| |
|
|
 | Acesso ao texto completo restrito à biblioteca da Embrapa Florestas. Para informações adicionais entre em contato com cnpf.biblioteca@embrapa.br. |
|
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 |
|
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.
Download
Esconder MarcMostrar Marc Completo |
|
Registro original: |
Embrapa Florestas (CNPF) |
|
|
Biblioteca |
ID |
Origem |
Tipo/Formato |
Classificação |
Cutter |
Registro |
Volume |
Status |
URL |
Voltar
|
|
|
Registro Completo
|
Biblioteca(s): |
Embrapa Semiárido. |
|
Data corrente: |
09/08/2016 |
|
Data da última atualização: |
26/01/2017 |
|
Tipo da produção científica: |
Artigo em Periódico Indexado |
|
Circulação/Nível: |
B - 4 |
|
Autoria: |
RESENDE, G. M. de; COSTA, N. D.; YURI, J. E. |
|
Afiliação: |
GERALDO MILANEZ DE RESENDE, CPATSA; NIVALDO DUARTE COSTA, CPATSA; JONY EISHI YURI, CPATSA. |
|
Título: |
Doses de nitrogênio na produtividade e classificação de bulbos de cultivares de cebola. |
|
Ano de publicação: |
2016 |
|
Fonte/Imprenta: |
Revista Brasileira de Agricultura Irrigada, Fortaleza, v. 10, n. 3, p. 605-613, 2016. |
|
DOI: |
10.7127/rbai.v10n300373 |
|
Idioma: |
Português |
|
Conteúdo: |
Os elementos mais absorvidos em termos de porcentagem na matéria seca da cebola são o potássio e nitrogênio. Como o objetivo de avaliar a produtividade e classificação de bulbos de cultivares de cebola em função de doses de nitrogênio foi conduzido um experimento no período de junho a setembro de 2013, em Petrolina-PE. O delineamento experimental utilizado foi de blocos ao acaso no esquema fatorial 5x2, compreendendo cinco doses de nitrogênio (0; 60; 120, 180 e 240 kg ha-1) e duas cultivares (Brisa IPA-12 e Vale Ouro IPA-11), com três repetições. A cultivar Brisa IPA-12 (80,7 t ha-1) foi superior a cultivar Vale Ouro IPA-11 (77,0 t ha-1). A dose de 183,2 kg ha-1 de N promoveu a maior produtividade comercial (94,7 t ha-1). A cultivar Brisa IPA-12 apresentou maior produção de refugos (2,4 t ha-1) comparativamente a cultivar Vale Ouro IPA-11 (1,1 t ha-1). Verificou-se com o aumento das doses uma redução gradativa da produção de bulbos considerados não comerciais, sendo a menor produção de refugos estimada na dose de 167,7 kg ha-1 de N. Maior massa fresca e bulbos de diâmetro superior foram obtidos com o incremento das doses de nitrogênio |
|
Palavras-Chave: |
Massa fresca de bulbo; Onion. |
|
Thesagro: |
Adubação; Allium Cepa; Bulbo; Cebola; Nitrogênio; Nutrição. |
|
Thesaurus NAL: |
Nutrients. |
|
Categoria do assunto: |
A Sistemas de Cultivo |
|
URL: |
https://ainfo.cnptia.embrapa.br/digital/bitstream/item/146189/1/Milanez-2016.pdf
|
|
Marc: |
LEADER 01946naa a2200265 a 4500
001 2050526
005 2017-01-26
008 2016 bl uuuu u00u1 u #d
024 7 $a10.7127/rbai.v10n300373$2DOI
100 1 $aRESENDE, G. M. de
245 $aDoses de nitrogênio na produtividade e classificação de bulbos de cultivares de cebola.$h[electronic resource]
260 $c2016
520 $aOs elementos mais absorvidos em termos de porcentagem na matéria seca da cebola são o potássio e nitrogênio. Como o objetivo de avaliar a produtividade e classificação de bulbos de cultivares de cebola em função de doses de nitrogênio foi conduzido um experimento no período de junho a setembro de 2013, em Petrolina-PE. O delineamento experimental utilizado foi de blocos ao acaso no esquema fatorial 5x2, compreendendo cinco doses de nitrogênio (0; 60; 120, 180 e 240 kg ha-1) e duas cultivares (Brisa IPA-12 e Vale Ouro IPA-11), com três repetições. A cultivar Brisa IPA-12 (80,7 t ha-1) foi superior a cultivar Vale Ouro IPA-11 (77,0 t ha-1). A dose de 183,2 kg ha-1 de N promoveu a maior produtividade comercial (94,7 t ha-1). A cultivar Brisa IPA-12 apresentou maior produção de refugos (2,4 t ha-1) comparativamente a cultivar Vale Ouro IPA-11 (1,1 t ha-1). Verificou-se com o aumento das doses uma redução gradativa da produção de bulbos considerados não comerciais, sendo a menor produção de refugos estimada na dose de 167,7 kg ha-1 de N. Maior massa fresca e bulbos de diâmetro superior foram obtidos com o incremento das doses de nitrogênio
650 $aNutrients
650 $aAdubação
650 $aAllium Cepa
650 $aBulbo
650 $aCebola
650 $aNitrogênio
650 $aNutrição
653 $aMassa fresca de bulbo
653 $aOnion
700 1 $aCOSTA, N. D.
700 1 $aYURI, J. E.
773 $tRevista Brasileira de Agricultura Irrigada, Fortaleza$gv. 10, n. 3, p. 605-613, 2016.
Download
Esconder MarcMostrar Marc Completo |
|
Registro original: |
Embrapa Semiárido (CPATSA) |
|
|
Biblioteca |
ID |
Origem |
Tipo/Formato |
Classificação |
Cutter |
Registro |
Volume |
Status |
Fechar
|
| Nenhum registro encontrado para a expressão de busca informada. |
|
|
