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| Registros recuperados : 97 | |
| 61. |  | PUGA, A. P.; CARVALHO, C. S.; LIGO, M. A. V.; PIRES, A. M. M.; PEREIRA NETO, B. G.; ANDRADE, C. A. de. Ammonia volatilization from nitrogen fertilizer formulated with biochar. In: WORLD CONGRESS OF SOIL SCIENCE, 21., 2018, Rio de Janeiro. Soil science: beyond food and fuel: abstracts. Viçosa, MG: SBCS, 2018. Trabalho 959.| Biblioteca(s): Embrapa Meio Ambiente. |
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| 62. | | BUSCHINELLI, C. C. de A.; PASTRELLO, B. M. C.; RAMOS, N. P.; LIGO, M. A. V.; PIRES, A. M. M.; VIEIRA, H. B. Avaliação de impacto socioambiental da cadeia produtiva da soja - uma análise na região de Londrina/PR. In: CONGRESSO BRASILEIRO DE PLANTAS OLEAGINOSAS, ÓLEOS, GORDURAS E BIODIESEL, 6., 2009. Montes Claros. Biodiesel: inovação tecnológica ? anais. Lavras: UFLA, 2009. p. 2962-2972| Biblioteca(s): Embrapa Meio Ambiente. |
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| 63. | | BUSCHINELLI, C. C. de A.; RODRIGUES, G. S.; RODRIGUES, I. A.; FRIGHETTO, R. T. S.; PIRES, A. M. M.; LIGO, M. A. V.; IRIAS, L. J. M. Avaliação socioambiental da produção de oleaginosas e a inserção no mercado de biocombustível no Brasil. In: CONGRESSO DA REDE BRASILEIRA DE TECNOLOGIA DE BIODIESEL, 2., 2007, Brasília. Anais... Brasília: ABIPTI, 2007. 6p.| Biblioteca(s): Embrapa Meio Ambiente. |
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| 64. | | BUSCHINELLI, C. C. de A.; RODRIGUES, G. S.; RODRIGUES, I. A.; FRIGHETTO, R. T. S.; PIRES, A. M. M.; LIGO, M. A. V.; IRIAS, L. J. M. Avaliação socioambiental da produção de oleaginosas e a inserção no mercado de biocombustível no Brasil. In: CONGRESSO DA REDE BRASILEIRA DE TECNOLOGIA DE BIODIESEL, 2., 2007, Brasília. Livro de resumos... Brasília, DF: ABIPTI, 2007. p. 76-77.| Biblioteca(s): Embrapa Meio Ambiente. |
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| 65. | | TATSCH, J. D.; ROCHA, H. R.; CABRAL, O. M. R.; FREITAS, H. C.; LLOPART, M.; ACOSTA, R.; LIGO, M. A. V. Avaliação do método de Multiple Imputation no preenchimento de falhas de fluxos de energia sobre uma área de cana-de-açúcar. In: BRAZILIAN MICROMETEOROLOGY WORKSHOP, 5., 2007, Santa Maria. Abstracts... Santa Maria: Universidade Federal de Santa Maria, 2007. CD-ROM.| Biblioteca(s): Embrapa Meio Ambiente. |
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| 67. | | PUGA, A. P.; QUEIROZ, M. C. de A.; LIGO, M. A. V.; CARVALHO, C. S.; PIRES, A. M. M.; SANTOS, J. de O.; ANDRADE, C. A. de. Nitrogen availability and ammonia volatilization in biochar-based fertilizers. Archives of Agronomy and Soil Science, v. 66, n. 7, p. 992-1004, 2020. Arquivo com texto completo contém a versão publicada online, sem dados de volume e paginação.| Biblioteca(s): Embrapa Meio Ambiente. |
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| 68. | | HERMES, L. C.; LIGO, M. A. V.; SOUZA, M. D. de; VIEIRA, S. R.; ABAKERLY, R. B.; CASTRO, O. M. de. Perda por defluvio superficial de 2,4D, atrazina, aldicarb sulfoxido e trifluralina em solo podzolico vermelho amarelo. IN: CONGRESSO BRASILEIRO DE CIÊNÇIA DO SOLO, 25., Viçosa, MG. Resumos expandidos. Viçosa: UFV, 1995. v.4, p. 2415-2416.| Biblioteca(s): Embrapa Tabuleiros Costeiros. |
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| 70. | | LIMA, M. A. de; NEVES, M. C.; PESSOA, M. C. P. Y.; HERMES, L. C.; LIGO, M. A. V.; CABRAL, O. Emissao de metano proveniente do cultivo de arroz irrigado no estado do Rio Grande do Sul, Brasil. Revista Cientifica Rural, v.3, n.2, p.61-67, 1998.| Biblioteca(s): Embrapa Meio Ambiente. |
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| 71. | | CABRAL, O. M. R.; ROCHA, H. R. da; GASH, J. H. C.; LIGO, M. A. V.; FREITAS, H. C. de; TATSCH, J. D. The energy and water balance of a Eucalyptus plantation in southeast Brazil. Journal of Hydrology, Amsterdam, v. 388, p. 208-216, 2010.| Biblioteca(s): Embrapa Meio Ambiente. |
