOSCIENCE AND REMOTE SENSING SYMPOSIUM, 2021, Brussels. Proceedings [...]. [S. l.]: IEEE, 2021. p. 4224-4227. IGARSS 2021. Paper WE2.MM-8.3. Biblioteca(s): Embrapa Agricultura Digital. |
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16. | | REIS, A. A. dos; SILVA, M. A. da; SANTOS, F. C. dos; ALBUQUERQUE FILHO, M. R. de; SILVEIRA, M. C. T. da; TEIXEIRA, E. C.; VASCONCELOS, A. de A.; BORGES, I. D.; SOUZA, W. G. Impacto do sistema de pastejo no estoque de carbono lábil do solo arenoso. In: CONGRESO INTERNACIONAL DE SISTEMAS SILVOPASTORILES, 12.; CONGRESO DE LA RED GLOBAL DE SISTEMAS SILVOPASTORILES, 2.; IV SEMINARIO NACIONAL DE SISTEMAS SILVOPASTORILES, 4., 2023, Montevideo; CONGRESO NACIONAL SISTEMAS SILVOPASTORILES, 5., 2023, Buenos Aires. Sistemas silvopastoriles: hacia una diversificación sostenible. Cali: CIPAV, 2023. p. 842-848. Biblioteca(s): Embrapa Milho e Sorgo. |
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17. | | TORO, A. P. S. G. D.; WERNER, J. P. S.; REIS, A. A. dos; ESQUERDO, J. C. D. M.; ANTUNES, J. F. G.; COUTINHO, A. C.; LAMPARELLI, R. A. C.; MAGALHÃES, P. S. G.; FIGUEIREDO, G. K. D. A. Evaluation of early season mapping of integrated crop livestock systems using Sentinel-2 data. The International Archives of the Photogrammetry, Remote Sensing and Spatial Information Sciences, v. 43, B3, p. 1335-1340, 2022. Edition of proceedings of the 2022 edition of the XXIVth ISPRS Congress, Nice, France. Biblioteca(s): Embrapa Agricultura Digital. |
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18. | | BUENO, I. T.; ANTUNES, J. F. G.; REIS, A. A. dos; WERNER, J. P. S.; TORO, A. P.; FIGUEIREDO, G. K. D. A.; ESQUERDO, J. C. D. M.; LAMPARELLI, R. A. C.; COUTINHO, A. C.; MAGALHÃES, P. S. G. Mapping integrated crop-livestock systems in Brazil with planetscope time series and deep learning. Remote Sensing of Environment, v. 299, 113886, Dec. 2023. Biblioteca(s): Embrapa Agricultura Digital. |
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19. | | REIS, A. A. dos; WERNER, J. P. S.; SILVA, B. C.; FIGUEIREDO, G. K. D. A.; ANTUNES, J. F. G.; ESQUERDO, J. C. D. M.; COUTINHO, A. C.; LAMPARELLI, R. A. C.; ROCHA, J. V.; MAGALHÃES, P. S. G. Monitoring pasture aboveground biomass and canopy height in an integrated crop-livestock system using textural information from PlanetScope imagery. Remote Sensing, v. 12, n. 16, p. 1-21, Aug. 2020. Article number: 2534. Biblioteca(s): Embrapa Agricultura Digital. |
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20. | | ANTUNES, J. F. G.; REIS, A. A. dos; ALMEIDA, H. S. L.; WERNER, J. P. S.; FIGUEIREDO, G. K. D. A.; ESQUERDO, J. C. D. M.; BUENO, I. T.; TORO, A. P. S. G. D.; LAMPARELLI, R. A. C.; COUTINHO, A. C.; MAGALHÃES, P. S. G. Classification of integrated crop-livestock systems using PlanetScope time series. In: SIMPÓSIO BRASILEIRO DE SENSORIAMENTO REMOTO, 20., 2023, Florianópolis. Anais [...]. São José dos Campos: Instituto Nacional de Pesquisas Espaciais, 2023. p. 916-919. Editores: Douglas Francisco Marcolino Gherardi, Ieda Del´Arco Sanches, Luiz Eduardo Oliveira e Cruz de Aragão. Biblioteca(s): Embrapa Agricultura Digital. |
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Registros recuperados : 23 | |
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Registro Completo
Biblioteca(s): |
Embrapa Agrobiologia. |
Data corrente: |
31/08/2020 |
Data da última atualização: |
31/08/2020 |
Tipo da produção científica: |
Artigo em Periódico Indexado |
Circulação/Nível: |
A - 1 |
Autoria: |
OLIVEIRA, A. L. de; COELHO JÚNIOR, M. G.; BARROS, D. A.; RESENDE, A. S. de; SANSEVERO, J. B. B.; BORGES, L. A. C.; BASSO, V. M.; FARIA, S. M. de. |
Afiliação: |
Athila Leandro de Oliveira, UFRRJ; Marcondes Geraldo Coelho Junior, UFRRJ; Dalmo Arantes Barros, Universidade Federal de Alfenas; ALEXANDER SILVA DE RESENDE, CNPAB; Jerônimo Boelsums Barreto Sansevero, UFRRJ; Luis Antônio Coimbra Borges, UFLA; Vanessa Maria Basso, UFRRJ; SERGIO MIANA DE FARIA, CNPAB. |
Título: |
Revisiting the concept of fiscal modules: implications for restoration andconservation programs in Brazil. |
Ano de publicação: |
2020 |
Fonte/Imprenta: |
Land Use Policy, v. 99, e104978, 2020. |
Idioma: |
Inglês |
Conteúdo: |
