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Registros recuperados : 159 | |
121. | ![Imagem marcado/desmarcado](/consulta/web/img/desmarcado.png) | SILVA, M. A. C. da; BEZERRA, M. A. de O.; CATELLA, A. C. Práticas milenares de pesca no Pantanal. Corumbá: Embrapa Pantanal, 2010. 6 p. Artigo de Divulgação na Mídia (ADM 141) Formato eletronico. Disponivel em: Agência Pantanal, Meat World, Aqui e destaque, Canal do produtor, Infobibos, Rios Vivos,
Campo Grande News, Maracaju News, Conheça o Pantanal, MS Notícias, Agora MS. Biblioteca(s): Embrapa Pantanal. |
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122. | ![Imagem marcado/desmarcado](/consulta/web/img/desmarcado.png) | VARGAS, R. D.; LIMA, R. P.; MARQUES, D. K. S.; CATELLA, A. C.; MORAES, A. S. Pesca no Pantanal do Mato Grosso do Sul (Bacia do Alto Paraguai). In: MARQUES, D. K. S.; MORAES, A. S. (Ed.). Pesca e piscicultura no Pantanal: o produtor pergunta, a Embrapa responde. Brasília, DF: Embrapa Informação Tecnológica; Corumbá: Embrapa Pantanal, 2010. (Coleção 500 perguntas, 500 respostas). p. 51-58. Biblioteca(s): Embrapa Pantanal. |
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124. | ![Imagem marcado/desmarcado](/consulta/web/img/desmarcado.png) | LIMA, V. S. N. C.; SILVA CRUZ, L. W.; CATELLA, A. C.; EATON, D. Resultados preliminares sobre as capturas e devoluções de peixes em pescarias esportivas no Rio Paraguai, MS, em 2003. In: SIMPÓSIO SOBRE RECURSOS NATURAIS E SÓCIO-ECONÔMICOS DO PANTANAL, 4., 2004, Corumbá, MS. Sustentabilidade regional: anais. Corumbá: Embrapa Pantanal: UCDB: UFMS: SEBRAE-MS, 2004. (CD-ROM). Biblioteca(s): Embrapa Pantanal. |
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125. | ![Imagem marcado/desmarcado](/consulta/web/img/desmarcado.png) | CATELLA, A. C.; SPACKI, V.; GINDRI, B. S.; BUENO, B.; ZUCCO, C. A. Características da pesca de iscas vivas na bacia do Alto Paraguai em Mato Grosso do Sul. In: SIMPÓSIO SOBRE RECURSOS NATURAIS E SOCIOECONÔMICOS DO PANTANAL, 6.; EVENTO DE INICIAÇÃO CIENTÍFICA DO PANTANAL, 1., 2013, Corumbá, MS. Desafios e soluções para o Pantanal: resumos. Corumbá: Embrapa Pantanal, 2013. Biblioteca(s): Embrapa Pantanal. |
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126. | ![Imagem marcado/desmarcado](/consulta/web/img/desmarcado.png) | CATELLA, A. C.; MASCARENHAS, R. de O.; ALBUQUERQUE, S. P.; ALBUQUERQUE, F. F. de; THEODORO, E. R. de M. Sistemas de estatísticas pesqueiras no Pantanal, Brasil: aspectos técnicos e políticos. Pan-American Journal of Aquatic Sciences, v.3, n.3, p. 174-192, 2008. Biblioteca(s): Embrapa Pantanal. |
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128. | ![Imagem marcado/desmarcado](/consulta/web/img/desmarcado.png) | MOARES, A. S.; RESENDE, E. K. de; PADOVANI, C. R.; CATELLA, A. C.; ALBUQUERQUE, F. F. de; ESPÍNDOLA, C. Análise da situação atual e impacto ambiental da pesca na Estrada-parque MS. In: WORKSHOP ESTRADA-PARQUE PANTANAL, 2., 2002, Corumbá, MS. Anais... [Corumbá]: SEMACT. Comite Gestor Estrada-Parque Pantanal: WWF, 2002. nao paginado. Biblioteca(s): Embrapa Pantanal. |
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131. | ![Imagem marcado/desmarcado](/consulta/web/img/desmarcado.png) | CATELLA, A. C.; ALBUQUERQUE, F. F. de; FRANCESCHINI, E.; PEIXER, J.; MORAES, A. S.; PALMEIRA, S. da S. Desembarque pesqueiro na bacia do Alto Paraguai em 1995. In: SIMPOSIO SOBRE RECURSOS NATURAIS E SOCIO-ECONOMICOS DO PANTANAL, 2., 1996, Corumba. Manejo e conservacao: resumos. Brasilia: EMBRAPA-SPI, 1996. p.78-79 Biblioteca(s): Embrapa Pantanal. |
