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Registros recuperados : 669 | |
421. | | SANTOS, S. A.; COSTA, C.; SOUZA, G. da S. e; MORAES, A. S.; ARRIGONI, M. De B. Qualidade da dieta selecionada por bovinos na sub-regiao da Nhecolandia, Pantanal. Revista Brasileira de Zootecnia, v.31, n.4, p.1663-1673, jul./ago. 2002. Biblioteca(s): Embrapa Pantanal. |
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422. | | BULLER, L. S.; LIMA, I. B. T. de; ORTEGA, E.; MORAES, A.; SILVA, G. B. S. da; ZANETTI, M. R. Soil improvement and mitigation of greenhouse gas emissions for integrated crop-livestock systems: Case study assessment in the Pantanal savanna highland, Brazil. Agricultural Systems, v. 137, p. 206-219, 2015. Biblioteca(s): Embrapa Territorial. |
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424. | | SILVA, B. E. S.; FARIAS, P. H. S.; SILVA, S. C. da; MORAES, A. da C.; HEINEMANN, A. B. Tendências e projeções da temperatura do ar no Estado de Goiás. In: SEMINÁRIO JOVENS TALENTOS, 11., 2017, Santo Antônio de Goiás. Coletânea dos resumos apresentados. Santo Antônio de Goiás: Embrapa Arroz e Feijão, 2017. p. 46. (Embrapa Arroz e Feijão. Documentos, 316). Biblioteca(s): Embrapa Arroz e Feijão. |
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425. | | PIVA, J. T.; DIECKOW, J.; BAYER, C.; ZANATTA, J. A.; MORAES, A. de; PAULETTI, V.; TOMAZI, M.; PERGHER, M. No-till reduces global warming potential in a subtropical Ferralsol. Plant and Soil, v. 361, p. 359-373, 2012. Biblioteca(s): Embrapa Florestas. |
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426. | | TOSTO, S. G.; MOTTA, R. S. da; ORTIZ, R. A.; KITAMURA, P. C.; COELHO, R.; MORAES, A. S.; RODIGHERI, H. Valoração ambiental de sistemas de manejo de solo: o caso do plantio direto na região do planalto médio, RS. Rio de Janeiro: Embrapa Solos, 2003. 29 p. (Embrapa Solos. Boletim de pesquisa e desenvolvimento, 35). Biblioteca(s): Embrapa Pantanal. |
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427. | | SANTOS FILHO, R. R.; MORAES, A. da C.; SCHUSTER, L. G.; SILVA, M. A. S. da; NOGUEIRA, L. C. Uso de geotecnologias para gestão de campos experimentais: um estudo de caso. In: SEMINÁRIO DO PROGRAMA INSTITUCIONAL DE BOLSAS DE INICIAÇÃO CIENTÍFICA-CNPQ, 6.; SEMINÁRIO DE PROGRAMAS DE BOLSAS DE INICIAÇÃO CIENTÍFICA-UNIT, 11.; SEMINÁRIO DO PROGRAMA INSTITUCIONAL DE BOLSAS DE INICIAÇÃO CIENTÍFICA-FAPITEC, 1., 2009, Aracaju. Seminários de iniciação científica da UNIT: anais. Aracaju: UNIT, 2009. 1 CD-ROM. p. 269 Resumo em anais. Biblioteca(s): Embrapa Tabuleiros Costeiros. |
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428. | | SOUZA, A. P. de; GONZALES, J. C.; RAMOS, C. I.; PALOSCHI, C. G.; MORAES, A. N. de. Variação Sazonal de Boophilus Microplus no Planalto Catarinense. Pesquisa Agropecuária Brasileira, Brasília, v.23, n.6, p.627-630, jun. 1988. Biblioteca(s): Embrapa Unidades Centrais. |
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430. | | BALBINOT JUNIOR, A. A.; VEIGA, M. da; MORAES, A. de; PELISSARI, A.; MAFRA, A. L.; DELA PICCOLLA, C. Winter pasture and cover crops and their effects on soil and summer grain crops. Pesquisa agropecuária Brasileira, Brasília, DF, v. 46, n. 10, p. 1357 -1363, out. 2011 Título em português: Pastagem e coberturas de inverno e seus efeitos sobre o solo e culturas estivais. Biblioteca(s): Embrapa Unidades Centrais. |
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431. | | BALBINOT JUNIOR, A. A.; VEIGA, M. da; MORAES, A. de; PELISSARI, A.; MAFRA, A. L.; PICCOLLA, C. D. Winter pasture and cover crops and their effects on soil and summer grain crops. Pesquisa Agropecuária Brasileira, Brasília, DF, v. 46, n. 10, p. 1357-1363, out. 2011. Biblioteca(s): Embrapa Soja. |
