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Registro Completo |
Biblioteca(s): |
Embrapa Cerrados; Embrapa Florestas. |
Data corrente: |
18/04/2022 |
Data da última atualização: |
11/07/2022 |
Tipo da produção científica: |
Artigo em Periódico Indexado |
Autoria: |
LAVELLE, P.; MATHIEU, J.; SPAIN. A.; BROWN, G. G.; FRAGOSO, C.; LAPIED, E.; AQUINO, A. de; BAROIS, I.; BARRIOS, E.; BARROS, M. E.; BEDANO, J. C.; BLANCHART, E.; CAULFIELD, M.; CHAGUEZA, Y.; DAI, J.; DECAËNS, T.; DOMINGUEZ, A.; DOMINGUEZ, Y.; FEIJOO, A.; FOLGARAIT, P.; FONTE, S. J.; GOROSITO, N.; HUERTA, E.; JIMENEZ, J. J.; KELLY, C.; LORANGER, G.; MARCHAO, R. L.; MARICHAL, R.; PRAXEDES, C.; RODRIGUEZ, L.; ROUSSEAU, G.; ROUSSEAU, L.; RUIZ, N.; SANABRIA, C.; SUAREZ, J. C.; TONDOH, J. E.; VALENÇA, A. de; VANEK, S. J.; VASQUEZ, J.; VELASQUEZ, E.; WEBSTER, E.; ZHANG, C. |
Afiliação: |
PATRICK LAVELLE, Université Paris-Sorbonne Nouvelle; JÉRÔME MATHIEU, Université Paris-Sorbonne Nouvelle; ALISTER SPAIN; GEORGE GARDNER BROWN, CNPF; CARLOS FRAGOSO, Red Biodiversidad y Sistemática, Instituto de Ecologia A.C., Xalapa; EMMANUEL LAPIED, Taxonomia Biodiversity Fund.; ADRIANA DE AQUINO; ISABELLE BAROIS, Red Ecología Funcional, Instituto de Ecologia A.C., Xalapa; EDMUNDO BARRIOS, FAO; MARIA ELEUSA BARROS, Université Paris-Sorbonne Nouvelle; JOSÉ CAMILO BEDANO, Universidad Nacional de Rio Cuarto; ERIC BLANCHART, Eco& Sols, Université de Montpellier, IRD, CIRAD, INRAe, Institut Agro; MARK CAULFIELD, Eco& Sols, Université de Montpellier, IRD, CIRAD, INRAe, Institut Agro; Wageningen University; YAMILETH CHAGUEZA, Universidad Nacional de Colombia; JUN DAI, South China Agricultural University; THIBAUD DECAËNS, Centre d'Ecologie Fonctionnelle et Evolutive; ANAHI DOMINGUEZ, Universidad Nacional de Rio Cuarto; YAMILETH DOMINGUEZ, Universidad del Atlántico; ALEXANDER FEIJOO, Universidad Tecnológica de Pereira; PATRICIA FOLGARAIT, Universidad Nacional de Quilmes; STEVEN J. FONTE, Colorado State University; NORMA GOROSITO, Universidad Nacional de Quilmes; ESPERANZA HUERTA, HUERTA; Wageningen University and Research; JUAN JOSE JIMENEZ, Pyrenean Institute of Ecology; COURTLAND KELLY, Colorado State University; GLADYS LORANGER, Université des Antilles; ROBELIO LEANDRO MARCHAO, CPAC; RAPHAEL MARICHAL, CIRAD; CATARINA PRAXEDES, Museu Paraense Emilio Goeldi; LEONARDO RODRIGUEZ, Universidad de la Amazonia; GUILLAUME ROUSSEAU, Maranhão State University; LAURENT ROUSSEAU, Université Paris-Sorbonne Nouvelle; NURIA RUIZ, French National Research Agency; CATALINA SANABRIA, UNIVALLE; JUAN CARLOS SUAREZ, Universidad de la Amazonia; JERÔME EBAGNERIN TONDOH, Université Nagui Abrogoua; ANNE DE VALENÇA, Wageningen University; STEVEN J. VANEK, Colorado State University; JOEL VASQUEZ, Instituto de Investigaciones de la Amazonia Peruana; Universidad Nacional de la Amazonia Peruana; ELENA VELASQUEZ, Universidad Nacional de Colombia; EMILY WEBSTER, University of California; CHI ZHANG, South China Agricultural University. |
Título: |
Soil macroinvertebrate communities: a world-wide assessment. |
Ano de publicação: |
2022 |
Fonte/Imprenta: |
Global Ecology and Biogeography, v. 31, n. 7, p. 1261-1276, 2022. |
DOI: |
https://doi.org/10.1111/geb.13492 |
Idioma: |
Inglês Português |
Conteúdo: |
AIM. Macroinvertebrates comprise a highly diverse set of taxa with great potential as indicators of soil quality. Communities were sampled at 3,694 sites distributed world-wide. We aimed to analyse the patterns of abundance, composition and network characteristics and their relationships to latitude, mean annual temperature and rainfall, land cover, soil texture and agricultural practices.