Fiscal modules (FMs) were created to facilitate the collection of the rural territorial tax in Brazil. In theory, thearea of a FM should be enough for a family to have income, survive, and thrive. The current Native VegetationProtection Law (Law 12.651/2012) gives equal treatment to all people who own up to four FMs through theEnvironmental Regularization Program for small properties and family agriculture. Thus, FMs are parameters forflexible land allocation, reducing the area in which the restoration of native vegetation is mandatory. In thisstudy, we sought to describe the history of the creation of FMs to verify the correlations between currentagricultural and socioeconomic indicators and FM size. We used a case study in the state of Rio de Janeiro insoutheast Brazil to analyze how updating the FM affects the Environmental Regularization Program proposed bythe Native Vegetation Protection Law. FMs were created in 1979 and set in 1980, but have never been updated.Current data on land use, rate of deforestation, and productivity in rural areas should lead to changes in the FMsize and value. Analyzing the data from municipalities in the state of Rio de Janeiro, we found that the groupsformed in the cluster analysis differed from the existing FM groups in the state, which range from 5 to 35 ha. Thisdifference may be a consequence of the failure to update the FM parameters, because updating the FM definitionmay result in less hectares in each FM. This would result in a larger area to be restored, according to theEnvironmental Regularization Program, and would thus favor the overall goals of forest restoration. MenosFiscal modules (FMs) were created to facilitate the collection of the rural territorial tax in Brazil. In theory, thearea of a FM should be enough for a family to have income, survive, and thrive. The current Native VegetationProtection Law (Law 12.651/2012) gives equal treatment to all people who own up to four FMs through theEnvironmental Regularization Program for small properties and family agriculture. Thus, FMs are parameters forflexible land allocation, reducing the area in which the restoration of native vegetation is mandatory. In thisstudy, we sought to describe the history of the creation of FMs to verify the correlations between currentagricultural and socioeconomic indicators and FM size. We used a case study in the state of Rio de Janeiro insoutheast Brazil to analyze how updating the FM affects the Environmental Regularization Program proposed bythe Native Vegetation Protection Law. FMs were created in 1979 and set in 1980, but have never been updated.Current data on land use, rate of deforestation, and productivity in rural areas should lead to changes in the FMsize and value. Analyzing the data from municipalities in the state of Rio de Janeiro, we found that the groupsformed in the cluster analysis differed from the existing FM groups in the state, which range from 5 to 35 ha. Thisdifference may be a consequence of the failure to update the FM parameters, because updating the FM definitionmay result in less hectares in each FM. This would result in a larger... Mostrar Tudo |
Palavras-Chave: |
Environmental regularization. |
Thesaurus NAL: |
Environmental policy; Forestry law. |
Categoria do assunto: |
K Ciência Florestal e Produtos de Origem Vegetal |
Marc: |
LEADER 02375naa a2200241 a 4500 001 2124643 005 2020-08-31 008 2020 bl uuuu u00u1 u #d 100 1 $aOLIVEIRA, A. L. de 245 $aRevisiting the concept of fiscal modules$bimplications for restoration andconservation programs in Brazil.$h[electronic resource] 260 $c2020 520 $aFiscal modules (FMs) were created to facilitate the collection of the rural territorial tax in Brazil. In theory, thearea of a FM should be enough for a family to have income, survive, and thrive. The current Native VegetationProtection Law (Law 12.651/2012) gives equal treatment to all people who own up to four FMs through theEnvironmental Regularization Program for small properties and family agriculture. Thus, FMs are parameters forflexible land allocation, reducing the area in which the restoration of native vegetation is mandatory. In thisstudy, we sought to describe the history of the creation of FMs to verify the correlations between currentagricultural and socioeconomic indicators and FM size. We used a case study in the state of Rio de Janeiro insoutheast Brazil to analyze how updating the FM affects the Environmental Regularization Program proposed bythe Native Vegetation Protection Law. FMs were created in 1979 and set in 1980, but have never been updated.Current data on land use, rate of deforestation, and productivity in rural areas should lead to changes in the FMsize and value. Analyzing the data from municipalities in the state of Rio de Janeiro, we found that the groupsformed in the cluster analysis differed from the existing FM groups in the state, which range from 5 to 35 ha. Thisdifference may be a consequence of the failure to update the FM parameters, because updating the FM definitionmay result in less hectares in each FM. This would result in a larger area to be restored, according to theEnvironmental Regularization Program, and would thus favor the overall goals of forest restoration. 650 $aEnvironmental policy 650 $aForestry law 653 $aEnvironmental regularization 700 1 $aCOELHO JÚNIOR, M. G. 700 1 $aBARROS, D. A. 700 1 $aRESENDE, A. S. de 700 1 $aSANSEVERO, J. B. B. 700 1 $aBORGES, L. A. C. 700 1 $aBASSO, V. M. 700 1 $aFARIA, S. M. de 773 $tLand Use Policy$gv. 99, e104978, 2020.
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