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 | Acesso ao texto completo restrito à biblioteca da Embrapa Florestas. Para informações adicionais entre em contato com cnpf.biblioteca@embrapa.br. |
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Registro Completo |
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Biblioteca(s): |
Embrapa Florestas. |
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Data corrente: |
31/03/2023 |
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Data da última atualização: |
17/08/2023 |
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Tipo da produção científica: |
Artigo em Periódico Indexado |
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Autoria: |
DUDAS, R. T.; DEMETRIO, W. C.; MAIA, L. S.; SÁTIRO, J. N. O.; SILVA, K. A.; NICOLA, V. B.; KILLE, P.; OLIVEIRA, C. M. R.; AFONSO, R. O.; RUSSELL, G.; FERREIRA, N. G. C.; CUNHA, L.; BROWN, G. G.; BARTZ, M. L. C. |
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Afiliação: |
RAFAELA T. DUDAS, UNIVERSIDADE POSITIVO; WILIAN C. DEMETRIO, UNIVERSIDADE FEDERAL DO PARANA; LILIANE S. MAIA, UNIVERSIDADE FEDERAL DO PARANA; JOSÉ N. O. SÁTIRO, UNIVERSIDADE FEDERAL DO PARANA; KARLO A. SILVA, UNIVERSIDADE POSITIVO; VITORIA B. NICOLA, UNIVERSIDADE POSITIVO; PETER KILLE, UNIVERSIDADE DE CARDIFF; CINTÍA M. R. OLIVEIRA, UNIVERSIDADE POSITIVO; RITA O. AFONSO, UNIVERSIDADE DE CARDIFF; GEORGINA RUSSELL, UNIVERSIDADE DE CARDIFF; NUNO G. C. FERREIRA, UNIVERSIDADE DE CARDIFF; LUIS CUNHA, UNIVERSIDADE DE COIMBRA; GEORGE GARDNER BROWN, CNPF; MARIE L. C. BARTZ, UNIVERSIDADE POSITIVO. |
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Título: |
Earthworm communities in long-term no-tillage systems and secondary forest fragments in Paraná, Southern Brazil. |
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Ano de publicação: |
2023 |
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Fonte/Imprenta: |
Zootaxa, v. 5255, n. 1, p. 347-361, 2023. |
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DOI: |
https://doi.org/10.11646/zootaxa.5255.1.28 |
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Idioma: |
Inglês |
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Conteúdo: |
The area destined for agricultural production in Paraná state in Brazil is ~6 million hectares, of which 79% are under notillage systems (NTS) that can positively affect earthworm populations. Furthermore, earthworm abundance and richness can be valuable soil quality. This study assessed earthworm communities in long-term no-tillage sites (NTS) and nearby secondary Atlantic Forest (SF) fragments. Sampling was performed in June 2018 and May 2019 using the quantitative Tropical Soil Biology and Fertility handsorting method (ISO-TSBF), complemented by qualitative sampling in three municipalities: Faxinal, Mauá da Serra and Palmeira, in NTS and SF. Eleven earthworm species, belonging to five families (Benhamiidae, Glossoscolecidae, Megascolecidae, Ocnerodrilidae, and Rhinodrilidae) were found along with seven native species (Glossoscolex sp.22, Glossoscolex sp.23, Fimoscolex sp.21, Fimoscolex sp.24, Fimoscolex sp.42, Andiorrhinus duseni and Urobenus brasiliensis) and four exotic or cosmopolitan species (Dichogaster gracilis, Amynthas gracilis, Metaphire californica and Pontoscolex corethrurus). The cosmopolitan P. corethrurus dominated Faxinal and Mauá da Serra, while in Palmeira Fimoscolex and Glossoscolex were the most abundant. Six species belonging to Glossoscolex and Fimoscolex were new to science and must be described. Overall, 239 individuals were found. In 2018 126 individuals were found (76 in NTS and 50 in SF) and in 2019, only 112 individuals were found (45 in NTS and 67 in SF). The highest earthworm abundance was in Faxinal (123 individuals), with 76 individuals in NTS and 47 in SF. In Mauá da Serra the same pattern was observed (SF>NTS), while in Palmeira in overall, fewer individuals (38) were collected (24 in NTS and 14 in SF). The NTS at Faxinal and SF Mauá da Serra in 2019 had only/more exotic/cosmopolitan species, while at the other dates and sites >50% of the specimens sampled were native species. Overall, forests had more native species than exotics: in 2018, natives represented > 75% of all specimens, but in 2019 both Faxinal and Mauá da Serra had more exotic species (> 65%), while at Palmeira, they represented 50% of the individuals. Earthworm total biomass for forest sites was higher in Faxinal (3.2 g) and NTS in Mauá da Serra (1.7 g) in 2019. Overall, the total biomass was higher in SF sites than NTS. Using a classification available for earthworm populations in no-tillage systems, all three sites were considered to have poor quality in terms of abundance (ind m-2), while for species richness, they were considered to have moderate (Faxinal and Mauá da Serra) and good quality (Palmeira). MenosThe area destined for agricultural production in Paraná state in Brazil is ~6 million