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134. | ![Imagem marcado/desmarcado](/consulta/web/img/desmarcado.png) | MASCARENHAS, R. O.; CATELLA, A. C.; ALBUQUERQUE, S. E.; ALBUQUERQUE, F. F.; THEODORO, E. R. M.; MOTTA, A. C. D. C.; PÖTTER, C. The technical and political challenges in the implementation of fishing statistics system: experiences in the brazilian Pantanal. In: INTECOL INTERNATIONAL WETLANDS CONFERENCE, 8., Cuiabá, 2008. Big wetlands, big concerns: abstracts. [Sl.: s.n], 2008. p. 120. Biblioteca(s): Embrapa Pantanal. |
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135. | ![Imagem marcado/desmarcado](/consulta/web/img/desmarcado.png) | CATELLA, A. C.; ALBUQUERQUE, S.; ALBUQUERQUE, F. F. de; CAMPOS, F. L. R.; SILVA, J. M. V.; JESUS, V. M. F. de. Tendências da pesca em 15 anos de monitoramento no Pantanal Sul. In: ENCONTRO BRASILEIRO DE ICTIOLOGIA, 19., 2011, Manaus. Anais...[Manaus]: SBI, 2011. p. 757. Biblioteca(s): Embrapa Pantanal. |
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136. | ![Imagem marcado/desmarcado](/consulta/web/img/desmarcado.png) | MOREIRA, M. M. M.; SAMBRANA, I. R.; BRAUN, L. G. A.; MELO, N. R. da S.; LIMA-GREEN , A.; MOREIRA, G. G.; ARENHART, N.; CATELLA, A. C. Monitoramento da pesca profissional artesanal no Pantanal baseado em um planejamento amostral probabilístico. In: ENCONTRO BRASILEIRO DE ICTIOLOGIA, 23., 2019, Belém, PA. Resumos... Belém, PA: Sociedade Brasileira de Ictiologia, 2019. p. 1041. Biblioteca(s): Embrapa Pantanal. |
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137. | ![Imagem marcado/desmarcado](/consulta/web/img/desmarcado.png) | NAVARRO, T. A.; AGUILA, M. R. D.; GARBELLINI, J. S.; DELBEM, A. C. B.; CATELLA, A. C.; LARA, J. A. F. de. Análises de minerais e composição centesimal em filé de Curimbatá (Prochilodus lineatus). In: ENCONTRO DE INICIAÇÃO CIENTÍFICA DA EMBRAPA PANTANAL E UNIVERSIDADE FEDERAL DE MATO GROSSO DO SUL, 3., SEMANA DE BIOLOGIA, 8. 2009, Corumbá. Resumos...Corumbá: Embrapa Pantanal, 2009. (Embrapa Pantanal. Documentos, 101). p. 16 Biblioteca(s): Embrapa Pantanal. |
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139. | ![Imagem marcado/desmarcado](/consulta/web/img/desmarcado.png) | RESENDE, E. K. de; CATELLA, A. C.; NASCIMENTO, F. L.; PALMEIRA, S. da S.; PEREIRA, R. A. C.; LIMA, M. de S.; ALMEIDA, V. L. L. de. Biologia do curimbata (Prochilodus lineatus), pintado (Pseudoplatystoma corruscans) e cachara (Pseudoplatystoma fasciatum) na bacia hidrografica do rio Miranda, Pantanal do Mato Grosso do Sul, Brasil. Corumba: EMBRAPA-CPAP, 1995. 75p. (EMBRAPA-CPAP. Boletim de Pesquisa, 2). Biblioteca(s): Embrapa Amazônia Ocidental. |
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140. | ![Imagem marcado/desmarcado](/consulta/web/img/desmarcado.png) | RESENDE, E. K. de; CATELLA, A. C.; NASCIMENTO, F. L.; PALMEIRA, S. da S.; PEREIRA, R. A. C.; LIMA, M. de S.; ALMEIDA, V. L. L. de. Biologia do Curimbatá (Prochilodus lineatus), Pintado (Pseudoplatystoma corruscans) e Cachara (Pseudoplatystoma fasciatum) na bacia hidrográfica do Rio Miranda, Pantanal do Mato Grosso do Sul, Brasil. Corumbá: EMBRAPA-CPAP, 1995. 75 p. (EMBRAPA-CPAP. Boletim de Pesquisa, 02). Biblioteca(s): Embrapa Agropecuária Oeste; Embrapa Amazônia Oriental; Embrapa Pantanal; Embrapa Unidades Centrais. |
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Registros recuperados : 159 | |
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![](/consulta/web/img/deny.png) | Acesso ao texto completo restrito à biblioteca da Embrapa Pantanal. Para informações adicionais entre em contato com cpap.biblioteca@embrapa.br. |
Registro Completo
Biblioteca(s): |
Embrapa Pantanal. |
Data corrente: |
30/11/2000 |
