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Registro Completo |
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Biblioteca(s): |
Embrapa Tabuleiros Costeiros. |
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Data corrente: |
29/03/2010 |
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Data da última atualização: |
06/04/2022 |
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Tipo da produção científica: |
Artigo em Anais de Congresso / Nota Técnica |
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Autoria: |
MOREIRA, M. A. B.; LIRA, M. A.; TALAMINI, V.; CARVALHO, H. W. L. de; ALVES, M. C. S.; ESPINOLA SOBRINHO, E.; OLIVEIRA, A. M. S. |
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Afiliação: |
MARCOS ANTONIO BARBOSA MOREIRA, CPATC; MARCELO ABDON LIRA, EMPARN; VIVIANE TALAMINI, CPATC; HELIO WILSON LEMOS DE CARVALHO, CPATC; MARIA CLEA SANTOS ALVES, EMPARN; ERNESTO ESPINOLA SOBRINHO, EMPARN; ALLYSON MAGNO SOUZA OLIVEIRA, EMPARN. |
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Título: |
Avaliação de genótipos de girassol quanto à infestação do besouro amarelo, Ciclocephala melanocephala no estado do Rio Grande do Norte. |
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Ano de publicação: |
2009 |
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Fonte/Imprenta: |
In: REUNIÃO NACIONAL DE PESQUISA DO GIRASSOL, 18., SIMPÓSIO NACIONAL SOBRE A CULTURA DO GIRASSOL, 6., 2009. Pelotas. Anais... Pelotas: Embrapa Clima Temperado, 2009. 388 p. Editado por Ana Claudia Barneche de Oliveira, Ana Paula Afonso Scheneid da Rosa e Márcia Vizzotto. |
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Páginas: |
p. 154-159. |
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Descrição Física: |
Artigo em anais. |
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Idioma: |
Português |
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Thesagro: |
Besouro; Girassol; Praga de Planta. |
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Categoria do assunto: |
-- |
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URL: |
https://ainfo.cnptia.embrapa.br/digital/bitstream/doc/662645/1/Avaliacao-de-genotipos0001.pdf
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Marc: |
LEADER 00961nam a2200217 a 4500
001 1662645
005 2022-04-06
008 2009 bl uuuu u00u1 u #d
100 1 $aMOREIRA, M. A. B.
245 $aAvaliação de genótipos de girassol quanto à infestação do besouro amarelo, Ciclocephala melanocephala no estado do Rio Grande do Norte.$h[electronic resource]
260 $aIn: REUNIÃO NACIONAL DE PESQUISA DO GIRASSOL, 18., SIMPÓSIO NACIONAL SOBRE A CULTURA DO GIRASSOL, 6., 2009. Pelotas. Anais... Pelotas: Embrapa Clima Temperado, 2009. 388 p. Editado por Ana Claudia Barneche de Oliveira, Ana Paula Afonso Scheneid da Rosa e Márcia Vizzotto.$c2009
300 $ap. 154-159.$cArtigo em anais.
650 $aBesouro
650 $aGirassol
650 $aPraga de Planta
700 1 $aLIRA, M. A.
700 1 $aTALAMINI, V.
700 1 $aCARVALHO, H. W. L. de
700 1 $aALVES, M. C. S.
700 1 $aESPINOLA SOBRINHO, E.
700 1 $aOLIVEIRA, A. M. S.
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Embrapa Tabuleiros Costeiros (CPATC) |
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 | Acesso ao texto completo restrito à biblioteca da Embrapa Amazônia Oriental. Para informações adicionais entre em contato com cpatu.biblioteca@embrapa.br. |
Registro Completo
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Biblioteca(s): |
Embrapa Amazônia Oriental. |
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Data corrente: |
29/03/2012 |
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Data da última atualização: |
11/11/2022 |
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Tipo da produção científica: |
Artigo em Periódico Indexado |
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Circulação/Nível: |
A - 2 |
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Autoria: |
PAULA, F. R. de; FERRAZ, S. F. de B.; GERHARD, P.; VETTORAZZI, C. A.; FERREIRA, A. |
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Afiliação: |
FELIPE ROSSETTI DE PAULA, ESALQ; SILVIO FROSINI DE BARROS FERRAZ, ESALQ; PEDRO GERHARD, CPATU; CARLOS ALBERTO VETTORAZZI, ESALQ; ANDERSON FERREIRA, USP. |
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Título: |
Large woody debris input and its influence on channel structure in agricultural lands of Southeast Brazil. |
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Ano de publicação: |
2011 |
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Fonte/Imprenta: |
Environmental Management, v. 48, n. 4, p. 750-763, Oct. 2011. |
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DOI: |
10.1007/s00267-011-9730-4 |
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Idioma: |
Inglês |
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Conteúdo: |
Riparian forests are important for the structure and functioning of stream ecosystems, providing structural components such as large woody debris (LWD). Changes in these forests will cause modifications in the LWD input to streams, affecting their structure. In order to assess the influence of riparian forests changes in LWD supply, 15 catchments (third and fourth order) with riparian forests at different conservation levels were selected for sampling. In each catchment we quantified the abundance, volume and diameter of LWD in stream channels; the number, area and volume of pools formed by LWD and basal area and tree diameter of riparian forest. We found that riparian forests were at a secondary successional stage with predominantly young trees (diameter at breast height \10 cm) in all studied streams. Results showed that basal area and diameter of riparian forest differed between the stream groups (forested and non-forested), but tree density did not differ between