hectares, of which 79% are under notillage systems (NTS) that can positively affect earthworm populations. Furthermore, earthworm abundance and richness can be valuable soil quality. This study assessed earthworm communities in long-term no-tillage sites (NTS) and nearby secondary Atlantic Forest (SF) fragments. Sampling was performed in June 2018 and May 2019 using the quantitative Tropical Soil Biology and Fertility handsorting method (ISO-TSBF), complemented by qualitative sampling in three municipalities: Faxinal, Mauá da Serra and Palmeira, in NTS and SF. Eleven earthworm species, belonging to five families (Benhamiidae, Glossoscolecidae, Megascolecidae, Ocnerodrilidae, and Rhinodrilidae) were found along with seven native species (Glossoscolex sp.22, Glossoscolex sp.23, Fimoscolex sp.21, Fimoscolex sp.24, Fimoscolex sp.42, Andiorrhinus duseni and Urobenus brasiliensis) and four exotic or cosmopolitan species (Dichogaster gracilis, Amynthas gracilis, Metaphire californica and Pontoscolex corethrurus). The cosmopolitan P. corethrurus dominated Faxinal and Mauá da Serra, while in Palmeira Fimoscolex and Glossoscolex were the most abundant. Six species belonging to Glossoscolex and Fimoscolex were new to science and must be described. Overall, 239 individuals were found. In 2018 126 individuals were found (76 in NTS and 50 in SF) and in 2019, only 112 individuals were found (45 in NTS and... Mostrar Tudo |
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Palavras-Chave: |
Conservation agriculture; Ecosystem engineer; Soil macrofauna. |
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Thesagro: |
Conservação do Solo; Ecossistema; Fertilidade do Solo; Minhoca. |
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Thesaurus Nal: |
Earthworms; Oligochaeta. |
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Categoria do assunto: |
P Recursos Naturais, Ciências Ambientais e da Terra |
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Marc: |
LEADER 03816naa a2200397 a 4500
001 2152915
005 2023-08-17
008 2023 bl uuuu u00u1 u #d
024 7 $ahttps://doi.org/10.11646/zootaxa.5255.1.28$2DOI
100 1 $aDUDAS, R. T.
245 $aEarthworm communities in long-term no-tillage systems and secondary forest fragments in Paraná, Southern Brazil.$h[electronic resource]
260 $c2023
520 $aThe area destined for agricultural production in Paraná state in Brazil is ~6 million hectares, of which 79% are under notillage systems (NTS) that can positively affect earthworm populations. Furthermore, earthworm abundance and richness can be valuable soil quality. This study assessed earthworm communities in long-term no-tillage sites (NTS) and nearby secondary Atlantic Forest (SF) fragments. Sampling was performed in June 2018 and May 2019 using the quantitative Tropical Soil Biology and Fertility handsorting method (ISO-TSBF), complemented by qualitative sampling in three municipalities: Faxinal, Mauá da Serra and Palmeira, in NTS and SF. Eleven earthworm species, belonging to five families (Benhamiidae, Glossoscolecidae, Megascolecidae, Ocnerodrilidae, and Rhinodrilidae) were found along with seven native species (Glossoscolex sp.22, Glossoscolex sp.23, Fimoscolex sp.21, Fimoscolex sp.24, Fimoscolex sp.42, Andiorrhinus duseni and Urobenus brasiliensis) and four exotic or cosmopolitan species (Dichogaster gracilis, Amynthas gracilis, Metaphire californica and Pontoscolex corethrurus). The cosmopolitan P. corethrurus dominated Faxinal and Mauá da Serra, while in Palmeira Fimoscolex and Glossoscolex were the most abundant. Six species belonging to Glossoscolex and Fimoscolex were new to science and must be described. Overall, 239 individuals were found. In 2018 126 individuals were found (76 in NTS and 50 in SF) and in 2019, only 112 individuals were found (45 in NTS and 67 in SF). The highest earthworm abundance was in Faxinal (123 individuals), with 76 individuals in NTS and 47 in SF. In Mauá da Serra the same pattern was observed (SF>NTS), while in Palmeira in overall, fewer individuals (38) were collected (24 in NTS and 14 in SF). The NTS at Faxinal and SF Mauá da Serra in 2019 had only/more exotic/cosmopolitan species, while at the other dates and sites >50% of the specimens sampled were native species. Overall, forests had more native species than exotics: in 2018, natives represented > 75% of all specimens, but in 2019 both Faxinal and Mauá da Serra had more exotic species (> 65%), while at Palmeira, they represented 50% of the individuals. Earthworm total biomass for forest sites was higher in Faxinal (3.2 g) and NTS in Mauá da Serra (1.7 g) in 2019. Overall, the total biomass was higher in SF sites than NTS. Using a classification available for earthworm populations in no-tillage systems, all three sites were considered to have poor quality in terms of abundance (ind m-2), while for species richness, they were considered to have moderate (Faxinal and Mauá da Serra) and good quality (Palmeira).