LOCATION. Sites are distributed in 41 countries, ranging from 55° S to 57° N latitude, from 0 to 4,000 m in elevation, with annual rainfall ranging from 500 to >3,000 mm and mean temperatures of 5?32°C.
TIME PERIOD. 1980-2018.
MAJOR TAXA STUDIED.
All soil macroinvertebrates: Haplotaxida; Coleoptera; Formicidae; Arachnida; Chilopoda; Diplopoda; Diptera; Isoptera; Isopoda; Homoptera; Hemiptera; Gastropoda; Blattaria; Orthoptera; Lepidoptera; Dermaptera; and ?others?.
METHODS.
Standard ISO 23611-5 sampling protocol was applied at all sites. Data treatment used a set of multivariate analyses, principal components analysis (PCA) on macrofauna data transformed by Hellinger?s method, multiple correspondence analysis for environmental data (latitude, elevation, temperature and average annual rainfall, type of vegetation cover) transformed into discrete classes, coinertia analysis to compare these two data sets, and bias-corrected and accelerated bootstrap tests to evaluate the part of the variance of the macrofauna data attributable to each of the environmental factors. Network analysis was performed. Each pairwise association of taxonomic units was tested against a null model considering local and regional scales, in order to avoid spurious correlations.
RESULTS
Communities were separated into five clusters reflecting their densities and taxonomic richness. They were significantly influenced by climatic conditions, soil texture and vegetation cover. Abundance and diversity, highest in tropical forests (1,895 ± 234 individuals/m2) and savannahs (1,796 ± 72 individuals/m2), progressively decreased in tropical cropping systems (tree-associated crops, 1,358 ± 120 individuals/m2; pastures, 1,178 ± 154 individuals/m2; and annual crops, 867 ± 62 individuals/m2), temperate grasslands (529 ± 60 individuals/m2), forests (232 ± 20 individuals/m2) and annual crops (231 ± 24 individuals/m2) and temperate dry forests and shrubs (195 ± 11 individuals/m2). Agricultural management decreased overall abundance by ≤54% in tropical areas and 64% in temperate areas. Connectivity varied with taxa, with dominant positive connections in litter transformers and negative connections with ecosystem engineers and Arachnida. Connectivity and modularity were higher in communities with low abundance and taxonomic richness.
MAIN CONCLUSIONS.
Soil macroinvertebrate communities respond to climatic, soil and land-cover conditions. All taxa, except termites, are found everywhere, and communities from the five clusters cover a wide range of geographical and environmental conditions. Agricultural practices significantly decrease abundance, although the presence of tree components alleviates this effect. MenosAIM. Macroinvertebrates comprise a highly diverse set of taxa with great potential as indicators of soil quality. Communities were sampled at 3,694 sites distributed world-wide. We aimed to analyse the patterns of abundance, composition and network characteristics and their relationships to latitude, mean annual temperature and rainfall, land cover, soil texture and agricultural practices.