groups. Differences were also observed in LWD abundance, volume, frequency of LWD pools with subunits and area and volume of LWD pools. LWD diameter, LWD that form pools diameter and frequency of LWD pools without subunits did not differ between stream groups. Regression analyses showed that LWD abundance and volume, and frequency of LWD pools (with and without subunits) were positively related with the proportion of riparian forest. LWD diameter was not correlated to riparian tree diameter. The frequency of LWD pools was correlated to the abundance and volume of LWD, but characteristics of these pools (area and volume) were not correlated to the diameter of LWD that formed the pools. These results show that alterations in riparian forest cause modifications in the LWD abundance and volume in the stream channel, affecting mainly the structural complexity of these ecosystems (reduction in the number and structural characteristics of LWD pools). Our results also demonstrate that riparian forest conservation actions must consider not only its extension, but also successional stage to guarantee the quantity and quality of LWD necessary to enable the structuring of stream channels. MenosRiparian forests are important for the structure and functioning of stream ecosystems, providing structural components such as large woody debris (LWD). Changes in these forests will cause modifications in the LWD input to streams, affecting their structure. In order to assess the influence of riparian forests changes in LWD supply, 15 catchments (third and fourth order) with riparian forests at different conservation levels were selected for sampling. In each catchment we quantified the abundance, volume and diameter of LWD in stream channels; the number, area and volume of pools formed by LWD and basal area and tree diameter of riparian forest. We found that riparian forests were at a secondary successional stage with predominantly young trees (diameter at breast height \10 cm) in all studied streams. Results showed that basal area and diameter of riparian forest differed between the stream groups (forested and non-forested), but tree density did not differ between groups. Differences were also observed in LWD abundance, volume, frequency of LWD pools with subunits and area and volume of LWD pools. LWD diameter, LWD that form pools diameter and frequency of LWD pools without subunits did not differ between stream groups. Regression analyses showed that LWD abundance and volume, and frequency of LWD pools (with and without subunits) were positively related with the proportion of riparian forest. LWD diameter was not correlated to riparian tree diameter. The frequency of LWD... Mostrar Tudo |
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Palavras-Chave: |
Mata Atlântica. |
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Thesagro: |
Mata Ciliar. |
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Categoria do assunto: |
K Ciência Florestal e Produtos de Origem Vegetal |
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Marc: |
LEADER 02827naa a2200205 a 4500
001 1920875
005 2022-11-11
008 2011 bl uuuu u00u1 u #d
024 7 $a10.1007/s00267-011-9730-4$2DOI
100 1 $aPAULA, F. R. de
245 $aLarge woody debris input and its influence on channel structure in agricultural lands of Southeast Brazil.$h[electronic resource]
260 $c2011
520 $aRiparian forests are important for the structure and functioning of stream ecosystems, providing structural components such as large woody debris (LWD). Changes in these forests will cause modifications in the LWD input to streams, affecting their structure. In order to assess the influence of riparian forests changes in LWD supply, 15 catchments (third and fourth order) with riparian forests at different conservation levels were selected for sampling. In each catchment we quantified the abundance, volume and diameter of LWD in stream channels; the number, area and volume of pools formed by LWD and basal area and tree diameter of riparian forest. We found that riparian forests were at a secondary successional stage with predominantly young trees (diameter at breast height \10 cm) in all studied streams. Results showed that basal area and diameter of riparian forest differed between the stream groups (forested and non-forested), but tree density did not differ between groups. Differences were also observed in LWD abundance, volume, frequency of LWD pools with subunits and area and volume of LWD pools. LWD diameter, LWD that form pools diameter and frequency of LWD pools without subunits did not differ between stream groups. Regression analyses showed that LWD abundance and volume, and frequency of LWD pools (with and without subunits) were positively related with the proportion of riparian forest. LWD diameter was not correlated to riparian tree diameter. The frequency of LWD pools was correlated to the abundance and volume of LWD, but characteristics of these pools (area and volume) were not correlated to the diameter of LWD that formed the pools. These results show that alterations in riparian forest cause modifications in the LWD abundance and volume in the stream channel, affecting mainly the structural complexity of these ecosystems (reduction in the number and structural characteristics of LWD pools). Our results also demonstrate that riparian forest conservation actions must consider not only its extension, but also successional stage to guarantee the quantity and quality of LWD necessary to enable the structuring of stream channels.
650 $aMata Ciliar
653 $aMata Atlântica
700 1 $aFERRAZ, S. F. de B.
700 1 $aGERHARD, P.
700 1 $aVETTORAZZI, C. A.
700 1 $aFERREIRA, A.
773 $tEnvironmental Management$gv. 48, n. 4, p. 750-763, Oct. 2011.
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