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Registros recuperados : 46 | |
18. | ![Imagem marcado/desmarcado](/consulta/web/img/desmarcado.png) | COUTINHO, T. C.; ROJAS, M. J.; PARIS, E. C.; FARINAS, C. S. Imobilização de beta-glicosidase em nanopartículas de hidroxiapatita. In: WORKSHOP DA REDE DE NANOTECNOLOGIA APLICADA AO AGRONEGÓCIO, 9., 2017, São Carlos. Anais ... São Carlos: Embrapa Instrumentação, 2017. p. 223-226. Editores: Caue Ribeiro de Oliveira, Elaine Cristina Paris, Luiz Henrique Capparelli Mattoso, Marcelo Porto Bemquerer, Maria Alice Martins, Odílio Benedito Garrido de Assis. Biblioteca(s): Embrapa Instrumentação. |
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19. | ![Imagem marcado/desmarcado](/consulta/web/img/desmarcado.png) | ROJAS, M. J.; MOMESSO, M.; MATTOSO, L. H. C.; FARINAS, C. S. Imobilização de fitase em nanopartículas de quitosana. In: WORKSHOP DA REDE DE NANOTECNOLOGIA APLICADA AO AGRONEGÓCIO, 9., 2017, São Carlos. Anais ... São Carlos: Embrapa Instrumentação, 2017. p. 227-230. Editores: Caue Ribeiro de Oliveira, Elaine Cristina Paris, Luiz Henrique Capparelli Mattoso, Marcelo Porto Bemquerer, Maria Alice Martins, Odílio Benedito Garrido de Assis. Biblioteca(s): Embrapa Instrumentação. |
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Registros recuperados : 46 | |
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Registro Completo
Biblioteca(s): |
Embrapa Arroz e Feijão. |
Data corrente: |
07/12/2021 |
Data da última atualização: |
07/12/2021 |
Tipo da produção científica: |
Capítulo em Livro Técnico-Científico |
Autoria: |
KHALIL, M. I.; CORDOVIL, C. M. D. S.; FRANCAVIGLIA, R.; HENRY, B.; KLUMPP, K.; KONCZ, P.; LLORENTE, M.; MADARI, B. E.; MUÑOZ-ROJAS, M.; RAINER, N. |
Afiliação: |
MOHAMMAD I. KHALIL, UNIVERSITY COLLEGE DUBLIN, IRELAND; CLÁUDIA M. D. S. CORDOVIL, UNIVERSITY OF LISBON, PORTUGAL; ROSA FRANCAVIGLIA, COUNCIL FOR AGRICULTURAL RESEARCH AND ECONOMICS, RESEARCH CENTRE FOR AGRICULTURE AND ENVIRONMENT, ROME, ITALY; BEVERLEY HENRY, QUEENSLAND UNIVERSITY OF TECHNOLOGY, BRISBANE, AUSTRALIA; KATJA KLUMPP, INRA, CLERMONT-FERRAND, FRANCE; PETER KONCZ, DUNA-IPOLY NATIONAL PARK DIRECTORATE, BUDAPEST, HUNGARY; MIREIA LLORENTE, UNIVERSITY OF EXTREMADURA, PLASENCIA CAMPUS, SPAIN; BEATA EMOKE MADARI, CNPAF; MIRIAM MUÑOZ-ROJAS, THE UNIVERSITY OF WESTERN AUSTRALIA; NERGER RAINER, SOIL & MORE IMPACTS GMBH, HAMBURG, GERMANY. |
Título: |
Grasslands. |
Ano de publicação: |
2021 |
Fonte/Imprenta: |
In: FAO. Recarbonizing global soils: a technical manual of recommended management practices: cropland, grassland, integrated systems and farming approaches. Rome, 2021. v. 3, p. 370-375. |
ISBN: |
978-92-5-134893-2 |
DOI: |
https://doi.org/10.4060/cb6595en |
Idioma: |
Inglês |
Conteúdo: |
Grasslands are among the largest ecosystems and cover around 3.5 billion-hectare (ha) area, representing 26 percent of the world land area and 70 percent of the world agricultural area. These grassland soils contain about 20 percent of the world?s soil organic carbon (SOC) stocks. There are different types of grasslands: natural grasslands, semi-natural grasslands, and agricultural grasslands. Grasslands that are self-seeded are often defined as natural or native grasslands. These grasslands are predominated by grasses, grass-like plants, forbs, or shrubs suitable for grazing or browsing. They are defined as rangelands when natural (native) or grazed, and defined as pastures when forage is managed by seeding, mowing (i.e. for hay, silage, renewable energy production), fertilization and irrigation. Agricultural grasslands can be permanent (>5-years old) or temporary (i.e. included within the crop rotation, grass/arable-ley). Permanent grassland is often (semi-) natural. |
Thesagro: |
Carbono; Solo. |
Thesaurus NAL: |
Carbon sequestration; Grassland soils. |
Categoria do assunto: |
P Recursos Naturais, Ciências Ambientais e da Terra |
URL: |
https://ainfo.cnptia.embrapa.br/digital/bitstream/item/228600/1/v3-p370.pdf
|
Marc: |
LEADER 01901naa a2200301 a 4500 001 2137224 005 2021-12-07 008 2021 bl uuuu u00u1 u #d 020 $a978-92-5-134893-2 024 7 $ahttps://doi.org/10.4060/cb6595en$2DOI 100 1 $aKHALIL, M. I. 245 $aGrasslands.$h[electronic resource] 260 $c2021 520 $aGrasslands are among the largest ecosystems and cover around 3.5 billion-hectare (ha) area, representing 26 percent of the world land area and 70 percent of the world agricultural area. These grassland soils contain about 20 percent of the world?s soil organic carbon (SOC) stocks. There are different types of grasslands: natural grasslands, semi-natural grasslands, and agricultural grasslands. Grasslands that are self-seeded are often defined as natural or native grasslands. These grasslands are predominated by grasses, grass-like plants, forbs, or shrubs suitable for grazing or browsing. They are defined as rangelands when natural (native) or grazed, and defined as pastures when forage is managed by seeding, mowing (i.e. for hay, silage, renewable energy production), fertilization and irrigation. Agricultural grasslands can be permanent (>5-years old) or temporary (i.e. included within the crop rotation, grass/arable-ley). Permanent grassland is often (semi-) natural. 650 $aCarbon sequestration 650 $aGrassland soils 650 $aCarbono 650 $aSolo 700 1 $aCORDOVIL, C. M. D. S. 700 1 $aFRANCAVIGLIA, R. 700 1 $aHENRY, B. 700 1 $aKLUMPP, K. 700 1 $aKONCZ, P. 700 1 $aLLORENTE, M. 700 1 $aMADARI, B. E. 700 1 $aMUÑOZ-ROJAS, M. 700 1 $aRAINER, N. 773 $tIn: FAO. Recarbonizing global soils: a technical manual of recommended management practices: cropland, grassland, integrated systems and farming approaches. Rome, 2021.$gv. 3, p. 370-375.
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Embrapa Arroz e Feijão (CNPAF) |
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