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Registro Completo |
Biblioteca(s): |
Embrapa Uva e Vinho. |
Data corrente: |
12/04/2022 |
Data da última atualização: |
14/07/2022 |
Tipo da produção científica: |
Capítulo em Livro Técnico-Científico |
Autoria: |
TONIETTO, J.; FALCADE, I.; GUERRA, C. C.; ZANUS, M. C. |
Afiliação: |
JORGE TONIETTO, CNPUV; IVANIRA FALCADE, Universidade de Caxias do Sul (UCS); CELITO CRIVELLARO GUERRA, CNPUV; MAURO CELSO ZANUS, CNPUV. |
Título: |
As Indicações Geográficas de vinhos do Rio Grande do Sul. |
Ano de publicação: |
2022 |
Fonte/Imprenta: |
In:Brasil. Ministério da Agricultura, Pecuária e Abastecimento. Indicações Geográficas do Rio Grande do Sul registradas até março de 2021. Brasília : MAPA/AECS, 2022. |
Páginas: |
136 p. |
Idioma: |
Português |
Notas: |
Capítulo V |
Conteúdo: |
As indicações geográficas (IG) no Brasil tiveram início no Rio Grande do Sul, através da estruturação da Indicação de Procedência (IP) Vale dos Vinhedos para vinhos. Esta novidade representou uma inovação, que foi apropriada pelo setor vitivinícola e, posteriormente, por diversos outras IGs de produtos no país. As ações de estímulo ao uso desse ativo de propriedade industrial foram feitas sobretudo a partir dos anos 1990 (Tonietto, 1993; Tonietto, 1994; Falcade & Tonietto, 1995), antes mesmo da promulgação da Lei de Propriedade Industrial (LPI) - Lei nº 9.279/1996 (Brasil, 1996), que introduziu, no Brasil, a possiblidade da proteção positiva das indicações geográficas (Brasil, 1996). |
Palavras-Chave: |
Brasil; Indicações geográficas (IG); Rio Grande do SUl. |
Thesagro: |
Vinho. |
Categoria do assunto: |
E Economia e Indústria Agrícola |
URL: |
https://ainfo.cnptia.embrapa.br/digital/bitstream/doc/1142177/1/IGs-RS-Cap5.pdf
|
Marc: |
LEADER 01461naa a2200229 a 4500 001 2142177 005 2022-07-14 008 2022 bl uuuu u00u1 u #d 100 1 $aTONIETTO, J. 245 $aAs Indicações Geográficas de vinhos do Rio Grande do Sul.$h[electronic resource] 260 $c2022 300 $a136 p. 500 $aCapítulo V 520 $aAs indicações geográficas (IG) no Brasil tiveram início no Rio Grande do Sul, através da estruturação da Indicação de Procedência (IP) Vale dos Vinhedos para vinhos. Esta novidade representou uma inovação, que foi apropriada pelo setor vitivinícola e, posteriormente, por diversos outras IGs de produtos no país. As ações de estímulo ao uso desse ativo de propriedade industrial foram feitas sobretudo a partir dos anos 1990 (Tonietto, 1993; Tonietto, 1994; Falcade & Tonietto, 1995), antes mesmo da promulgação da Lei de Propriedade Industrial (LPI) - Lei nº 9.279/1996 (Brasil, 1996), que introduziu, no Brasil, a possiblidade da proteção positiva das indicações geográficas (Brasil, 1996). 650 $aVinho 653 $aBrasil 653 $aIndicações geográficas (IG) 653 $aRio Grande do SUl 700 1 $aFALCADE, I. 700 1 $aGUERRA, C. C. 700 1 $aZANUS, M. C. 773 $tIn:Brasil. Ministério da Agricultura, Pecuária e Abastecimento. Indicações Geográficas do Rio Grande do Sul registradas até março de 2021. Brasília : MAPA/AECS, 2022.
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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: |
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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.
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