650 $aEarthworms
650 $aOligochaeta
650 $aConservação do Solo
650 $aEcossistema
650 $aFertilidade do Solo
650 $aMinhoca
653 $aConservation agriculture
653 $aEcosystem engineer
653 $aSoil macrofauna
700 1 $aDEMETRIO, W. C.
700 1 $aMAIA, L. S.
700 1 $aSÁTIRO, J. N. O.
700 1 $aSILVA, K. A.
700 1 $aNICOLA, V. B.
700 1 $aKILLE, P.
700 1 $aOLIVEIRA, C. M. R.
700 1 $aAFONSO, R. O.
700 1 $aRUSSELL, G.
700 1 $aFERREIRA, N. G. C.
700 1 $aCUNHA, L.
700 1 $aBROWN, G. G.
700 1 $aBARTZ, M. L. C.
773 $tZootaxa$gv. 5255, n. 1, p. 347-361, 2023.
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Registro original: |
Embrapa Florestas (CNPF) |
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Biblioteca |
ID |
Origem |
Tipo/Formato |
Classificação |
Cutter |
Registro |
Volume |
Status |
URL |
Voltar
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Registro Completo
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Biblioteca(s): |
Embrapa Amazônia Ocidental; Embrapa Amazônia Oriental; Embrapa Florestas; Embrapa Solos. |
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Data corrente: |
19/07/2021 |
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Data da última atualização: |
13/09/2021 |
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Tipo da produção científica: |
Artigo em Periódico Indexado |
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Circulação/Nível: |
A - 1 |
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Autoria: |
DEMETRIO, W. C.; CONRADO, A. C.; ACIOLI, A. N. S.; FERREIRA, A. C.; BARTZ, M. L. C.; JAMES, S. W.; SILVA, E. da; MAIA, L. S.; MARTINS, G. C.; MACEDO, R. S.; STANTON, D. W. G.; LAVELLE, P.; VELASQUEZ, E.; ZANGERLÉ, A.; BARBOSA, R.; TAPIA-CORAL, S. C.; MUNIZ, A. W.; SANTOS, A.; FERREIRA, T.; SEGALLA, R. F.; DECAËNS, T.; NADOLNY, H. S.; PEÑA-VENEGAS, C. P.; MAIA, C. M. B. F.; PASINI, A.; MOTA, A. F.; TAUBE JÚNIOR, P. S.; SILVA, T. A. C.; REBELLATO, L.; OLIVEIRA JUNIOR, R. C. de; NEVES, E. G.; LIMA, H. P.; FEITOSA, R. M.; TORRADO, P. V.; McKEY, D.; CLEMENT, C. R.; SHOCK, M. P.; TEIXEIRA, W. G.; MOTTA, A. C. V.; MELO, V. F.; DIECKOW, J.; GARRASTAZU, M. C.; CHUBATSU, L. S.; KILLE, P.; BROWN, G. G.; CUNHA, L. |
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Afiliação: |
WILIAN C. DEMETRIO, Federal University of Paraná; ANA C. CONRADO, Federal University of Paraná; AGNO N. S. ACIOLI, UFAM; ALEXANDRE C. FERREIRA, Federal University of Paraná; MARIE L. C. BARTZ, University of Coimbra; SAMUEL W. JAMES, Maharishi International University; ELODIE DA SILVA, CNPF; LILIANNE S. MAIA, Federal University of Paraná; GILVAN COIMBRA MARTINS, CPAA; RODRIGO S. MACEDO, Instituto Nacional do Semiárido; DAVID W. G. STANTON, Swedish Museum of Natural History; PATRICK LAVELLE, Institut de Recherche pour le Développement; ELENA VELASQUEZ, Universidad Nacional de Colombia; ANNE ZANGERLÉ, Ministère de l’Agriculture, de la Viticulture et de la Protection des consommateurs; RAFAELLA BARBOSA, Centro Universitário do Norte; SANDRA C. TAPIA-CORAL, Servicio Nacional de Aprendizaje; ALEKSANDER WESTPHAL MUNIZ, CPAA; ALESSANDRA SANTOS, Federal University of Paraná; TALITA FERREIRA, Federal University of Paraná; RODRIGO F. SEGALLA, Federal University of Paraná; THIBAUD DECAËNS, CEFE, Univ Montpellier; HERLON S. NADOLNY, Federal University of Paraná; CLARA