| |
|
|
| Registros recuperados : 21 | |
| 2. |  | SUGAYAMA, R. L.; IEDE, E. T.; STANCIOLI, A. R.; ALVES, G. A.; OLIVEIRA, I. M. de. Ameaças fitossanitárias. In: SUGAYAMA, R. L.; SILVA, M. L. da; SILVA, S. X. de B.; RIBEIRO, L. C.; RANGEL, L. E. P. (Ed.). Defesa vegetal: fundamentos, ferramentas, políticas e perspectivas Belo Horizonte: Sociedade Brasileira de Defesa Agropecuária, 2015. p. 449-471.| Biblioteca(s): Embrapa Florestas. |
|   |
| 5. | | NEVES, B. P. das; OLIVEIRA, I. P. de; VALOIS, A. C. C. Práticas e técnicas sustentáveis do uso do nim indiano para o produtor na terra do Ninco, dona Dira e senhor Kita. [Brasília, DF]: Embrapa, 2006. 35 p. color. il. Cartilha. Convênio Geral de Cooperação Técnica para P&D e DTRTA do MAPA e Embrapa com o Maranhão (SEAGRO, SECTEC, SEPLAN, UEMA, INAGRO, FAEMA.| Biblioteca(s): Embrapa Agroindústria Tropical; Embrapa Amazônia Ocidental; Embrapa Amazônia Oriental; Embrapa Arroz e Feijão; Embrapa Cocais; Embrapa Florestas; Embrapa Meio-Norte; Embrapa Roraima; Embrapa Unidades Centrais. |
| |
| 6. | | PINATTI, D. G.; CONTE, R. A.; OLIVEIRA, I. de; FERREIRA, J. C.; ROMÃO, E. L. Desenvolvimentos tecnológicos recentes sobre florestas energéticas. In: CONGRESSO BRASILEIRO SOBRE FLORESTAS ENERGÉTICAS, 1., 2009, Belo Horizonte. Anais. Colombo: Embrapa Florestas, 2009. 1 CD-ROM. (Embrapa Florestas. Documentos, 178). Seção: Derivados Energéticos de Alto Valor Agregado.| Biblioteca(s): Embrapa Florestas. |
| |
| 8. | | CAMPOS, J. C. C.; LEITE, H. G.; OLIVEIRA, I. A. de. Variacao da forma e do volume do tronco de clones de Eucalipto em duas regioes. In: CONGRESSO FLORESTAL PANAMERICANO, 1.; CONGRESSO FLORESTAL BRASILEIRO, 7., 1993, Curitiba. Floresta para o Desenvolvimento: Política, Ambiente, Tecnologia e Mercado: anais. São Paulo: SBS; [S.l.]: SBEF, 1993. v.2, p.559-565.| Biblioteca(s): Embrapa Florestas. |
| |
| 10. | | BORDRN, B.; OLIVEIRA, R. K. de; HIGA, R. C. V.; OLIVEIRA, I. R. de; ZANATTA, J. A. Adaptação agrícola e florestal às mudanças climáticas. In: ANDREOLI, C. V.; PHILIPPI JUNIOR, A. (ed.). Sustentabilidade no agronegócio. Santana de Parnaiba: Manole, 2021. cap. 19, p. 537-560. (Ambiental, 28).| Biblioteca(s): Embrapa Florestas. |
|  |
| 11. | | FREITAS, L. de; CASAGRANDE, J. C.; OLIVEIRA, I. A. de; CAMPOS, M. C. C.; OLIVEIRA, V. M. R. de. Atributos químicos de latossolo vermelho submetido a diferentes manejos. Floresta, Curitiba, v. 45, n. 2, p. 229-240, abr./jun. 2015.| Biblioteca(s): Embrapa Florestas. |
| |
| 12. | | FREIRE E CRUZ, A.; PASSOS, M. A. A.; JOSÉ, A. A. da S.; TORRES, S. B.; OLIVEIRA, I. S. de. Métodos para análise de sementes de Bowdichia virgilioides Kunth. Scientia Forestalis, Piracicaba, v. 40, n. 93, p. 77-84, mar. 2012.| Biblioteca(s): Embrapa Florestas. |
| |
| 13. | | FRANÇA, F.; MELO, E. de; OLIVEIRA, I. B. de; REIS, A. T. C. C.; ALVES, G. L.; COSTA, M. F. Plantas vasculares das áreas alagadas dos Marimbus, Chapada Diamantina, BA, Brasil. Hoehnea, São Paulo, v. 37, n. 4, p. 719-730, dez. 2010.| Biblioteca(s): Embrapa Florestas. |
| |
| 14. | | ROMÃO, E. L.; CONTE, R. A.; PINATTI, D. G.; OLIVEIRA, I. de; PEREIRA, M. L. G.; FERREIRA, J. C. Sequência de tratamentos para redução de metais alcalinos e enxofre em celulignina destinada à obtenção de gás de síntese para geração de energia termoelétrica. In: CONGRESSO BRASILEIRO SOBRE FLORESTAS ENERGÉTICAS, 1., 2009, Belo Horizonte. Anais. Colombo: Embrapa Florestas, 2009. 1 CD-ROM. (Embrapa Florestas. Documentos, 178). Seção: Derivados Energéticos de Alto Valor Agregado.| Biblioteca(s): Embrapa Florestas. |
| |