Data da última atualização: |
30/11/2000 |
Autoria: |
WILLINK, P. W.; FROEHLICH, O.; MACHADO-ALLISON, A.; MENESES, N.; OYAKAWA, O.; CATELLA, A. C.; CHERNOFF, B.; LIMA, F. C. T.; TOLEDO-PIZA, M.; ORTEGA, H.; ZANATA, A. M.; BARRIGA, R. |
Afiliação: |
Field Museum. Department of Zoology (Chicago); UFMS. Departmento de Biologia (Campo Grande, MS); Universidad Central de Venezuela (Caracas); USP. Museu de Zoologia (Sao Paulo); Embrapa Pantanal (Corumba, MS). |
Título: |
Fishes of the Rios Negro, Negrinho, Taboco, Aquidauana, Taquari, and Miranda, Pantanal, Brasil: diversity, distribution, critical habitats and value. |
Ano de publicação: |
2000 |
Fonte/Imprenta: |
In: WILLINK, P.W.; CHERNOFF, B.; ALONSO, L.E.; MONTAMBAULT, J.R.; LOURIVAL, R., ed. A Biological assessment of the aquatic ecosystem of the Pantanal, Mato Grosso do Sul, Brasil. Washington, DC: Conservation International, 2000. capitulo 6, |
Páginas: |
p.63-81. |
Série: |
(Conservation International. RAP Bulletin of Biological Assessment, 18). |
ISBN: |
1-881173-35-6 |
Idioma: |
Inglês |
Notas: |
Titulo em portugues: Diversidade, distribuicao, e habitats criticos dos peixes dos rios: Negro, Negrinho, Taboco, Taquari e Miranda, e sua importancia para conservacao e desenvolvimento sustentavel do Pantanal, Mato Grosso do Sul, Brasil. |
Conteúdo: |
Fish were sampled from 77 localiteis in the Rio Negro, Upper Rio Taquari, Upper Rio Aquidauana and Upper Rio Miranda drainages. A total of 193 fish species were collected. Of these fish species, 90 (47%) were Characiformes, 72 (37%) were Siluriformes, 15 (8%) were Perciformes and 11(6%) were Gymnotiformes. Cyprinodontiformes (2 species, 1%), Beloniformes (1 species, 0.5%), Synbranchiformes (1 species, 0.5%) and Pleuronectiformes (1 species, 0.5%) were also represented. The family with the most species was Characidae (67 species, 35%), followed by Loricariidae (29 species, 15%) and Cichlidae (15 species, 8%). Of these 193 species, 36 (19%) are believed to be new to science. The specimens collected are believed to be a reasonable representation of the area's ichthyofauna, although additional species are likely to be found in the headwaters and large-bodied fishes were probably undersampled. Endemicity was higher in the headwaters than in the floodplain, probably because of the relatively greater difficulty in dispersing from one headwater drainage to another. The parts of streams located above waterfalls are less productive and diversified than those below. Otherwise, two types of situations were noticed in the headwaters. 1) Relatively unmodified streams with a large number of ecological niches and a high biodiversity. Biodiversity and abundance were particularly high in the clear water limestone areas of the Rio Miranda drainage in Bonito and adjacent areas. 2) Streams heavily impacted by pollution, siltation, and/or deforestation. These streams had few microhabitats and were inhabited mainly by opportunistic species. Biodiversity in the Negro drainage (67 in the Upper Negro to 113 in the Lower Negro, 26 in the Upper Taboco to 77 in the Middle Taboco). This increase in biodiversity is correlated with increases in river size and habitat complexity, with hatitat complexity correlated with the degree of seasonal flooding. Some taxa were collected throughout the drainage, whereas others were collected only in restricted areas. Many juvenile fishes were collected in the bracos mortos (a lateral arm of a river where the upriver channel has been closed), swamps and baias (seasonal lakes or ponds generally isolated from the river system except in times of flooding), emphasizing the importance of these as nursery