P. PEÑA-VENEGAS, Instituto Amazónico de Investigaciones Científicas SINCHI; CLÁUDIA M. B. F. MAIA, CNPF; AMARILDO PASINI, Universidade Estadual de Londrina; ANDRÉ F. MOTA, Federal University of Paraná; PAULO S. TAUBE JÚNIOR, Universidade Federal do Oeste do Pará; TELMA A. C. SILVA, INPA; LILIAN REBELLATO, Universidade Federal do Oeste do Pará; RAIMUNDO COSME DE OLIVEIRA JUNIOR, CPATU; EDUARDO G. NEVES, Museu de Arqueologia e Etnologia, Universidade de São Paulo; HELENA P. LIMA, Museu Paraense Emílio Goeldi; RODRIGO M. FEITOSA, Federal University of Paraná; PABLO VIDAL TORRADO, ESALQ; DOYLE MCKEY, CEFE, Univ Montpellier, CNRS; CHARLES R. CLEMENT, INPA; MYRTLE P. SHOCK, Universidade Federal do Oeste do Pará; WENCESLAU GERALDES TEIXEIRA, CNPS; ANTÔNIO C. V. MOTTA, Federal University of Paraná; VANDER F. MELO, Federal University of Paraná; JEFERSON DIECKOW, Federal University of Paraná; MARILICE CORDEIRO GARRASTAZU, CNPF; LEDA S. CHUBATSU, Federal University of Paraná; PETER KILLE, Cardiff University; GEORGE GARDNER BROWN, CNPF; LUÍS CUNHA, University of Coimbra. |
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Título: |
A "dirty" footprint: macroinvertebrate diversity in Amazonian Anthropic soils. |
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Ano de publicação: |
2021 |
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Fonte/Imprenta: |
Global Change Biology, v. 27, n. 19, p. 4575-4591, Oct. 2021. |
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DOI: |
10.1111/gcb.15752 |
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Idioma: |
Inglês |
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Conteúdo: |
Amazonian rainforests, once thought to be pristine wilderness, are increasingly known to have been widely inhabited, modified, and managed prior to European arrival, by human populations with diverse cultural backgrounds. Amazonian Dark Earths (ADEs) are fertile soils found throughout the Amazon Basin, created by pre-Columbian societies with sedentary habits. Much is known about the chemistry of these soils, yet their zoology has been neglected. Hence, we characterized soil fertility, macroinvertebrate communities, and their activity at nine archeological sites in three Amazonian regions in ADEs and adjacent reference soils under native forest (young and old) and agricultural systems. |
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Palavras-Chave: |
Amazonian Dark Earths; Ants; Archeological sites; Termites; Terra Preta de Índio. |
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Thesagro: |
Biodiversidade; Biologia do Solo; Cupim; Fauna; Fertilidade do Solo; Formiga; Minhoca; Uso da Terra. |
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Thesaurus NAL: |
Anthrosols; Earthworms; Formicidae; Land use change; Soil biology; Soil fauna; Soil fertility. |
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Categoria do assunto: |
--
P Recursos Naturais, Ciências Ambientais e da Terra |
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URL: |
https://ainfo.cnptia.embrapa.br/digital/bitstream/item/225924/1/gcb.15752.pdf
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Marc: |
LEADER 03074naa a2200913 a 4500
001 2133025
005 2021-09-13
008 2021 bl uuuu u00u1 u #d
024 7 $a10.1111/gcb.15752$2DOI
100 1 $aDEMETRIO, W. C.
