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| Registros recuperados : 7 | |
| 2. |  | LANGE, A.; MARTINES, A. M.; SILVA, M. A. C. da; SORREANO, M. C. M.; CABRAL, C. P.; MALAVOLTA, E. Efeito de deficiência de micronutrientes no estado nutricional da mamoneira cultivar Iris. Pesquisa Agropecuária Brasileira, Brasília, DF, v. 40, n. 1, p. 61-67, jan. 2005 Título em inglês: Micronutrient deficiency effect on the nutritional status of the castor bean cultivar Iris.| Biblioteca(s): Embrapa Unidades Centrais. |
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| 3. | | NAKATANI, A. S.; MARTINES, A. M.; NOGUEIRA, M. A.; FAGOTTI, D. S. L.; OLIVEIRA, A. G.; BINI, D.; SOUSA, J. P.; CARDOSO, E. J. B. N. Changes in the genetic structure of Bacteria and microbial activity in an agricultural soil amended with tannery sludge. Soil Biology & Biochemistry, v. 43, n.1, p. 106-114, Jan. 2011.| Biblioteca(s): Embrapa Soja. |
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| 4. | | BATISTA JÚNIOR, C. B.; ALBINO, U. B.; MARTINES, A. M.; SARIDAKIS, D. P.; MATSUMOTO, L. S.; AVANZI, M. A.; ANDRADE, G. Efeito fungistático de Bacillus thuringiensis e de outras bactérias sobre alguns fungos fitopatogênicos. Pesquisa Agropecuária Brasileira, Brasília, DF, v. 37, n. 8, p. 1189-1194, ago. 2002 Notas Científicas.
Título em inglês: Fungistatic effect of Bacillus thuringiensis and of other bacteria on some plant pathogenic fungi.| Biblioteca(s): Embrapa Unidades Centrais. |
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| 5. | | NAKATANI, A. S.; NOGUEIRA, M. A.; MARTINES, A. M.; SANTOS, C. A. dos; BALDESIN, L. F.; MARSCHNER, P.; CARDOSO, E. J. B. N. Effects of tannery sludge application on physiological and fatty acid profiles of the soil microbial community. Applied Soil Ecology, v. 61, p. 92-99, 2012.| Biblioteca(s): Embrapa Soja. |
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| 6. | | NIEMEYER, J. C.; CARDOSO, E. J. B. N.; NUNES, M. E. T.; ALVES, P. R. L.; MARTINES, A. M.; ANDRÉA, M. M. de; BROWN, G. G.; NIVA, C. C. Preparo do substrato teste. In: NIVA, C. C.; BROWN, G. G. (Ed.). Ecotoxicologia terrestre: métodos e aplicações dos ensaios com oligoquetas. Brasília, DF: Embrapa, 2019. Cap. 7, p. 143-151.| Biblioteca(s): Embrapa Cerrados; Embrapa Florestas. |
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| 7. | | SANTOS, C. A.; PANCHONI, L. C.; BINI, D.; KUWANO, B. H.; CARMO, K. B.; SILVA, S. M. C. P.; MARTINES, A. M.; ANDRADE, G.; ANDRADE, D. S.; CARDOSO, E. J. B. N.; ZANGARO, W.; NOGUEIRA, M. A. Land application of municipal landfill leachate: fate of ions and ammonia volatilization. Journal of Environmental Quality, v. 42, n. 2, p. 523-531, Mar./Apr. 2013.| Biblioteca(s): Embrapa Soja. |
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 | Acesso ao texto completo restrito à biblioteca da Embrapa Soja. Para informações adicionais entre em contato com valeria.cardoso@embrapa.br. |
Registro Completo
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Biblioteca(s): |
Embrapa Soja. |
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Data corrente: |
02/12/2013 |
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Data da última atualização: |
02/02/2017 |
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Tipo da produção científica: |
Artigo em Periódico Indexado |
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Circulação/Nível: |
A - 1 |
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Autoria: |
SANTOS, C. A.; PANCHONI, L. C.; BINI, D.; KUWANO, B. H.; CARMO, K. B.; SILVA, S. M. C. P.; MARTINES, A. M.; ANDRADE, G.; ANDRADE, D. S.; CARDOSO, E. J. B. N.; ZANGARO, W.; NOGUEIRA, M. A. |
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Afiliação: |
USP; UEL; USP; UEL; UEL; UEL; USP; UEL; IAPAR; USP; UEL; MARCO ANTONIO NOGUEIRA, CNPSO. |
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Título: |
Land application of municipal landfill leachate: fate of ions and ammonia volatilization. |
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Ano de publicação: |
2013 |
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Fonte/Imprenta: |
Journal of Environmental Quality, v. 42, n. 2, p. 523-531, Mar./Apr. 2013. |
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DOI: |
10.2134/jeq2012.0170 |
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Idioma: |
Inglês |
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Conteúdo: |
Landfill leachates are pollutants rich in ammoniacal N, Na, and K, but land application potentially offers an alternative for recycling these leachate nutrients. We applied landfill leachate corresponding to 0, 110, 220, 330, and 440 kg ha?1 of total N, divided in three applications ( July, August, and October 2008), onto the surface of an acidic (pH 5.5?6.0) clay (79% clay) Ultisol and monitored NH3 volatilization just after applications and microbiological (0?10 cm) and chemical attributes (0?60-cm soil depth) in August 2008,