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| 72. | | TATSCH, J. D.; CABRAL, O. M. R.; MORIONDO, M.; BINDI, M.; ROCHA, H. R. da; LIGO, M. A. V.; FREITAS, H. C. de. Implementação de um modelo genérico de culturas para a cana-de-açúcar no sudeste do Brasil. In: LIMA, M. A.; BODDEY, R. M.; ALVES, B. J. R.; MACHADO, P. L. O. de A.; URQUIAGA, S. (Ed.). Estoques de carbono e emissões de gases de efeito estufa na agropecuária brasileira. Brasília, DF: Embrapa; Jaguariúna: Embrapa Meio Ambiente, 2012. p. 223-237.| Biblioteca(s): Embrapa Meio Ambiente. |
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| 73. | | TATSCH, J. D.; CABRAL, O. M. R.; MORIONDO, M.; BINDI, M.; ROCHA, H. R. da; LIGO, M. A. V.; FREITAS, H. C. de. Implementation of a genetic model for sugarcane crops in the Southeastern region of Brazil. In: BODDEY, R. M.; LIMA, M. A.; ALVES, B. J. R.; MACHADO, P. L. O. de A.; URQUIAGA, S. (Ed.). Carbon stocks and greenhouse gas emissions in Brazilian agriculture. Brasília, DF: Embrapa, 2014. Chapter 7.| Biblioteca(s): Embrapa Meio Ambiente. |
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| 74. | | LIMA, M. A. de; BOEIRA, R. C.; CASTRO, V. L. S. S. de; LIGO, M. A. V.; CABRAL, O. M. R.; VIEIRA, R. F.; LUIZ, A. J. B. Estimativa das emissões de gases de efeito estufa provenientes de atividades agrícolas no Brasil. In: LIMA, M. A. de; CABRAL, O. M. R.; GONZALEZ MIGUEZ, J. D. (Ed.). Mudanças climáticas globais e a agropecuária brasileira. Jaguariúna: Embrapa Meio Ambiente, 2001. 397p. Cap. 7, p.169-189.| Biblioteca(s): Embrapa Meio Ambiente. |
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| 75. | | CABRAL, O. M. R.; GASH, J. H. C.; ROCHA, H. R. da; MARSDEN, C.; LIGO, M. A. V.; FREITAS, H. C. de; TATSCH, J. D.; GOMES, E. Fluxes of CO2 above a plantation of Eucalyptus in southeast Brazil. Agricultural and Forest Meteorology, v. 151, p. 49?59, 2011.| Biblioteca(s): Embrapa Meio Ambiente. |
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| 79. | | LIMA, M. A. de; ALVES, B. J. R.; PESSOA, M. C. P. Y.; LIGO, M. A. V.; VILLELA, O. V.; CARVALHO, E. C. de. Preparação de relatórios de referência sobre emissões de gases de efeito estufa por atividades agropecuárias (pecuária, dejetos animais, arroz irrigado, queima de resíduos agrícolas e solos agrícolas) para o Estado de São Paulo no período de 1990 a 2006. In: FÓRUM DE APRESENTAÇÃO DE RESULTADOS DE PESQUISA: AVANÇOS E OPORTUNIDADES, 1., 2014, Campinas. Anais... Jaguariúna: Embrapa Meio Ambiente, 2014. RE019. 3 p.| Biblioteca(s): Embrapa Meio Ambiente. |
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| 80. | | RODRIGUES, G. S.; RODRIGUES, I. A.; BUSCHINELLI, C. C. de A.; LIGO, M. A. V.; PIRES, A. M. M.; FRIGHETTO, R. T. S.; IRIAS, L. J. M. Socio-environmental impact of biodiesel production in Brazil. Journal of Technology Management & Innovation, v.2, n.2, p.46-65, 2007.| Biblioteca(s): Embrapa Meio Ambiente. |
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| Registros recuperados : 97 | |
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Registro Completo
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Biblioteca(s): |
Embrapa Meio Ambiente. |
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Data corrente: |
04/01/2019 |
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Data da última atualização: |
30/01/2019 |
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Tipo da produção científica: |
Resumo em Anais de Congresso |
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Autoria: |
PUGA, A. P.; CARVALHO, C. S.; LIGO, M. A. V.; PIRES, A. M. M.; PEREIRA NETO, B. G.; ANDRADE, C. A. de. |
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Afiliação: |
Aline Peregrina Puga; Cristina Silva Carvalho, UEMA; MARCOS ANTONIO VIEIRA LIGO, CNPMA; ADRIANA MARLENE MORENO PIRES, CNPMA; Braulio Garcia Pereira Neto, Carbosolo Desenvolvimento Agrícola; CRISTIANO ALBERTO DE ANDRADE, CNPMA. |
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Título: |
Ammonia volatilization from nitrogen fertilizer formulated with biochar. |