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433. | | OLIVEIRA, E. J. de; GODOY, I. J. de; MORAES, A. R. A. de; MARTINS, A. L. M.; PEREIRA, J. C. V. N. A.; BORTOLETTO, N.; KASAI, F. S. Adaptabilidade e estabilidade de genótipos de amendoim de porte rasteiro. Pesquisa Agropecuária Brasileira, Brasília, DF, v. 41, n. 8, p. 1253-1260, ago. 2006 Título em inglês: Adaptability and stability of peanut genotypes of runner growth habit. Biblioteca(s): Embrapa Unidades Centrais. |
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434. | | SOUZA, K.; POLTRONIERI, L. S.; VERZIGNASSI, J. R.; BENCHIMOL, R. L.; SILVA, J. C. da; MORAES, A.; COSTA, R. C. da. Algas causando necrose foliar em helicônia no Pará. In: JORNADA DE INICIAÇÃO CIENTÍFICA DO PET, 2., 2007, Belém, PA. Iniciação científica e a formação profissional: anais. Belém, PA: PROEN/UFRA, 2007. 1 CD-ROM. Biblioteca(s): Embrapa Amazônia Oriental. |
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436. | | HOFFMANN, L. V.; MORAES, A. da C.; MENDES, L. de M. O.; COSTA, N. L. da; LIMA, M. M. de A. Algodão nativo do Brasil em perigo de extinção. Revista de Recursos Genéticos - RG News, v. 5, n. 2, p. 88, 2019. Resumos apresentado no SIMPÓSIO DA REDE DE RECURSOS GENÉTICOS VEGETAIS DO NORDESTE, 4., 2019, Areias. Anais... Biblioteca(s): Embrapa Algodão; Embrapa Arroz e Feijão. |
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437. | | SILVA, M. R.; PELISSARI, A.; MORAES, A. de; SANDINI, I. E.; CASSOL, L. C.; ASSMANN, T. S.; OLIVEIRA, E. B. de. Acumulação de nutrientes e produção forrageira de aveia e azevém em função da aplicação de calcário e gesso em superfície. Revista de Ciências Agrárias, Lisboa, v.38, n.3, p. 346-356, set. 2015. Biblioteca(s): Embrapa Florestas. |
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438. | | COSTA, N. de L.; MORAES, A. de; CARVALHO, F. C. F. de; MONTEIRO, A. L. G.; SILVA, A. L. P.; OLIVEIRA, R. A. de. Acúmulo de forragem e composição química de Trachypogon plumosus sob níveis de correção da fertilidade do solo. In: CONGRESSO BRASILEIRO DE ZOOTECNIA, 24., 2014, Vitória. A Zootecnia fazendo o Brasil crescer. Vitória, ES: UFES, 2014. Biblioteca(s): Embrapa Roraima. |
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439. | | COSTA, N. de L.; MORAES, A. de; CARVALHO, P. C. F. de; MAGALHAES, J. A.; RODRIGUES, B. H. N.; SANTOS, F. J. de S. Acúmulo de forragem e morfogênese de Axonopus aureus sob adubação potássica. Research, Society and Development, v. 8, n. 8, 2019. Biblioteca(s): Embrapa Meio-Norte; Embrapa Roraima. |
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440. | | COSTA, N. de L.; MORAES, A. de; CARVALHO, F. C. F. de; MONTEIRO, A. L. G.; SILVA, A. L. P.; OLIVEIRA, R. A. de. Acúmulo de forragem e morfogênese de Axonopus aureus sob níveis de adubação nitrogenada. In: CONGRESSO NORDESTINO DE PRODUÇÃO ANIMAL, 9., 2014, Ilhéus. Produção animal: novas diretrizes; trabalhos apresentados. Ilhéus: SNPA, 2014. 3 f. Biblioteca(s): Embrapa Roraima. |
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Registros recuperados : 669 | |
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Registro Completo
Biblioteca(s): |
Embrapa Florestas. |
Data corrente: |
10/11/2014 |
Data da última atualização: |
10/11/2014 |
Tipo da produção científica: |
Artigo em Periódico Indexado |
Circulação/Nível: |
A - 1 |
Autoria: |
SORDI, A.; DIECKOW, J.; BAYER, C.; ALBUQUERQUE, M. A.; PIVA, J. T.; ZANATTA, J. A.; TOMAZI, M.; ROSA, C. M. da; MORAES, A. de. |
Afiliação: |
ANDRÉ SORDI, Programa de Pós-Graduação em Ciência do Solo, UFPR; Jeferson Dieckow, UFPR; Cimélio Bayer, UFRGS; MÁRCIO AMARAL ALBUQUERQUE, Programa de pós-graduação em Ciência do Solo, UFPR; JONATAS THIAGO PIVA, UFSC; JOSILEIA ACORDI ZANATTA, CNPF; Michely Tomazi, UFRGS; CARLA MACHADO DA ROSA, UFRGS; Anibal de Moraes, UFPR. |