245 $aA "dirty" footprint$bmacroinvertebrate diversity in Amazonian Anthropic soils.$h[electronic resource]
260 $c2021
520 $aAmazonian rainforests, once thought to be pristine wilderness, are increasingly known to have been widely inhabited, modified, and managed prior to European arrival, by human populations with diverse cultural backgrounds. Amazonian Dark Earths (ADEs) are fertile soils found throughout the Amazon Basin, created by pre-Columbian societies with sedentary habits. Much is known about the chemistry of these soils, yet their zoology has been neglected. Hence, we characterized soil fertility, macroinvertebrate communities, and their activity at nine archeological sites in three Amazonian regions in ADEs and adjacent reference soils under native forest (young and old) and agricultural systems.
650 $aAnthrosols
650 $aEarthworms
650 $aFormicidae
650 $aLand use change
650 $aSoil biology
650 $aSoil fauna
650 $aSoil fertility
650 $aBiodiversidade
650 $aBiologia do Solo
650 $aCupim
650 $aFauna
650 $aFertilidade do Solo
650 $aFormiga
650 $aMinhoca
650 $aUso da Terra
653 $aAmazonian Dark Earths
653 $aAnts
653 $aArcheological sites
653 $aTermites
653 $aTerra Preta de Índio
700 1 $aCONRADO, A. C.
700 1 $aACIOLI, A. N. S.
700 1 $aFERREIRA, A. C.
700 1 $aBARTZ, M. L. C.
700 1 $aJAMES, S. W.
700 1 $aSILVA, E. da
700 1 $aMAIA, L. S.
700 1 $aMARTINS, G. C.
700 1 $aMACEDO, R. S.
700 1 $aSTANTON, D. W. G.
700 1 $aLAVELLE, P.
700 1 $aVELASQUEZ, E.
700 1 $aZANGERLÉ, A.
700 1 $aBARBOSA, R.
700 1 $aTAPIA-CORAL, S. C.
700 1 $aMUNIZ, A. W.
700 1 $aSANTOS, A.
700 1 $aFERREIRA, T.
700 1 $aSEGALLA, R. F.
700 1 $aDECAËNS, T.
700 1 $aNADOLNY, H. S.
700 1 $aPEÑA-VENEGAS, C. P.
700 1 $aMAIA, C. M. B. F.
700 1 $aPASINI, A.
700 1 $aMOTA, A. F.
700 1 $aTAUBE JÚNIOR, P. S.
700 1 $aSILVA, T. A. C.
700 1 $aREBELLATO, L.
700 1 $aOLIVEIRA JUNIOR, R. C. de
700 1 $aNEVES, E. G.
700 1 $aLIMA, H. P.
700 1 $aFEITOSA, R. M.
700 1 $aTORRADO, P. V.
700 1 $aMcKEY, D.
700 1 $aCLEMENT, C. R.
700 1 $aSHOCK, M. P.
700 1 $aTEIXEIRA, W. G.
700 1 $aMOTTA, A. C. V.
700 1 $aMELO, V. F.
700 1 $aDIECKOW, J.
700 1 $aGARRASTAZU, M. C.
700 1 $aCHUBATSU, L. S.
700 1 $aKILLE, P.
700 1 $aBROWN, G. G.
700 1 $aCUNHA, L.
773 $tGlobal Change Biology$gv. 27, n. 19, p. 4575-4591, Oct. 2021.
