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| 41. |  | SOUZA, C. P. C.; ABREU, C. A. de; ANDRADE, C. A. de; COSCIONE, A. R.; CUNHA, J. F. da. Comparison of analytical methods for quantifying the levels of lead, cadmium, chromium, and nickel in mineral fertilizers and industrial by-products. Communications in Soil Science and Plant Analysis, New York, v. 46, sup. 1, p. 34-56, 2015.| Biblioteca(s): Embrapa Meio Ambiente. |
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| 44. | | VARGAS, V. P; CANTARELLA, H.; MARTINS, A. A; SOARES, J. R; CARMO, J. B.; ANDRADE, C. A. de. Sugarcane crop residue increases N2O and CO2 emissions under high soil moisture conditions. Sugar Tech, New Delhi, v. 16, n. 2, p. 174?179, 2014.| Biblioteca(s): Embrapa Meio Ambiente. |
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| 46. | | CARNIER, R.; ABREU, C. A. de; ANDRADE, C. A. de; FERNANDES, A. O.; SILVEIRA, A. P. D.; COSCIONE, A. R. Soil quality index as a tool to assess biochars soil quality improvement in a heavy metal-contaminated soil Environmental Geochemistry and Health, v. 45, n. 8, p. 6027-6041, 2023.| Biblioteca(s): Embrapa Meio Ambiente. |
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| 47. | | COSCIONE, A. R.; SILVA, L. F. M.; De MARIA, I. C.; ANDRADE, C. A. de; FERRACINI, V. L. Solução do solo e análise de componentes principais para monitoramento da aplicação de lodo de esgoto. Revista Brasileira de Ciência do Solo, Viçosa, v. 38, n. 5, p. 1654-1662, 2014.| Biblioteca(s): Embrapa Meio Ambiente. |
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| 48. | | MARIA, I. C. de; PURQUERIO, L. F. V.; ANDRADE, C. A. de; WUTKE, E. B.; TIVELLI, S. W. Atributos físicos após tratamentos para recuperação da qualidade do solo em estufa agrícola. In: CONGRESSO BRASILEIRO DE CIÊNCIA DO SOLO, 33., 2011, Uberlândia. Solos nos biomas brasileiros: sustentabilidade e mudanças climáticas: anais. [Uberlândia]: SBCS: UFU, ICIAG, 2011. 1 CD-ROM.| Biblioteca(s): Embrapa Meio Ambiente. |
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| 49. | | NORONHA, N. C.; ANDRADE, C. A. de; CERRI, C. C.; PICCOLO, M. de C.; COSTA, J. J. F. Disponibilidade do ferro em sistemas de recuperação de pastagens. In: CONGRESSO BRASILEIRO DE CIÊNCIA DO SOLO, 33., 2011, Uberlândia. Solos nos biomas brasileiros: sustentabilidade e mudanças climáticas: anais. [Uberlândia]: SBCS: UFU, ICIAG, 2011. 1 CD-ROM. 4 p.| Biblioteca(s): Embrapa Meio Ambiente. |
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 | Acesso ao texto completo restrito à biblioteca da Embrapa Meio Ambiente. Para informações adicionais entre em contato com cnpma.biblioteca@embrapa.br. |
Registro Completo
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Biblioteca(s): |
Embrapa Meio Ambiente. |
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Data corrente: |
09/02/2018 |
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Data da última atualização: |
30/10/2019 |
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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: |
GRUTZMACHER, P.; PUGA, A. P.; BIBAR, M. P. S.; COSCIONE, A. R.; PACKER, A. P.; ANDRADE, C. A. de. |
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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. |
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Título: |
Carbon stability and mitigation of fertilizer induced N2O emissions in soil amended with biochar. |
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Ano de publicação: |
2018 |
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Fonte/Imprenta: |
Science of The Total Environment, v. 625, p. 1459-1466, 2018. |
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DOI: |
https://doi.org/10.1016/j.scitotenv.2017.12.196 |
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Idioma: |
Inglês |
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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 |
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Palavras-Chave: |
Biocarvão; Biomassa pirolisada; Black carbon; Pyrolized biomass. |
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Thesagro: |
Biomassa; Carbono; Nitrogênio. |
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Thesaurus NAL: |
Biochar; carbon sequestration; Greenhouse gas emissions; nitrogen; Pyrolysis. |
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Categoria do assunto: |
P Recursos Naturais, Ciências Ambientais e da Terra |
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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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