LOCATION. Sites are distributed in 41 countries, ranging from 55° S to 57° N latitude, from 0 to 4,000 m in elevation, with annual rainfall ranging from 500 to >3,000 mm and mean temperatures of 5?32°C.
TIME PERIOD. 1980-2018.
MAJOR TAXA STUDIED.
All soil macroinvertebrates: Haplotaxida; Coleoptera; Formicidae; Arachnida; Chilopoda; Diplopoda; Diptera; Isoptera; Isopoda; Homoptera; Hemiptera; Gastropoda; Blattaria; Orthoptera; Lepidoptera; Dermaptera; and ?others?.
METHODS.
Standard ISO 23611-5 sampling protocol was applied at all sites. Data treatment used a set of multivariate analyses, principal components analysis (PCA) on macrofauna data transformed by Hellinger?s method, multiple correspondence analysis for environmental data (latitude, elevation, temperature and average annual rainfall, type of vegetation cover) transformed into discrete classes, coinertia analysis to compare these two data sets, and bias-corrected and accelerated bootstrap tests to evaluate the part of the variance of the macrofauna data attributable to each of the environmental factors. Network analysis was perf... Mostrar Tudo |
Palavras-Chave: |
Banco de dados; Cobertura da terra; Communities; Ecologia do solo; Macrofauna; Macrofauna database; Macroinvertebrados; Network analysis; Soil macroinvertebrates. |
Thesaurus Nal: |
Land cover; Soil ecology. |
Categoria do assunto: |
P Recursos Naturais, Ciências Ambientais e da Terra |
Marc: |
LEADER 05077naa a2200757 a 4500 001 2142258 005 2022-07-11 008 2022 bl uuuu u00u1 u #d 024 7 $ahttps://doi.org/10.1111/geb.13492$2DOI 100 1 $aLAVELLE, P. 245 $aSoil macroinvertebrate communities$ba world-wide assessment.$h[electronic resource] 260 $c2022 520 $aAIM. Macroinvertebrates comprise a highly diverse set of taxa with great potential as indicators of soil quality. Communities were sampled at 3,694 sites distributed world-wide. We aimed to analyse the patterns of abundance, composition and network characteristics and their relationships to latitude, mean annual temperature and rainfall, land cover, soil texture and agricultural practices. LOCATION. Sites are distributed in 41 countries, ranging from 55° S to 57° N latitude, from 0 to 4,000 m in elevation, with annual rainfall ranging from 500 to >3,000 mm and mean temperatures of 5?32°C. TIME PERIOD. 1980-2018. MAJOR TAXA STUDIED. All soil macroinvertebrates: Haplotaxida; Coleoptera; Formicidae; Arachnida; Chilopoda; Diplopoda; Diptera; Isoptera; Isopoda; Homoptera; Hemiptera; Gastropoda; Blattaria; Orthoptera; Lepidoptera; Dermaptera; and ?others?. METHODS. Standard ISO 23611-5 sampling protocol was applied at all sites. Data treatment used a set of multivariate analyses, principal components analysis (PCA) on macrofauna data transformed by Hellinger?s method, multiple correspondence analysis for environmental data (latitude, elevation, temperature and average annual rainfall, type of vegetation cover) transformed into discrete classes, coinertia analysis to compare these two data sets, and bias-corrected and accelerated bootstrap tests to evaluate the part of the variance of the macrofauna data attributable to each of the environmental factors. Network analysis was performed. Each pairwise association of taxonomic units was tested against a null model considering local and regional scales, in order to avoid spurious correlations. RESULTS Communities were separated into five clusters reflecting their densities and taxonomic richness. They were significantly influenced by climatic conditions, soil texture and