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Registro Completo |
Biblioteca(s): |
Embrapa Soja. |
Data corrente: |
30/06/2005 |
Data da última atualização: |
22/05/2006 |
Autoria: |
BROWN, G. G.; OLIVEIRA, L. J. |
Título: |
White grubs as agricultural pests and as ecosystem engineers. |
Ano de publicação: |
2004 |
Fonte/Imprenta: |
In: INTERNATIONAL COLLOQUIUM ON SOIL ZOOLOGY AND ECOLOGY, 14., 2004. Mont Saint Aignan. Abstracts. Mont Saint Aignan: Université de Rouen, 2004. p. 112. |
Idioma: |
Inglês |
Conteúdo: |
The family Melolonthidae (Scarabaeoidae) can be divided into six subfamilies, and in Brazil, the most common larvae living in soils in agroecosystems are of the Rutelinae (e. g., Anomala spp.) and Dynastinae (e. g., Cyclocephala and Bothynus spp.) subfamilies, that feed on OM and rarely on roots and of the Melolonthinae subfamily (e. g., Phyllophaga, Diloboderus spp.), that feed mostly on roots and less on OM. The objective of this study was evaluate the role of Melolonthidae in agroecosystems, where the density of melolonthid larvae in soils can range from a few to >100 individuals m -2. Larvae can vary from less than 1cm, at first instars up to 7cm at the final (3rd) instar. Melolonthid larvae consume from 45 to 80 times their own weight during their development (Móron 1987). Phyllophaga cuyabana in the 3 rd instar, feeding on soybean roots, weigh on average 0.8 to 1g and can consume >30 times their biomass, returning about 16 to 20% to the soil as faeces. In soybean production systems in Brazil, rhizophagous larvae generally tend to become pests in situations where soil biodiversity is reduced, favoring the predominance and population increase of rhizophages, and when the larger individuals (3rd instar) occur in synchrony with the most susceptible plant stages. Furthermore, environmental conditions can also reduce plant tolerance to rhizophagy, or cause the facultativly phytophagous larvae to move from saprophagy to rhizophagy. Obbligatory (e. g., Bothynus spp.) and facultatively (e. g., Diloboderus spp.) saprophagous species are typically more abundant in no-tillage agroecosystems, where the larvae construct vertical tunnels in the soil (galleries up to 3cm wide), connected to the soil surface when they are actively feeding. In samples taken in soybean in Londrina, PR we observed that the total volume of the holes opened by the beetles and/or larvae per surface area (m²), was almost 10 times greater in no-tillage than conventional tillage. On the other hand, population fluctuation of the rhizophagous P. cuyabana was similar in both no- and conventionall-tillage, although rhizophagous larvae also open tunnels (temporary) in the soil, generally for locomotion (searching for food) and pupation. Tunnels of saprophagous species can be abundant (>70m-2) and >1 m deep. Some species bury large amounts of plant litter, contributing to its decomposition and mineralization, significantly increasing P, K and OM content of the galleries compared with adjacent soil (Gassen 1993). These bopores also increase soil porosity and aeration, improve drainage, serve as pathways for root growth and as refuge for many other invertebrates. However, in cases where large saprophagous larvae populations are present, most of the surface litter is rapidly incorported, reducing available resources for other saprophagous organisms (e.g., millipedes, earthworms), possibly reducing their abundance by competition. In sum, due to their physical effects on soils and the induced changes to resource availability in the soil ecosystem, white grubs should be considered as ecosystem engineers. MenosThe family Melolonthidae (Scarabaeoidae) can be divided into six subfamilies, and in Brazil, the most common larvae living in soils in agroecosystems are of the Rutelinae (e. g., Anomala spp.) and Dynastinae (e. g., Cyclocephala and Bothynus spp.) subfamilies, that feed on OM and rarely on roots and of the Melolonthinae subfamily (e. g., Phyllophaga, Diloboderus spp.), that feed mostly on roots and less on OM. The objective of this study was evaluate the role of Melolonthidae in agroecosystems, where the density of melolonthid larvae in soils can range from a few to >100 individuals m -2. Larvae can vary from less than 1cm, at first instars up to 7cm at the final (3rd) instar. Melolonthid larvae consume from 45 to 80 times their own weight during their development (Móron 1987). Phyllophaga cuyabana in the 3 rd instar, feeding on soybean roots, weigh on average 0.8 to 1g and can consume >30 times their biomass, returning about 16 to 20% to the soil as faeces. In soybean production systems in Brazil, rhizophagous larvae generally tend to become pests in situations where soil biodiversity is reduced, favoring the predominance and population increase of rhizophages, and when the larger individuals (3rd instar) occur in synchrony with the most susceptible plant stages. Furthermore, environmental conditions can also reduce plant tolerance to rhizophagy, or cause the facultativly phytophagous larvae to move from saprophagy to rhizophagy. Obbligatory (e. g., Bothynus spp.) and facu... Mostrar Tudo |
Palavras-Chave: |
Ecologia do solo; Fertilidade so solo. |
Thesagro: |
Ecologia Vegetal. |
Categoria do assunto: |
-- |
Marc: |
LEADER 03694naa a2200169 a 4500 001 1464171 005 2006-05-22 008 2004 bl --- 0-- u #d 100 1 $aBROWN, G. G. 245 $aWhite grubs as agricultural pests and as ecosystem engineers. 260 $c2004 520 $aThe family Melolonthidae (Scarabaeoidae) can be divided into six subfamilies, and in Brazil, the most common larvae living in soils in agroecosystems are of the Rutelinae (e. g., Anomala spp.) and Dynastinae (e. g., Cyclocephala and Bothynus spp.) subfamilies, that feed on OM and rarely on roots and of the Melolonthinae subfamily (e. g., Phyllophaga, Diloboderus spp.), that feed mostly on roots and less on OM. The objective of this study was evaluate the role of Melolonthidae in agroecosystems, where the density of melolonthid larvae in soils can range from a few to >100 individuals m -2. Larvae can vary from less than 1cm, at first instars up to 7cm at the final (3rd) instar. Melolonthid larvae consume from 45 to 80 times their own weight during their development (Móron 1987). Phyllophaga cuyabana in the 3 rd instar, feeding on soybean roots, weigh on average 0.8 to 1g and can consume >30 times their biomass, returning about 16 to 20% to the soil as faeces. In soybean production systems in Brazil, rhizophagous larvae generally tend to become pests in situations where soil biodiversity is reduced, favoring the predominance and population increase of rhizophages, and when the larger individuals (3rd instar) occur in synchrony with the most susceptible plant stages. Furthermore, environmental conditions can also reduce plant tolerance to rhizophagy, or cause the facultativly phytophagous larvae to move from saprophagy to rhizophagy. Obbligatory (e. g., Bothynus spp.) and facultatively (e. g., Diloboderus spp.) saprophagous species are typically more abundant in no-tillage agroecosystems, where the larvae construct vertical tunnels in the soil (galleries up to 3cm wide), connected to the soil surface when they are actively feeding. In samples taken in soybean in Londrina, PR we observed that the total volume of the holes opened by the beetles and/or larvae per surface area (m²), was almost 10 times greater in no-tillage than conventional tillage. On the other hand, population fluctuation of the rhizophagous P. cuyabana was similar in both no- and conventionall-tillage, although rhizophagous larvae also open tunnels (temporary) in the soil, generally for locomotion (searching for food) and pupation. Tunnels of saprophagous species can be abundant (>70m-2) and >1 m deep. Some species bury large amounts of plant litter, contributing to its decomposition and mineralization, significantly increasing P, K and OM content of the galleries compared with adjacent soil (Gassen 1993). These bopores also increase soil porosity and aeration, improve drainage, serve as pathways for root growth and as refuge for many other invertebrates. However, in cases where large saprophagous larvae populations are present, most of the surface litter is rapidly incorported, reducing available resources for other saprophagous organisms (e.g., millipedes, earthworms), possibly reducing their abundance by competition. In sum, due to their physical effects on soils and the induced changes to resource availability in the soil ecosystem, white grubs should be considered as ecosystem engineers. 650 $aEcologia Vegetal 653 $aEcologia do solo 653 $aFertilidade so solo 700 1 $aOLIVEIRA, L. J. 773 $tIn: INTERNATIONAL COLLOQUIUM ON SOIL ZOOLOGY AND ECOLOGY, 14., 2004. Mont Saint Aignan. Abstracts. Mont Saint Aignan: Université de Rouen, 2004. p. 112.