areas. Terrestrial input of nutrients from riparina vegetation and as a consequence of the seasonal flooding is believed to be critical to the aquatic food chains which support the Pantanal fishes. The majority of an individual's annual growth occurs during the period of high water. Seasonal floods also serve as a cue for many fishes to reproduce, and help to maintain the habitat complexity of the region by rejuvenating the swamps, bracos mortos and baias. These areas, now rich in nutrients function as the nursery areas for fishes. Deforestation is a severe threat because in removes the vegetation from alongside the rivers, decreasing allochthonous input and increasing sedimentation. Disruption of the seasonal flooding (e.g., from local dredging or the Hidrovia Paraguai-Parana) would be catastrophic to the fishes of the Pantanal. MenosFish were sampled from 77 localiteis in the Rio Negro, Upper Rio Taquari, Upper Rio Aquidauana and Upper Rio Miranda drainages. A total of 193 fish species were collected. Of these fish species, 90 (47%) were Characiformes, 72 (37%) were Siluriformes, 15 (8%) were Perciformes and 11(6%) were Gymnotiformes. Cyprinodontiformes (2 species, 1%), Beloniformes (1 species, 0.5%), Synbranchiformes (1 species, 0.5%) and Pleuronectiformes (1 species, 0.5%) were also represented. The family with the most species was Characidae (67 species, 35%), followed by Loricariidae (29 species, 15%) and Cichlidae (15 species, 8%). Of these 193 species, 36 (19%) are believed to be new to science. The specimens collected are believed to be a reasonable representation of the area's ichthyofauna, although additional species are likely to be found in the headwaters and large-bodied fishes were probably undersampled. Endemicity was higher in the headwaters than in the floodplain, probably because of the relatively greater difficulty in dispersing from one headwater drainage to another. The parts of streams located above waterfalls are less productive and diversified than those below. Otherwise, two types of situations were noticed in the headwaters. 1) Relatively unmodified streams with a large number of ecological niches and a high biodiversity. Biodiversity and abundance were particularly high in the clear water limestone areas of the Rio Miranda drainage in Bonito and adjacent areas. 2) Streams heavi... Mostrar Tudo |
Palavras-Chave: |
Brasil; Conservation; Distribuicao; Distribution; Diversidade; Diversity; Ictiofauna. |
Thesagro: |
Conservação; Desenvolvimento Sustentável; Habitat; Peixe; Pesquisa. |
Thesaurus NAL: |
Brazil; fish; Pantanal; research; sustainable development. |
Categoria do assunto: |
-- |
Marc: |
LEADER 04999naa a2200505 a 4500 001 1804355 005 2000-11-30 008 2000 bl uuuu u00u1 u #d 020 $a1-881173-35-6 100 1 $aWILLINK, P. W. 245 $aFishes of the Rios Negro, Negrinho, Taboco, Aquidauana, Taquari, and Miranda, Pantanal, Brasil$bdiversity, distribution, critical habitats and value. 260 $c2000 300 $ap.63-81. 490 $a(Conservation International. RAP Bulletin of Biological Assessment, 18). 500 $aTitulo em portugues: Diversidade, distribuicao, e habitats criticos dos peixes dos rios: Negro, Negrinho, Taboco, Taquari e Miranda, e sua importancia para conservacao e desenvolvimento sustentavel do Pantanal, Mato Grosso do Sul, Brasil. 