January 2009, and May 2009. Ammonium (up to 30 mg kg?1), NO3 ? (up to 160 mg kg?1), Na, K (up to 1.1 cmolc kg?1 each), and electrical conductivity (up to 1 dS m?1) increased transiently in soil following applications. Despite >90% of the total leachate N being ammoniacal, NO3 ? predominated in the first soil sampling, 14 d after the second application, suggesting fast nitrification, but it decreased in the soil profile thereafter. From 5 to 25% of the total applied N volatilized as NH3, with maximum losses within the first
3 d. Applications inhibited (50%) the relative nitrification rate and increased (50%) hot-water-soluble carbohydrates in the soil at the highest rate. No effects were observed on soil microbial biomass C (114?205 mg kg?1) and activity (5?8 mg CO2?C kg?1 d?1) or on corn grain yields (6349?7233 kg ha?1). Controlled land application seems to be a viable alternative for landfill leachate management, but NO3 ? leaching, NH3 volatilization, and accumulation of salinizing ions must be monitored in the long term to prevent
environmental degradation. MenosLandfill leachates are pollutants rich in ammoniacal N, Na, and K, but land application potentially offers an alternative for recycling these leachate nutrients. We applied landfill leachate corresponding to 0, 110, 220, 330, and 440 kg ha?1 of total N, divided in three applications ( July, August, and October 2008), onto the surface of an acidic (pH 5.5?6.0) clay (79% clay) Ultisol and monitored NH3 volatilization just after applications and microbiological (0?10 cm) and chemical attributes (0?60-cm soil depth) in August 2008,
January 2009, and May 2009. Ammonium (up to 30 mg kg?1), NO3 ? (up to 160 mg kg?1), Na, K (up to 1.1 cmolc kg?1 each), and electrical conductivity (up to 1 dS m?1) increased transiently in soil following applications. Despite >90% of the total leachate N being ammoniacal, NO3 ? predominated in the first soil sampling, 14 d after the second application, suggesting fast nitrification, but it decreased in the soil profile thereafter. From 5 to 25% of the total applied N volatilized as NH3, with maximum losses within the first
3 d. Applications inhibited (50%) the relative nitrification rate and increased (50%) hot-water-soluble carbohydrates in the soil at the highest rate. No effects were observed on soil microbial biomass C (114?205 mg kg?1) and activity (5?8 mg CO2?C kg?1 d?1) or on corn grain yields (6349?7233 kg ha?1). Controlled land application seems to be a viable alternative for landfill leachate management, but NO3 ? leaching, NH3 volatilizatio... Mostrar Tudo |
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Palavras-Chave: |
Volatização de amônia. |
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Categoria do assunto: |
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Marc: |
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100 1 $aSANTOS, C. A.
245 $aLand application of municipal landfill leachate$bfate of ions and ammonia volatilization.$h[electronic resource]
260 $c2013
520 $aLandfill leachates are pollutants rich in ammoniacal N, Na, and K, but land application potentially offers an alternative for recycling these leachate nutrients. We applied landfill leachate corresponding to 0, 110, 220, 330, and 440 kg ha?1 of total N, divided in three applications ( July, August, and October 2008), onto the surface of an acidic (pH 5.5?6.0) clay (79% clay) Ultisol and monitored NH3 volatilization just after applications and microbiological (0?10 cm) and chemical attributes (0?60-cm soil depth) in August 2008, January 2009, and May 2009. Ammonium (up to 30 mg kg?1), NO3 ? (up to 160 mg kg?1), Na, K (up to 1.1 cmolc kg?1 each), and electrical conductivity (up to 1 dS m?1) increased transiently in soil following applications. Despite >90% of the total leachate N being ammoniacal, NO3 ? predominated in the first soil sampling, 14 d after the second application, suggesting fast nitrification, but it decreased in the soil profile thereafter. From 5 to 25% of the total applied N volatilized as NH3, with maximum losses within the first 3 d. Applications inhibited (50%) the relative nitrification rate and increased (50%) hot-water-soluble carbohydrates in the soil at the highest rate. No effects were observed on soil microbial biomass C (114?205 mg kg?1) and activity (5?8 mg CO2?C kg?1 d?1) or on corn grain yields (6349?7233 kg ha?1). Controlled land application seems to be a viable alternative for landfill leachate management, but NO3 ? leaching, NH3 volatilization, and accumulation of salinizing ions must be monitored in the long term to prevent environmental degradation.
653 $aVolatização de amônia
700 1 $aPANCHONI, L. C.
700 1 $aBINI, D.
700 1 $aKUWANO, B. H.
700 1 $aCARMO, K. B.
700 1 $aSILVA, S. M. C. P.
700 1 $aMARTINES, A. M.
700 1 $aANDRADE, G.
700 1 $aANDRADE, D. S.
700 1 $aCARDOSO, E. J. B. N.
700 1 $aZANGARO, W.
700 1 $aNOGUEIRA, M. A.
773 $tJournal of Environmental Quality$gv. 42, n. 2, p. 523-531, Mar./Apr. 2013.
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