vegetation cover. Abundance and diversity, highest in tropical forests (1,895 ± 234 individuals/m2) and savannahs (1,796 ± 72 individuals/m2), progressively decreased in tropical cropping systems (tree-associated crops, 1,358 ± 120 individuals/m2; pastures, 1,178 ± 154 individuals/m2; and annual crops, 867 ± 62 individuals/m2), temperate grasslands (529 ± 60 individuals/m2), forests (232 ± 20 individuals/m2) and annual crops (231 ± 24 individuals/m2) and temperate dry forests and shrubs (195 ± 11 individuals/m2). Agricultural management decreased overall abundance by ≤54% in tropical areas and 64% in temperate areas. Connectivity varied with taxa, with dominant positive connections in litter transformers and negative connections with ecosystem engineers and Arachnida. Connectivity and modularity were higher in communities with low abundance and taxonomic richness. MAIN CONCLUSIONS. Soil macroinvertebrate communities respond to climatic, soil and land-cover conditions. All taxa, except termites, are found everywhere, and communities from the five clusters cover a wide range of geographical and environmental conditions. Agricultural practices significantly decrease abundance, although the presence of tree components alleviates this effect. 650 $aLand cover 650 $aSoil ecology 653 $aBanco de dados 653 $aCobertura da terra 653 $aCommunities 653 $aEcologia do solo 653 $aMacrofauna 653 $aMacrofauna database 653 $aMacroinvertebrados 653 $aNetwork analysis 653 $aSoil macroinvertebrates 700 1 $aMATHIEU, J. 700 1 $aSPAIN. A. 700 1 $aBROWN, G. G. 700 1 $aFRAGOSO, C. 700 1 $aLAPIED, E. 700 1 $aAQUINO, A. de 700 1 $aBAROIS, I. 700 1 $aBARRIOS, E. 700 1 $aBARROS, M. E. 700 1 $aBEDANO, J. C. 700 1 $aBLANCHART, E. 700 1 $aCAULFIELD, M. 700 1 $aCHAGUEZA, Y. 700 1 $aDAI, J. 700 1 $aDECAËNS, T. 700 1 $aDOMINGUEZ, A. 700 1 $aDOMINGUEZ, Y. 700 1 $aFEIJOO, A. 700 1 $aFOLGARAIT, P. 700 1 $aFONTE, S. J. 700 1 $aGOROSITO, N. 700 1 $aHUERTA, E. 700 1 $aJIMENEZ, J. J. 700 1 $aKELLY, C. 700 1 $aLORANGER, G. 700 1 $aMARCHAO, R. L. 700 1 $aMARICHAL, R. 700 1 $aPRAXEDES, C. 700 1 $aRODRIGUEZ, L. 700 1 $aROUSSEAU, G. 700 1 $aROUSSEAU, L. 700 1 $aRUIZ, N. 700 1 $aSANABRIA, C. 700 1 $aSUAREZ, J. C. 700 1 $aTONDOH, J. E. 700 1 $aVALENÇA, A. de 700 1 $aVANEK, S. J. 700 1 $aVASQUEZ, J. 700 1 $aVELASQUEZ, E. 700 1 $aWEBSTER, E. 700 1 $aZHANG, C. 773 $tGlobal Ecology and Biogeography$gv. 31, n. 7, p. 1261-1276, 2022.
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Embrapa Florestas (CNPF) |
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Biblioteca(s): |
Embrapa Amazônia Oriental. |
Data corrente: |
14/03/2013 |
Data da última atualização: |
27/10/2023 |
Tipo da produção científica: |
Artigo em Anais de Congresso |
Autoria: |
SILVA, P. A.; MELO, W. S.; CUNHA, R. L.; CUNHA, E. F. M.; LOPES, A. S.; PENA, R. S. |
Afiliação: |
PRISCILLA ANDRADE SILVA, UFPA; W. S. MELO, UNIVERSIDADE ESTADUAL DE CAMPINAS; ROBERTO LISBOA CUNHA, CPATU; ELISA FERREIRA MOURA CUNHA, CPATU; A. S. LOPES, UFPA; ROSINELSON DA SILVA PENA, UFPA. |
Título: |
Caracterização de farinhas de tapioca comerciais produzidas no Estado do Pará. |
Ano de publicação: |
2012 |
Fonte/Imprenta: |
In: CONGRESSO BRASILEIRO DE ENGENHARIA QUÍMICA, 19., 2012, Búzios. Anais... São Paulo: Associação Brasileira de Engenharia Química, 2012. |
Páginas: |
p. 8269-8277. |
Idioma: |
Português |
Conteúdo: |