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Registro original: |
Embrapa Florestas (CNPF) |
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ID |
Origem |
Tipo/Formato |
Classificação |
Cutter |
Registro |
Volume |
Status |
Fechar
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Registro completo
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Biblioteca(s): |
Catálogo Coletivo de Periódicos Embrapa; Embrapa Algodão; Embrapa Amapá; Embrapa Amazônia Oriental; Embrapa Arroz e Feijão; Embrapa Cerrados; Embrapa Mandioca e Fruticultura; Embrapa Meio-Norte; Embrapa Pantanal; Embrapa Rondônia; Embrapa Semiárido; Embrapa Soja; Embrapa Trigo; Embrapa Uva e Vinho. MenosCatálogo Coletivo de Periódicos Embrapa; Embrapa Algodão; Embrapa Amapá; Embrapa Amazônia Oriental; Embrapa Arroz e Feijão; Embrapa Cerrados; Embrapa Mandioca e Fruticultura; Embrapa Meio-Norte; Embrapa Pantanal; Embrapa Rondônia... Mostrar Todas |
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Identificador: |
2826 |
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Data corrente: |
09/05/2002 |
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Data da última atualização: |
09/05/2002 |
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Código do título: |
0900592 |
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ISSN: |
0100-6967 |
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Código CCN: |
027582-4 |
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Título e Subtítulo: |
DIVULGACAO AGRONOMICA |
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Entidade: |
Shell Quimica S.A. |
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Local de publicação: |
Sao Paulo-SP |
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Periodicidade: |
irregular |
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Inicio de publicação: |
1959 |
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Coleções da unidade: |
Embrapa Algodão
1961/79 (3,5-9,11,13,14-19,21-46)
Classificação: 632.05
Embrapa Amapá
1966 (22); 1969 (27); 1972 (32); 1973 (33); 1975 (36); 1976 (39-41); 1978 (43-44); 1979 (46)
Embrapa Amazônia Oriental
1959 (1); 1960 (2); 1961 (3-4); 1962 (5-8); 1963 (10); 1964 (11-13); 1965 (14-17); 1966 (18-22); 1967 (23); 1968 (24-26); 1969 (27); 1970 (28-29); 1971 (30-31); 1972 (32); 1973 (33); 1974 (34-35); 1975 (36-37); 1976 (38-41); 1977 (42); 1978 (43-44); 1979 (45-46); 1980 (47)
Classificação: 632.05D518
Embrapa Arroz e Feijão
1960 (1); 1962 (6); 1963 (10); 1964 (12-13,15); 1965 (16-17); 1966 (19,22); 1967 (23); 1968 (24-26); 1969 (27); 1970 (28-29); 1971 (30-31); 1972 (32); 1973 (33); 1974 (34-35); 1975 (36-37); 1976 (38-40); 1977 (42); 1978 (43-44); 1979 (45)
Embrapa Cerrados
1959-60 (1-2); 1961 (4); 1962 (6); 1964 (11); 1965; 1966 (18-22); 1968 (24,26); 1969 (27); 1970-80 (28-47)
Classificação: 632.05
Embrapa Mandioca e Fruticultura
1960(1-2); 1961(3-4); 1962(5-8); 1963(9-10); 1964(11-13); 1965(14-17); 1966(18-22); 1967(23); 1968(24-26); 1969(27); 1970(28-29); 1971(30-31); 1972(32); 1973(33); 1974(34-35); 1975(36-37); 1976(38-41); 1977(42); 1978(43-44); 1979(45-46); 1980(47);
Embrapa Meio-Norte
1961 (4); 1964 (12); 1965 (14-17); 1966 (18-21); 1967 (23); 1968/78 (25-44); 1979 (45)
Classificação: 632.05
Embrapa Pantanal
1971-80 (30,33,38-40,42-47)
Classificação: 23A
Embrapa Rondônia
1967 (23); 1969-71 (27-30); 1973-74 33-35; 1976 (39); 1978 (43-44); 1979-80 (45-47);
Classificação: 632.05
Embrapa Semiárido
1960 (2); 1961 (1,3); 1962 (7-8); 1965 (14-16); 1966 (20); 1967 (23); 1968 (24-26); 1969 (27); 1970 (28-29); 1971 (30-31); 1972 (32); 1973 (33); 1974 (34-35); 1975 (36-37); 1976 (39-41); 1978 (43-44); 1979 (45-46); 1980 (47);
Embrapa Soja
1965 (17); 1966(20); 1970 (28-29); 1971 (30); 1972 (32); 1973 (33); 1974 (34-35); 1975 (36-37); 1976 (38-41); 1977 (42); 1978(43-44); 1979 (46); 1980 (47)
Classificação: 632.05
Embrapa Trigo
1960/80 (1-2) 1960; (3-4) 1961; (5-8) 1962; (9-10) 1963; (11-13) 1964; (15-16) 1965; (18-22) 1966; (23) 1967; (24-26) 1968; (27) 1969; (28-29) 1970; (30-31) 1971; (32) 1972; (33) 1973; (34-35) 1974; (36-37) 1975; (38-41) 1976; (42) 1977; (43-44) 1978; (45-46) 1979; (47) 1980.
Classificação: 632.05
Embrapa Uva e Vinho
1961 (1); 1962 (8); 1963 (10); 1964 (11-13); 1965 (14-17); 1966 (18-22); 1967 (23); 1968 (24-26); 1969 (27); 1970 (28-29); 1971 (30-31); 1972 (32); 1973 (33); 1974 (34); 1975 (35-37); 1976 (38-41); 1977 (42); 1978 (44); 1979 (45-46); 1980 (47)
Classificação: 632.05 |
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