Título: |
Nitrous oxide emission factors for urine and dung patchesin a subtropical Brazilian pastureland. |
Ano de publicação: |
2014 |
Fonte/Imprenta: |
Agriculture, Ecosystems and Environment, v. 190, p. 94-103, 2014. |
Idioma: |
Inglês |
Conteúdo: |
tCattle urine and dung (faeces) patches are nitrous oxide (N2O) sources in pasturelands with impactsin the global N2O budget, but specific information about those emissions are still missing for Braziliansubtropical and tropical regions. We conducted a sequence of 3 field-trials (summer, winter and spring,90 days each) to evaluate the N2O emission and emission factor (EF) after the deposition of 3 volumes ofcattle urine or 3 weights of dung (½, 1 and 1½ time the mean urination volume or defecation weight ofFriesian cows) on a free-drained Cambisol of a subtropical pastureland of Brazil. The N2O emission peaks(3198 g N2O-N m−2h−1after urine in summer was the highest) occurred on average 17 ± 9 days afterapplication (DAA), both for urine and dung, and dropped to the background levels 41 ± 10 DAA of urineand 49 ± 10 DAA of dung. The highest contents of NH4+-N in soil (200?250 mg N kg−1) occurred one dayafter urine application and 10?14 days later for dung (100?200 mg N kg−1). Nitrate peaks occurred from23 to 26 DAA in urine patches (∼40?50 mg N kg−1) and 19?50 DAA in dung patches (∼40?50 mg N kg−1).The N2O emission peaks for urine coincided with soil NH4+-N peak in winter but with soil NO3−-N peakin spring. For dung, the emission peak seemed to be more associated with soil NO3−-N than to NH4+-N,either in winter or spring (inorganic-N was not assessed in summer). It was not possible to concludewhether nitrification or denitrification was the dominant process in N2O production, but it seemed thatboth played relevant roles. The EF for urine, averaged across the seasons, diminished with increments inurine volume, from 0.33% in ½ volume to 0.19% in 1½ volume, possibly because urine percolated deeperinto the soil and proportionally less N remained available for N2O production in the top layer. The EFfor dung was 0.19%, 0.12% and 0.14% for ½, 1 and 1½ weight, respectively, showing no clear trend withincrement in dung weight. The lowest EFs for urine and dung occurred in winter, possibly because oflowest temperatures and soil water-filled pore space. The average EF for dung (0.15%) was lower thanthat of urine (0.26%), because urea-N of urine is more readily available for the hydrolysis than organicN forms of dung. This result suggests that these two excreta should be addressed separately in nationalgreenhouse gases inventories or communications. Our results suggest that the default 2% EF proposed inIPCC Guidelines for cattle excreta are overestimated for subtropical Brazil. MenostCattle urine and dung (faeces) patches are nitrous oxide (N2O) sources in pasturelands with impactsin the global N2O budget, but specific information about those emissions are still missing for Braziliansubtropical and tropical regions. We conducted a sequence of 3 field-trials (summer, winter and spring,90 days each) to evaluate the N2O emission and emission factor (EF) after the deposition of 3 volumes ofcattle urine or 3 weights of dung (½, 1 and 1½ time the mean urination volume or defecation weight ofFriesian cows) on a free-drained Cambisol of a subtropical pastureland of Brazil. The N2O emission peaks(3198 g N2O-N m−2h−1after urine in summer was the highest) occurred on average 17 ± 9 days afterapplication (DAA), both for urine and dung, and dropped to the background levels 41 ± 10 DAA of urineand 49 ± 10 DAA of dung. The highest contents of NH4+-N in soil (200?250 mg N kg−1) occurred one dayafter urine application and 10?14 days later for dung (100?200 mg N kg−1). Nitrate peaks occurred from23 to 26 DAA in urine patches (∼40?50 mg N kg−1) and 19?50 DAA in dung patches (∼40?50 mg N kg−1).The N2O emission peaks for urine coincided with soil NH4+-N peak in winter but with soil NO3−-N peakin spring. For dung, the emission peak seemed to be more associated with soil NO3−-N than to NH4+-N,either in winter or spring (inorganic-N was not assessed in summer). It was not possible to concludewhether nitrification or d... Mostrar Tudo |
