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Registros recuperados : 138 | |
23. | ![Imagem marcado/desmarcado](/consulta/web/img/desmarcado.png) | CHIARADIA, J. J.; CHIBA, M. K.; ANDRADE, C. A. de; OLIVEIRA, C. de; LAVORENTI, A. Produtividade e nutrição de mamona cultivada em área de reforma de canavial tratada com lodo de esgoto. Revista Brasileira de Ciência do Solo, Viçosa, MG, v. 33, n.3, p. 701-709, mai./jun. 2009. Biblioteca(s): Embrapa Semiárido; Embrapa Solos / UEP-Recife. |
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25. | ![Imagem marcado/desmarcado](/consulta/web/img/desmarcado.png) | PUGA, A. P.; GRUTZMACHER, P.; CERRI, C. E. P.; RIBEIRINHO, V. S.; ANDRADE, C. A. de. Biochar-based nitrogen fertilizers: greenhouse gas emissions, use efficiency, and maize yield in tropical soils. Science of The Total Environment, v. 704, article 135375, 2019. Biblioteca(s): Embrapa Meio Ambiente. |
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27. | ![Imagem marcado/desmarcado](/consulta/web/img/desmarcado.png) | RAMOS, N. P.; ANDRADE, C. A. de; ROSSETO, R.; PIRES, A. M. M. A cana-de-açúcar e suas relações com a matéria orgânica do solo. In: BETTIOL, W.; SILVA, C. A.; CERRI, C. E. P.; MARTIN NETO, L.; ANDRADE, C. A. de (ed.). Entendendo a matéria orgânica do solo em ambientes tropical e subtropical. Brasília, DF: Embrapa, 2023. cap. 23; p. 645-675 Biblioteca(s): Embrapa Agropecuária Oeste; Embrapa Meio Ambiente. |
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28. | ![Imagem marcado/desmarcado](/consulta/web/img/desmarcado.png) | CARVALHO, C. S.; RIBEIRINHO, V. S.; ANDRADE, C. A. de; GRUTZMACHER, P.; PIRES, A. M. M. Composição química da matéria orgânica de lodos de esgoto. Agrária, Recife, v. 10, n. 3, p. 413-419, 2015. Biblioteca(s): Embrapa Meio Ambiente. |
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29. | ![Imagem marcado/desmarcado](/consulta/web/img/desmarcado.png) | SOUZA, C. P. C de; ABREU, C. A. de; ANDRADE, C. A. de. Identidade de métodos analíticos para quantificação dos teores totais de Zn e Cu em fertilizantes minerais e materiais secundários. In: REUNIÃO BRASILEIRA DE FERTILIDADE DO SOLO E NUTRIÇÃO DE PLANTAS, 30.; REUNIÃO BRASILEIRA SOBRE MICORRIZAS, 14.; SIMPÓSIO BRASILEIRO DE MICROBIOLOGIA DO SOLO, 12.; REUNIÃO BRASILEIRA DE BIOLOGIA DO SOLO, 9.; SIMPÓSIO SOBRE SELÊNIO NO BRASIL, 1., 2012, Maceió. A responsabilidade socioambiental da pesquisa agrícola: anais. Viçosa, MG: SBCS, 2012. 1 CD-ROM. Biblioteca(s): Embrapa Meio Ambiente. |
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30. | ![Imagem marcado/desmarcado](/consulta/web/img/desmarcado.png) | SILVA, C. A.; CERRI, C. E. P.; ANDRADE, C. A. de; MARTIN NETO, L.; BETTIOL, W. Matéria orgânica do solo: ciclo, compartimentos e funções. In: BETTIOL, W.; SILVA, C. A.; CERRI, C. E. P.; MARTIN NETO, L.; ANDRADE, C. A. de (ed.). Entendendo a matéria orgânica do solo em ambientes tropical e subtropical. Brasília, DF: Embrapa, 2023. cap. 1. p. 17-47. Biblioteca(s): Embrapa Instrumentação; Embrapa Meio Ambiente. |
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31. | ![Imagem marcado/desmarcado](/consulta/web/img/desmarcado.png) | GUERRINI, I. A.; JAMES, J.; NALESSO, P. H. P.; ANDRADE, C. A. de; HARRISON, R. B. A matéria orgânica do solo no cultivo de espécies florestais. In: BETTIOL, W.; SILVA, C. A.; CERRI, C. E. P.; MARTIN NETO, L.; ANDRADE, C. A. de (ed.). Entendendo a matéria orgânica do solo em ambientes tropical e subtropical. Brasília, DF: Embrapa, 2023. cap. 24. p. 677-704. Biblioteca(s): Embrapa Meio Ambiente. |
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33. | ![Imagem marcado/desmarcado](/consulta/web/img/desmarcado.png) | ANDRADE, C. A. de; SILVA, L. F. M.; PIRES, A. M. M.; COSCIONE, A. R. Mineralização do carbono e do nitrogênio no solo após sucessivas aplicações de lodo de esgoto. Pesquisa Agropecuária Brasileira, Brasília, DF, v. 48, n. 5, p. 536-544, maio 2013. Biblioteca(s): Embrapa Meio Ambiente; Embrapa Unidades Centrais. |
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37. | ![Imagem marcado/desmarcado](/consulta/web/img/desmarcado.png) | ANDRADE, C. A. de; LUIZ, A. J. B.; CARNIER, R.; AYER, J. E. B. Quantificação e monitoramento do estoque de carbono no solo: quantos pontos amostrar? Quantificação e monitoramento do estoque de carbono no solo: quantos pontos amostrar? In: CARBON SCIENCE TALKS, 2023, Campinas. [Resumos...] Campinas: Agro Bayer Brasil, 2023. Trabalho 13.; In: CARBON SCIENCE TALKS, 2023, Campinas. [Resumos...] Campinas: Agro Bayer Brasil, 2023. Trabalho 13. p. 34-35 Biblioteca(s): Embrapa Meio Ambiente. |