| 15. | | QUEIROZ, A. F. S.; OLIVEIRA, O. M. C.; OLIVEIRA, I. B.; ARGÔLO, J. L.; SANTOS, J. B.; NANO, R. M. W.; RODRIGUES, R. P. Impactos geoambientais em florestas de Manguezal do Estado da Bahia: subsídios a um programa de preservação da biodiversidade em Ecossistema Manguezal da América Tropical. In: CONGRESSO E EXPOSIÇÃO INTERNACIONAL SOBRE FLORESTAS, 6., 2000, Porto Seguro. Resumos técnicos. Rio de Janeiro: Instituto Ambiental Biosfera, 2000. p. 520-524.| Biblioteca(s): Embrapa Florestas. |
| |
| 17. | | VERLY, O. M.; OLIVEIRA, I. M. M. de; SANTOS, C. T. F. dos; FIALHO JUNIOR, L. L.; ROSA, P. R.; CHAVES, A. G. S.; FRANCO, F. M. Caracterização florística e fitossociologia de um fragmento de Cerradão em Cáceres, Mato Grosso. Pesquisa Florestal Brasileira, Colombo, v. 40, e201801742, 2020. 13 p.| Biblioteca(s): Embrapa Florestas. |
|  |
| 18. | | OLIVEIRA, I. A. de; MARQUES JÚNIOR, J.; CAMPOS, M. C. C.; AQUINO, R. E. de; SIQUEIRA, D. S.; FREITAS, L. de. Spacial variability and sampling density of chemical attributes in archaeological black earth and native forest soil in Manicoré, AM. Floresta, Curitiba, v. 44, n. 4, p. 735-746, 2014.| Biblioteca(s): Embrapa Florestas. |
| |
| 19. | | BIANCHI, M. de O.; OLIVEIRA, I. P. de; CORREIA, M. E. F.; RESENDE, A. da S.; CAMPELLO, E. F. C.; SILVA, E. M. R. da. Soil macrofauna response to different proportions of legume trees in land reclamation. In: INTERNATIONAL COLLOQUIUM ON SOIL ZOOLOGY, 15; INTERNATIONAL COLLOQUIUM ON APTERYGOTA, 12., 2008, Curitiba. Biodiversity, conservation and sustainabele management of soil animal: abstracts. Colombo: Embrapa Florestas. Editors: George Gardner Brown; Klaus Dieter Sautter; Renato Marques; Amarildo Pasini. 1 CD-ROM.| Biblioteca(s): Embrapa Florestas. |
| |
| 20. | | PIVELLO, V. R.; ROCHA, R. M.; VITULE, J. R. S.; BRAGA, R. R.; BROWN, G. G.; CASTRO, C. F.; CRUZ NETO, C. C.; FRANCO, A. C. S.; HERINGER, G.; MAGALHÃES, A. L. B.; MIRANDA, R. J.; MORMUL, R. P.; OLIVEIRA, I.; SAULINO, H. H. L.; MATOS, D. M. S. Impactos de espécies exóticas invasoras sobre as contribuições da natureza para as pessoas (CNP), o desenvolvimento sustentável e a boa qualidade de vida. In: DECHOUM, M. S.; JUNQUEIRA, A. O. R.; ORSI, M. L. (org.). Relatório temático sobre espécies exóticas invasoras, biodiversidade e serviços ecossistêmicos. São Carlos: Cubo, 2024. cap. 4 p. 133-184.| Biblioteca(s): Embrapa Florestas. |
| |
| Registros recuperados : 21 | |
|
|
|
 | 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: |
22/09/2008 |
|
Data da última atualização: |
22/09/2008 |
|
Autoria: |
BIANCHI, M. de O.; OLIVEIRA, I. P. de; CORREIA, M. E. F.; RESENDE, A. da S.; CAMPELLO, E. F. C.; SILVA, E. M. R. da. |
|
Título: |
Soil macrofauna response to different proportions of legume trees in land reclamation. |
|
Ano de publicação: |
2008 |
|
Fonte/Imprenta: |
In: INTERNATIONAL COLLOQUIUM ON SOIL ZOOLOGY, 15; INTERNATIONAL COLLOQUIUM ON APTERYGOTA, 12., 2008, Curitiba. Biodiversity, conservation and sustainabele management of soil animal: abstracts. Colombo: Embrapa Florestas. Editors: George Gardner Brown; Klaus Dieter Sautter; Renato Marques; Amarildo Pasini. 1 CD-ROM. |
|
Idioma: |
Inglês |
|
Conteúdo: |
Soil biota is the major responsable for the regulation of various processes such as decomposition,
mineralization and nurient cycling wich affect the plant growth and the production maintenance
in long-term (LAVELLE, 1997). The aim of this study was to evaluate the influence of planting
legume trees as an estrategy for land reclamation above soil macrofauna. The study area
includes a slope, at the Municipality of Valença, Rio de Janeiro state ? Brazil, originally in the