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Registro original: |
Embrapa Soja (CNPSO) |
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104. | ![Imagem marcado/desmarcado](/consulta/web/img/desmarcado.png) | KOVALSKI, R.; NIVA, C. C.; BROWN, G. G. Estudo da biologia de um enquitreídeo coletado na região de Colombo, Paraná, Brasil. In: EVENTO DE INICIAÇÃO CIENTÍFICA DA EMBRAPA FLORESTAS, 8., 2009, Colombo. Anais. Colombo: Embrapa Florestas, 2009. 1 CD-ROM. (Embrapa Florestas. Documentos, 186). EVINCI. Resumo.Tipo: Resumo em Anais de Congresso |
Biblioteca(s): Embrapa Florestas. |
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111. | ![Imagem marcado/desmarcado](/consulta/web/img/desmarcado.png) | MASCHIO, W.; VEZZANI, F. M.; BROWN, G. G. Earthworm populations in Eucalyptus spp plantation at Embrapa Forestry, Brazil (Oligochaeta). In: PAVLÍCEK, T.; CARDET, P.; ALMEIDA, M. T.; PASCOAL, C.; CÁSSIO, F. (Ed.). Advances in earthworm taxonomy VI (Annelida: Oligochaeta). Heidelberg: Kasparek Verlag, 2014. p. 114-126. Presented at the 6th International Oligochaete Taxonomy Meeting, Palmeira de Faro, Portugal, 2013.Tipo: Capítulo em Livro Técnico-Científico |
Biblioteca(s): Embrapa Florestas. |
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112. | ![Imagem marcado/desmarcado](/consulta/web/img/desmarcado.png) | KORASAKI, V.; BROWN, G. G.; PASINI, A.; LOPES, J. Earthworm populations in three Atlantic Rainforest fragments with different disturbance levels near Londrina, Paraná, Brazil. In: International Symposium on Earthworm Ecology, 8., 2006, Kraków. Abstracts... Kraków: Jagiellonian University, 2006. p. 74.Biblioteca(s): Embrapa Soja. |
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113. | ![Imagem marcado/desmarcado](/consulta/web/img/desmarcado.png) | BARTZ, M. L. C.; PASINI, A.; BROWN, G. G. Earthworm richness, abundance and biomass in different land use systems in northern Paraná, Brazil (Oligochaeta). In: PAVLÍCEK, T.; CARDET, P.; ALMEIDA, M. T.; PASCOAL, C.; CÁSSIO, F. (Ed.). Advances in earthworm taxonomy VI (Annelida: Oligochaeta). Heidelberg: Kasparek Verlag, 2014. p. 59-73. Presented at the 6th International Oligochaete Taxonomy Meeting, Palmeira de Faro, Portugal, 2013.Tipo: Capítulo em Livro Técnico-Científico |
Biblioteca(s): Embrapa Florestas. |
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114. | ![Imagem marcado/desmarcado](/consulta/web/img/desmarcado.png) | BARTZ, M. L. C.; PASINI, A.; BROWN, G. G. Earthworms in agroecosystems of Northern Paraná, Brazil. 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.Tipo: Resumo em Anais de Congresso |
Biblioteca(s): Embrapa Florestas. |
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115. | ![Imagem marcado/desmarcado](/consulta/web/img/desmarcado.png) | BARTZ, M. L. C.; PASINI, A.; BROWN, G. G. Earthworms from Mato Grosso, Brazil, and new records of species from the state. Pesquisa Agropecuária Brasileira, Brasilia, DF, v. 44, n. 8, p. 934-939, ago. 2009.Tipo: Artigo em Periódico Indexado | Circulação/Nível: B - 1 |
Biblioteca(s): Embrapa Florestas; Embrapa Unidades Centrais. |
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120. | ![Imagem marcado/desmarcado](/consulta/web/img/desmarcado.png) | ORTIZ, C. A.; FRAGOSO, C.; BROWN, G.; EQUIHUA, M. Influence of an exotic worm, soil moisture and quality food on growth, reproduction and cast production of Balanteodrilus pearsei (Acanthodrilini). In: INTERNATIONAL SYMPOSIUM ON EARTHWORM ECOLOGY, 7., 2002, Cardiff. Book of abstracts. Cardiff: Cardiff University, 2002. p.48-49.Biblioteca(s): Embrapa Soja. |
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