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38. | ![Imagem marcado/desmarcado](/consulta/web/img/desmarcado.png) | PUGA, A. P.; PIRES, A. M. M.; BETTIOL, W.; ANDRADE, C. A. de. Uso de lodo de esgoto na agricultura. In: BETTIOL, W.; SILVA, C. A.; CERRI, C. E. P.; MARTIN NETO, L.; ANDRADE, C. A. de (ed.). Entendendo a matéria orgânica do solo em ambientes tropical e subtropical. Brasília, DF: Embrapa, 2023. cap. 17; p. 507-530 Biblioteca(s): Embrapa Agropecuária Oeste; Embrapa Meio Ambiente. |
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39. | ![Imagem marcado/desmarcado](/consulta/web/img/desmarcado.png) | GRUNVALD, A. K.; CARVALHO, C. G. P. de; OLIVEIRA, A. C. B. de; ANDRADE, C. A. de B. Adaptabilidade e estabilidade de genótipos de girassol no Brasil Central. Pesquisa Agropecuária Brasileira, Brasília, DF, v. 43, n. 11, p. 1483-1493, nov. 2008. Biblioteca(s): Embrapa Clima Temperado; Embrapa Soja; Embrapa Unidades Centrais. |
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Registros recuperados : 138 | |
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![](/consulta/web/img/deny.png) | Acesso ao texto completo restrito à biblioteca da Embrapa Meio Ambiente. Para informações adicionais entre em contato com cnpma.biblioteca@embrapa.br. |
Registro Completo
Biblioteca(s): |
Embrapa Meio Ambiente. |
Data corrente: |
09/02/2018 |
Data da última atualização: |
30/10/2019 |
Tipo da produção científica: |
Artigo em Periódico Indexado |
Circulação/Nível: |
A - 1 |
Autoria: |
GRUTZMACHER, P.; PUGA, A. P.; BIBAR, M. P. S.; COSCIONE, A. R.; PACKER, A. P.; ANDRADE, C. A. de. |
Afiliação: |
PRISCILA GRUTZMACHER; ALINE PEREGRINA PUGA, FAPESP; MARIA PAULA SILVEIRA BIBAR, JBS Ambiental; ALINE RENEE COSCIONE, IAC; ANA PAULA CONTADOR PACKER, CNPMA; CRISTIANO ALBERTO DE ANDRADE, CNPMA. |
Título: |
Carbon stability and mitigation of fertilizer induced N2O emissions in soil amended with biochar. |
Ano de publicação: |
2018 |
Fonte/Imprenta: |
Science of The Total Environment, v. 625, p. 1459-1466, 2018. |
DOI: |
https://doi.org/10.1016/j.scitotenv.2017.12.196 |
Idioma: |
Inglês |
Conteúdo: |
Biochar is a promising tool for an efficient and low environmental impact agriculture since can offer both soil carbon (C) sequestration and mitigation of nitrous oxide (N2O) emissions. The extent of biochar C stability after soil amendment and efficiency in reducing N2O emissions from an external nitrogen (N) source were accessed through laboratory incubations. A clay loam soil was amended with chicken manure (CM), sewage sludge (SS), eucalyptus sawdust (ES) and filter cake (FC) feedstocks and corresponding slow-pyrolysis (400 °C) biochars at 5 g C kg? 1 soil in combination with two N fertilizer rates (0 and 140 mg N kg? 1 soil). Carbon dioxide (CO2) and N2O emissions were measured during 60 days. Biochars and feedstocks CO2 emissions were described by an exponential first order kinetics model. For C mineralization an interaction effect was observed for feedstock source and organic amendment. Lower values of mineralizable C was found for biochars than corresponding feedstocks, except for ES. Carbon losses in 60 days of incubation totaled between 0.8 and 9.4% and 2.4 and 32% for biochars and feedstocks, respectively. Regarding to N2O emissions, only CM-biochar impacted emissions with a two-fold increase in non-fertilized soil. When NH4NO3 was co-applied, biochars reduced fertilizer induced N2O emissions, reaching a seven-fold reduction in SS-biochar treatment. The fertilizer emission factor (EF) decreased with biochar amendments as well, varying between 0.01 and 0.08% of the fertilizer N emitted as N2O, which shows the biochar potential to reduce fertilizer induced N2O emissions, with major reduction by SS-biochar mitigating 87% of the soil-fertilizer emissions. Such potential could be explored by designing biochars based on feedstock chemical and structural properties, including a mixed feedstock source biochar that promotes C sequestration and mitigates N2O emissions. MenosBiochar is a promising tool for an efficient and low environmental impact agriculture since can offer both soil carbon (C) sequestration and mitigation of nitrous oxide (N2O) emissions. The extent of biochar C stability after soil amendment and efficiency in reducing N2O emissions from an external nitrogen (N) source were accessed through laboratory incubations. A clay loam soil was amended with chicken manure (CM), sewage sludge (SS), eucalyptus sawdust (ES) and filter cake (FC) feedstocks and corresponding slow-pyrolysis (400 °C) biochars at 5 g C kg? 1 soil in combination with two N fertilizer rates (0 and 140 mg N kg? 1 soil). Carbon dioxide (CO2) and N2O emissions were measured during 60 days. Biochars and feedstocks CO2 emissions were described by an exponential first order kinetics model. For C mineralization an interaction effect was observed for feedstock source and organic amendment. Lower values of mineralizable C was found for biochars than corresponding feedstocks, except for ES. Carbon losses in 60 days of incubation totaled between 0.8 and 9.4% and 2.4 and 32% for biochars and feedstocks, respectively. Regarding to N2O emissions, only CM-biochar impacted emissions with a two-fold increase in non-fertilized soil. When NH4NO3 was co-applied, biochars reduced fertilizer induced N2O emissions, reaching a seven-fold reduction in SS-biochar treatment. The fertilizer emission factor (EF) decreased with biochar amendments as well, varying between 0.01 and 0.08% of the... Mostrar Tudo |
Palavras-Chave: |
Biocarvão; Biomassa pirolisada; Black carbon; Pyrolized biomass. |
Thesagro: |
Biomassa; Carbono; Nitrogênio. |
Thesaurus NAL: |
Biochar; carbon sequestration; Greenhouse gas emissions; nitrogen; Pyrolysis. |
Categoria do assunto: |
P Recursos Naturais, Ciências Ambientais e da Terra |
Marc: |
LEADER 02891naa a2200337 a 4500 001 2087580 005 2019-10-30 008 2018 bl uuuu u00u1 u #d 024 7 $ahttps://doi.org/10.1016/j.scitotenv.2017.12.196$2DOI 100 1 $aGRUTZMACHER, P. 245 $aCarbon stability and mitigation of fertilizer induced N2O emissions in soil amended with biochar.$h[electronic resource] 260 $c2018 520 $aBiochar is a promising tool for an efficient and low environmental impact agriculture since can offer both soil carbon (C) sequestration and mitigation of nitrous oxide (N2O) emissions. The extent of biochar C stability after soil amendment and efficiency in reducing N2O emissions from an external nitrogen (N) source were accessed through laboratory incubations. A clay loam soil was amended with chicken manure (CM), sewage sludge (SS), eucalyptus sawdust (ES) and filter cake (FC) feedstocks and corresponding slow-pyrolysis (400 °C) biochars at 5 g C kg? 1 soil in combination with two N fertilizer rates (0 and 140 mg N kg? 1 soil). Carbon dioxide (CO2) and N2O emissions were measured during 60 days. Biochars and feedstocks CO2 emissions were described by an exponential first order kinetics model. For C mineralization an interaction effect was observed for feedstock source and organic amendment. Lower values of mineralizable C was found for biochars than corresponding feedstocks, except for ES. Carbon losses in 60 days of incubation totaled between 0.8 and 9.4% and 2.4 and 32% for biochars and feedstocks, respectively. Regarding to N2O emissions, only CM-biochar impacted emissions with a two-fold increase in non-fertilized soil. When NH4NO3 was co-applied, biochars reduced fertilizer induced N2O emissions, reaching a seven-fold reduction in SS-biochar treatment. The fertilizer emission factor (EF) decreased with biochar amendments as well, varying between 0.01 and 0.08% of the fertilizer N emitted as N2O, which shows the biochar potential to reduce fertilizer induced N2O emissions, with major reduction by SS-biochar mitigating 87% of the soil-fertilizer emissions. Such potential could be explored by designing biochars based on feedstock chemical and structural properties, including a mixed feedstock source biochar that promotes C sequestration and mitigates N2O emissions. 650 $aBiochar 650 $acarbon sequestration 650 $aGreenhouse gas emissions 650 $anitrogen 650 $aPyrolysis 650 $aBiomassa 650 $aCarbono 650 $aNitrogênio 653 $aBiocarvão 653 $aBiomassa pirolisada 653 $aBlack carbon 653 $aPyrolized biomass 700 1 $aPUGA, A. P. 700 1 $aBIBAR, M. P. S. 700 1 $aCOSCIONE, A. R. 700 1 $aPACKER, A. P. 700 1 $aANDRADE, C. A. de 773 $tScience of The Total Environment$gv. 625, p. 1459-1466, 2018.
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