Atlantic Forest Biome, but under a secondary sucession process. In the experimental area it
was introduced seven tree fixing nitrogen legumes species in four proportions of the total number
of trees planted: 0% (0L), 25% (25L), 50% (50L) and 75% (75L). Other samples were taken in
a secondary forest, and in two areas of pasture, an abandoned pasture (Pasture B), with
spontaneous vegetation, grass and some bushes, and other pasture that is regularly grazed by
animals, with predominance of Brachiaria grass ( Pasture A). The sampling occurred at the end
of the dry season, using the method TSBF (ANDERSON & INGRAM, 1993) at depths of 0-10
cm, 10-20 cm and 20-30 cm, and the litter layer. Treatment 50L had the lowest total fauna groups
richness and at the same time that showed the highest macrofauna density, mainly because of
the Formicidae dominance. However, in the treatments 25L and 75L it was observed the lowest
abundance and in contrast the greatest groups richness what suggests that they contribute to
the better soil fauna colonization. Analyzing the macrofauna vertical distribution, in the almost all
areas the largest abundance of organisms occurred in the soil superficial layer (0-10 cm),
exception for 25L and 75L treatments. The soil fauna colonization of this layer raised 70% in
Pastures A and B. This similarity observed in vertical distribuition between the forest and pastures,
suggests an influence of the sampling period, that took place after the dry season, when the
vegetation was very affected. The number of individuals present in the 10-20 cm depth proved
to be roughly similar for all treatments, while the greatest abundance in 20-30 cm was observed
in 75L treatment. The soil fauna diversity was similar among treatments, with the predominance
of the family Formicidae, followed by Isoptera, characterizing the intense colonization of social
insects in these systems. MenosSoil biota is the major responsable for the regulation of various processes such as decomposition,
mineralization and nurient cycling wich affect the plant growth and the production maintenance
in long-term (LAVELLE, 1997). The aim of this study was to evaluate the influence of planting
legume trees as an estrategy for land reclamation above soil macrofauna. The study area
includes a slope, at the Municipality of Valença, Rio de Janeiro state ? Brazil, originally in the
Atlantic Forest Biome, but under a secondary sucession process. In the experimental area it
was introduced seven tree fixing nitrogen legumes species in four proportions of the total number
of trees planted: 0% (0L), 25% (25L), 50% (50L) and 75% (75L). Other samples were taken in
a secondary forest, and in two areas of pasture, an abandoned pasture (Pasture B), with
spontaneous vegetation, grass and some bushes, and other pasture that is regularly grazed by
animals, with predominance of Brachiaria grass ( Pasture A). The sampling occurred at the end
of the dry season, using the method TSBF (ANDERSON & INGRAM, 1993) at depths of 0-10
cm, 10-20 cm and 20-30 cm, and the litter layer. Treatment 50L had the lowest total fauna groups
richness and at the same time that showed the highest macrofauna density, mainly because of
the Formicidae dominance. However, in the treatments 25L and 75L it was observed the lowest
abundance and in contrast the greatest groups richness what suggests that they contribute to
the bette... Mostrar Tudo |
|
Categoria do assunto: |
-- |
|
Marc: |
LEADER 03183naa a2200181 a 4500
001 1314885
005 2008-09-22
008 2008 bl uuuu u00u1 u #d
100 1 $aBIANCHI, M. de O.