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Ano de publicação: |
2018 |
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Fonte/Imprenta: |
In: WORLD CONGRESS OF SOIL SCIENCE, 21., 2018, Rio de Janeiro. Soil science: beyond food and fuel: abstracts. Viçosa, MG: SBCS, 2018. Trabalho 959. |
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Idioma: |
Português |
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Conteúdo: |
Ammonia (NH3) volatilization results in low N use efficiency by crops. The aim of this study were to evaluate NH3 volatilization from nitrogen fertilizer formulated (F) with biochar (BC). In a incubation experiment the fertilizers were applied to soil surface. NH3 volatilized was captured by H2SO4 solution. BC used in the production of fertilizers is from eucalyptus (charcoal fines). Two types of formulated fertilizers were tested: granulated (F6 and F8; mixture of BC, urea and additives) and coated granulated fertilizers (F17 and F19; coating of urea granule with BC, acidified or not, and additives). Treatments tested were: 1) blank; 2) control; 3) soil + urea; 4) soil + F6 (10% N, 51% BC); 5) soil + F8 (20% N, 29% BC); 6) soil + F17 (20% N, 29% BC) and 7) soil + F19 (32% N, 20% BC). Granulated fertilizers (F6 and F8) and F17 coated fertilizer volatilized lower amounts of NH3 than urea, indicating greater efficiency when applied to the surface. In the case of F17, where the BC was previously acidified prior covering urea granule, acidification must have influenced the reduction of NH3 losses. In total urea volatilized 71% of N applied while F6 and F8 showed losses of 60% and 66%, respectively. F8 was produced with 20% N and 29% BC, while F6 with the lowest NH3 loss had 10% N and 51% BC. Proportion of BC in the fertilizer and the BC/N ratio appear as important in reducing N loss by NH3 volatilization. F19 showed worse performance than urea, volatilizing 80% of the applied N. However, F17 which was coated with previously acidified BC, presented lower volatilization (64%) compared to F19 and urea. In the equations of first-order chemical kinetics model describing the urea NH3 volatilization process of BC granulated and BC-coated fertilizers, it was found that the lowest N0 values (indicates the stabilization value of the volatilization process) belong to F6 and F8 (@64%), 12% lower than urea (N0=73%). It was observed that the highest value of N0 was of F19 (84%), confirming the BC alkalinity effect (pH@ 7.7) favoring N losses when fertilizer production technology was the coating of urea granule with BC without prior acidification. F6 and F8 tested in this study demonstrated potential to be applied in top dressing fertilization, due to lower volatilization rates, providing lower risk of N losses due to volatilization of NH3. Granulated F6 and coated F17 provided reductions between 10 and 15% for NH3 losses compared to urea. MenosAmmonia (NH3) volatilization results in low N use efficiency by crops. The aim of this study were to evaluate NH3 volatilization from nitrogen fertilizer formulated (F) with biochar (BC). In a incubation experiment the fertilizers were applied to soil surface. NH3 volatilized was captured by H2SO4 solution. BC used in the production of fertilizers is from eucalyptus (charcoal fines). Two types of formulated fertilizers were tested: granulated (F6 and F8; mixture of BC, urea and additives) and coated granulated fertilizers (F17 and F19; coating of urea granule with BC, acidified or not, and additives). Treatments tested were: 1) blank; 2) control; 3) soil + urea; 4) soil + F6 (10% N, 51% BC); 5) soil + F8 (20% N, 29% BC); 6) soil + F17 (20% N, 29% BC) and 7) soil + F19 (32% N, 20% BC). Granulated fertilizers (F6 and F8) and F17 coated fertilizer volatilized lower amounts of NH3 than urea, indicating greater efficiency when applied to the surface. In the case of F17, where the BC was previously acidified prior covering urea granule, acidification must have influenced the reduction of NH3 losses. In total urea volatilized 71% of N applied while F6 and F8 showed losses of 60% and 66%, respectively. F8 was produced with 20% N and 29% BC, while F6 with the lowest NH3 loss had 10% N and 51% BC. Proportion of BC in the fertilizer and the BC/N ratio appear as important in reducing N loss by NH3 volatilization. F19 showed worse performance than urea, volatilizing 80% of the applied N.... Mostrar Tudo |