A farinha de tapioca é um alimento produzido artesanalmente a partir da fécula de mandioca (Manihot esculenta Crantz) purificada. É muito consumida na Região Amazônica, na forma de mingaus, roscas, bolos, pudins, sorvetes, bem corno no acompanhamento da bebida regional açaí. No estado do Pará, particularmente na Zona Bragantina, estão situadas as "casas de farinha de tapioca", onde a farinha é elaborada de forma artesanal e em pequena escala. O objetivo deste trabalho foi caracterizar duas farinhas de tapioca com características distintas, produzidas no estado do Pará: uma no Baixo Amazonas (município de Santarém) e outra na Zona Bragantina (município de Santa Izabel). As duas farinhas de tapioca apresentaram perfis granulométricos distintos, e diferença significativa (p<0,05) para a maioria dos parâmetros físico-químicos e tecnológicos analisados. A farinha proveniente de Santarém apresentou maior umidade (10,7%), que pode ser justificada pela maior capacidade de adsorver água, devido a sua maior área específica (menor granulometria). A eletromicrografia de varredura indicou diâmetro médio dos grânulos de amido das farinhas de Santa Izabel e de Santarém de 30 e 15 um, respectivamente. A partir das características dos dois produtos analisados, foi possível constatar que não existe um processo padrão utilizado na produção da farinha de tapioca |
Palavras-Chave: |
Fécula de mandioca. |
Thesagro: |
Farinha; Mandioca; Manihot Esculenta; Tapioca. |
Thesaurus NAL: |
Amazonia. |
Categoria do assunto: |
Q Alimentos e Nutrição Humana |
URL: |
https://ainfo.cnptia.embrapa.br/digital/bitstream/item/104553/1/SEPARATAS-6807.pdf
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Marc: |
LEADER 02170nam a2200253 a 4500 001 1953096 005 2023-10-27 008 2012 bl uuuu u00u1 u #d 100 1 $aSILVA, P. A. 245 $aCaracterização de farinhas de tapioca comerciais produzidas no Estado do Pará. 260 $aIn: CONGRESSO BRASILEIRO DE ENGENHARIA QUÍMICA, 19., 2012, Búzios. Anais... São Paulo: Associação Brasileira de Engenharia Química$c2012 300 $ap. 8269-8277. 520 $aA farinha de tapioca é um alimento produzido artesanalmente a partir da fécula de mandioca (Manihot esculenta Crantz) purificada. É muito consumida na Região Amazônica, na forma de mingaus, roscas, bolos, pudins, sorvetes, bem corno no acompanhamento da bebida regional açaí. No estado do Pará, particularmente na Zona Bragantina, estão situadas as "casas de farinha de tapioca", onde a farinha é elaborada de forma artesanal e em pequena escala. O objetivo deste trabalho foi caracterizar duas farinhas de tapioca com características distintas, produzidas no estado do Pará: uma no Baixo Amazonas (município de Santarém) e outra na Zona Bragantina (município de Santa Izabel). As duas farinhas de tapioca apresentaram perfis granulométricos distintos, e diferença significativa (p<0,05) para a maioria dos parâmetros físico-químicos e tecnológicos analisados. A farinha proveniente de Santarém apresentou maior umidade (10,7%), que pode ser justificada pela maior capacidade de adsorver água, devido a sua maior área específica (menor granulometria). A eletromicrografia de varredura indicou diâmetro médio dos grânulos de amido das farinhas de Santa Izabel e de Santarém de 30 e 15 um, respectivamente. A partir das características dos dois produtos analisados, foi possível constatar que não existe um processo padrão utilizado na produção da farinha de tapioca 650 $aAmazonia 650 $aFarinha 650 $aMandioca 650 $aManihot Esculenta 650 $aTapioca 653 $aFécula de mandioca 700 1 $aMELO, W. S. 700 1 $aCUNHA, R. L. 700 1 $aCUNHA, E. F. M. 700 1 $aLOPES, A. S. 700 1 $aPENA, R. S.
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