245 $aSoil macrofauna response to different proportions of legume trees in land reclamation.
260 $c2008
520 $aSoil biota is the major responsable for the regulation of various processes such as decomposition, mineralization and nurient cycling wich affect the plant growth and the production maintenance in long-term (LAVELLE, 1997). The aim of this study was to evaluate the influence of planting legume trees as an estrategy for land reclamation above soil macrofauna. The study area includes a slope, at the Municipality of Valença, Rio de Janeiro state ? Brazil, originally in the Atlantic Forest Biome, but under a secondary sucession process. In the experimental area it was introduced seven tree fixing nitrogen legumes species in four proportions of the total number of trees planted: 0% (0L), 25% (25L), 50% (50L) and 75% (75L). Other samples were taken in a secondary forest, and in two areas of pasture, an abandoned pasture (Pasture B), with spontaneous vegetation, grass and some bushes, and other pasture that is regularly grazed by animals, with predominance of Brachiaria grass ( Pasture A). The sampling occurred at the end of the dry season, using the method TSBF (ANDERSON & INGRAM, 1993) at depths of 0-10 cm, 10-20 cm and 20-30 cm, and the litter layer. Treatment 50L had the lowest total fauna groups richness and at the same time that showed the highest macrofauna density, mainly because of the Formicidae dominance. However, in the treatments 25L and 75L it was observed the lowest abundance and in contrast the greatest groups richness what suggests that they contribute to the better soil fauna colonization. Analyzing the macrofauna vertical distribution, in the almost all areas the largest abundance of organisms occurred in the soil superficial layer (0-10 cm), exception for 25L and 75L treatments. The soil fauna colonization of this layer raised 70% in Pastures A and B. This similarity observed in vertical distribuition between the forest and pastures, suggests an influence of the sampling period, that took place after the dry season, when the vegetation was very affected. The number of individuals present in the 10-20 cm depth proved to be roughly similar for all treatments, while the greatest abundance in 20-30 cm was observed in 75L treatment. The soil fauna diversity was similar among treatments, with the predominance of the family Formicidae, followed by Isoptera, characterizing the intense colonization of social insects in these systems.
700 1 $aOLIVEIRA, I. P. de
700 1 $aCORREIA, M. E. F.
700 1 $aRESENDE, A. da S.
700 1 $aCAMPELLO, E. F. C.
700 1 $aSILVA, E. M. R. da
773 $tIn: INTERNATIONAL COLLOQUIUM ON SOIL ZOOLOGY, 15; INTERNATIONAL COLLOQUIUM ON APTERYGOTA, 12., 2008, Curitiba. Biodiversity, conservation and sustainabele management of soil animal: abstracts. Colombo: Embrapa Florestas. Editors: George Gardner Brown; Klaus Dieter Sautter; Renato Marques; Amarildo Pasini. 1 CD-ROM.
Download
Esconder MarcMostrar Marc Completo |
|
Registro original: |
Embrapa Florestas (CNPF) |
|
|
Biblioteca |
ID |
Origem |
Tipo/Formato |
Classificação |
Cutter |
Registro |
Volume |
Status |
Fechar
|
| Nenhum registro encontrado para a expressão de busca informada. |
|
|