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Palavras-Chave: |
Increased efficiency; Mitigation; N losses; NH3. |
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Categoria do assunto: |
P Recursos Naturais, Ciências Ambientais e da Terra |
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URL: |
https://ainfo.cnptia.embrapa.br/digital/bitstream/item/190309/1/RA-LigoMAV-et-al-21WCSS-2018-Trabalho-959.pdf
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Marc: |
LEADER 03188nam a2200217 a 4500
001 2103028
005 2019-01-30
008 2018 bl uuuu u00u1 u #d
100 1 $aPUGA, A. P.
245 $aAmmonia volatilization from nitrogen fertilizer formulated with biochar.$h[electronic resource]
260 $aIn: WORLD CONGRESS OF SOIL SCIENCE, 21., 2018, Rio de Janeiro. Soil science: beyond food and fuel: abstracts. Viçosa, MG: SBCS, 2018. Trabalho 959.$c2018
520 $aAmmonia (NH3) volatilization results in low N use efficiency by crops. The aim of this study were to evaluate NH3 volatilization from nitrogen fertilizer formulated (F) with biochar (BC). In a incubation experiment the fertilizers were applied to soil surface. NH3 volatilized was captured by H2SO4 solution. BC used in the production of fertilizers is from eucalyptus (charcoal fines). Two types of formulated fertilizers were tested: granulated (F6 and F8; mixture of BC, urea and additives) and coated granulated fertilizers (F17 and F19; coating of urea granule with BC, acidified or not, and additives). Treatments tested were: 1) blank; 2) control; 3) soil + urea; 4) soil + F6 (10% N, 51% BC); 5) soil + F8 (20% N, 29% BC); 6) soil + F17 (20% N, 29% BC) and 7) soil + F19 (32% N, 20% BC). Granulated fertilizers (F6 and F8) and F17 coated fertilizer volatilized lower amounts of NH3 than urea, indicating greater efficiency when applied to the surface. In the case of F17, where the BC was previously acidified prior covering urea granule, acidification must have influenced the reduction of NH3 losses. In total urea volatilized 71% of N applied while F6 and F8 showed losses of 60% and 66%, respectively. F8 was produced with 20% N and 29% BC, while F6 with the lowest NH3 loss had 10% N and 51% BC. Proportion of BC in the fertilizer and the BC/N ratio appear as important in reducing N loss by NH3 volatilization. F19 showed worse performance than urea, volatilizing 80% of the applied N. However, F17 which was coated with previously acidified BC, presented lower volatilization (64%) compared to F19 and urea. In the equations of first-order chemical kinetics model describing the urea NH3 volatilization process of BC granulated and BC-coated fertilizers, it was found that the lowest N0 values (indicates the stabilization value of the volatilization process) belong to F6 and F8 (@64%), 12% lower than urea (N0=73%). It was observed that the highest value of N0 was of F19 (84%), confirming the BC alkalinity effect (pH@ 7.7) favoring N losses when fertilizer production technology was the coating of urea granule with BC without prior acidification. F6 and F8 tested in this study demonstrated potential to be applied in top dressing fertilization, due to lower volatilization rates, providing lower risk of N losses due to volatilization of NH3. Granulated F6 and coated F17 provided reductions between 10 and 15% for NH3 losses compared to urea.
653 $aIncreased efficiency
653 $aMitigation
653 $aN losses
653 $aNH3
700 1 $aCARVALHO, C. S.
700 1 $aLIGO, M. A. V.
700 1 $aPIRES, A. M. M.
700 1 $aPEREIRA NETO, B. G.
700 1 $aANDRADE, C. A. de
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