520 $aFish were sampled from 77 localiteis in the Rio Negro, Upper Rio Taquari, Upper Rio Aquidauana and Upper Rio Miranda drainages. A total of 193 fish species were collected. Of these fish species, 90 (47%) were Characiformes, 72 (37%) were Siluriformes, 15 (8%) were Perciformes and 11(6%) were Gymnotiformes. Cyprinodontiformes (2 species, 1%), Beloniformes (1 species, 0.5%), Synbranchiformes (1 species, 0.5%) and Pleuronectiformes (1 species, 0.5%) were also represented. The family with the most species was Characidae (67 species, 35%), followed by Loricariidae (29 species, 15%) and Cichlidae (15 species, 8%). Of these 193 species, 36 (19%) are believed to be new to science. The specimens collected are believed to be a reasonable representation of the area's ichthyofauna, although additional species are likely to be found in the headwaters and large-bodied fishes were probably undersampled. Endemicity was higher in the headwaters than in the floodplain, probably because of the relatively greater difficulty in dispersing from one headwater drainage to another. The parts of streams located above waterfalls are less productive and diversified than those below. Otherwise, two types of situations were noticed in the headwaters. 1) Relatively unmodified streams with a large number of ecological niches and a high biodiversity. Biodiversity and abundance were particularly high in the clear water limestone areas of the Rio Miranda drainage in Bonito and adjacent areas. 2) Streams heavily impacted by pollution, siltation, and/or deforestation. These streams had few microhabitats and were inhabited mainly by opportunistic species. Biodiversity in the Negro drainage (67 in the Upper Negro to 113 in the Lower Negro, 26 in the Upper Taboco to 77 in the Middle Taboco). This increase in biodiversity is correlated with increases in river size and habitat complexity, with hatitat complexity correlated with the degree of seasonal flooding. Some taxa were collected throughout the drainage, whereas others were collected only in restricted areas. Many juvenile fishes were collected in the bracos mortos (a lateral arm of a river where the upriver channel has been closed), swamps and baias (seasonal lakes or ponds generally isolated from the river system except in times of flooding), emphasizing the importance of these as nursery areas. Terrestrial input of nutrients from riparina vegetation and as a consequence of the seasonal flooding is believed to be critical to the aquatic food chains which support the Pantanal fishes. The majority of an individual's annual growth occurs during the period of high water. Seasonal floods also serve as a cue for many fishes to reproduce, and help to maintain the habitat complexity of the region by rejuvenating the swamps, bracos mortos and baias. These areas, now rich in nutrients function as the nursery areas for fishes. Deforestation is a severe threat because in removes the vegetation from alongside the rivers, decreasing allochthonous input and increasing sedimentation. Disruption of the seasonal flooding (e.g., from local dredging or the Hidrovia Paraguai-Parana) would be catastrophic to the fishes of the Pantanal. 650 $aBrazil 650 $afish 650 $aPantanal 650 $aresearch 650 $asustainable development 650 $aConservação 650 $aDesenvolvimento Sustentável 650 $aHabitat 650 $aPeixe 650 $aPesquisa 653 $aBrasil 653 $aConservation 653 $aDistribuicao 653 $aDistribution 653 $aDiversidade 653 $aDiversity 653 $aIctiofauna 700 1 $aFROEHLICH, O. 700 1 $aMACHADO-ALLISON, A. 700 1 $aMENESES, N. 700 1 $aOYAKAWA, O. 700 1 $aCATELLA, A. C. 700 1 $aCHERNOFF, B. 700 1 $aLIMA, F. C. T. 700 1 $aTOLEDO-PIZA, M. 700 1 $aORTEGA, H. 700 1 $aZANATA, A. M. 700 1 $aBARRIGA, R. 773 $tIn: WILLINK, P.W.; CHERNOFF, B.; ALONSO, L.E.; MONTAMBAULT, J.R.; LOURIVAL, R., ed. A Biological assessment of the aquatic ecosystem of the Pantanal, Mato Grosso do Sul, Brasil. Washington, DC: Conservation International, 2000. capitulo 6
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