Palavras-Chave: |
Fator de emissão; Óxido nitroso; Volume de urina. |
Thesagro: |
Gado; Nitrato; Pastagem. |
Categoria do assunto: |
-- |
Marc: |
LEADER 03383naa a2200289 a 4500 001 1999594 005 2014-11-10 008 2014 bl uuuu u00u1 u #d 100 1 $aSORDI, A. 245 $aNitrous oxide emission factors for urine and dung patchesin a subtropical Brazilian pastureland.$h[electronic resource] 260 $c2014 520 $atCattle urine and dung (faeces) patches are nitrous oxide (N2O) sources in pasturelands with impactsin the global N2O budget, but specific information about those emissions are still missing for Braziliansubtropical and tropical regions. We conducted a sequence of 3 field-trials (summer, winter and spring,90 days each) to evaluate the N2O emission and emission factor (EF) after the deposition of 3 volumes ofcattle urine or 3 weights of dung (½, 1 and 1½ time the mean urination volume or defecation weight ofFriesian cows) on a free-drained Cambisol of a subtropical pastureland of Brazil. The N2O emission peaks(3198 g N2O-N m−2h−1after urine in summer was the highest) occurred on average 17 ± 9 days afterapplication (DAA), both for urine and dung, and dropped to the background levels 41 ± 10 DAA of urineand 49 ± 10 DAA of dung. The highest contents of NH4+-N in soil (200?250 mg N kg−1) occurred one dayafter urine application and 10?14 days later for dung (100?200 mg N kg−1). Nitrate peaks occurred from23 to 26 DAA in urine patches (∼40?50 mg N kg−1) and 19?50 DAA in dung patches (∼40?50 mg N kg−1).The N2O emission peaks for urine coincided with soil NH4+-N peak in winter but with soil NO3−-N peakin spring. For dung, the emission peak seemed to be more associated with soil NO3−-N than to NH4+-N,either in winter or spring (inorganic-N was not assessed in summer). It was not possible to concludewhether nitrification or denitrification was the dominant process in N2O production, but it seemed thatboth played relevant roles. The EF for urine, averaged across the seasons, diminished with increments inurine volume, from 0.33% in ½ volume to 0.19% in 1½ volume, possibly because urine percolated deeperinto the soil and proportionally less N remained available for N2O production in the top layer. The EFfor dung was 0.19%, 0.12% and 0.14% for ½, 1 and 1½ weight, respectively, showing no clear trend withincrement in dung weight. The lowest EFs for urine and dung occurred in winter, possibly because oflowest temperatures and soil water-filled pore space. The average EF for dung (0.15%) was lower thanthat of urine (0.26%), because urea-N of urine is more readily available for the hydrolysis than organicN forms of dung. This result suggests that these two excreta should be addressed separately in nationalgreenhouse gases inventories or communications. Our results suggest that the default 2% EF proposed inIPCC Guidelines for cattle excreta are overestimated for subtropical Brazil. 650 $aGado 650 $aNitrato 650 $aPastagem 653 $aFator de emissão 653 $aÓxido nitroso 653 $aVolume de urina 700 1 $aDIECKOW, J. 700 1 $aBAYER, C. 700 1 $aALBUQUERQUE, M. A. 700 1 $aPIVA, J. T. 700 1 $aZANATTA, J. A. 700 1 $aTOMAZI, M. 700 1 $aROSA, C. M. da 700 1 $aMORAES, A. de 773 $tAgriculture, Ecosystems and Environment$gv. 190, p. 94-103, 2014.
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