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Registro Completo |
Biblioteca(s): |
Embrapa Florestas. |
Data corrente: |
31/03/2023 |
Data da última atualização: |
17/08/2023 |
Tipo da produção científica: |
Artigo em Periódico Indexado |
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. |
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. |
Título: |
Earthworm communities in long-term no-tillage systems and secondary forest fragments in Paraná, Southern Brazil. |
Ano de publicação: |
2023 |
Fonte/Imprenta: |
Zootaxa, v. 5255, n. 1, p. 347-361, 2023. |
DOI: |
https://doi.org/10.11646/zootaxa.5255.1.28 |
Idioma: |
Inglês |
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 |
Palavras-Chave: |
Conservation agriculture; Ecosystem engineer; Soil macrofauna. |
Thesagro: |
Conservação do Solo; Ecossistema; Fertilidade do Solo; Minhoca. |
Thesaurus Nal: |
Earthworms; Oligochaeta. |
Categoria do assunto: |
P Recursos Naturais, Ciências Ambientais e da Terra |
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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Registro Completo
Biblioteca(s): |
Embrapa Agrobiologia. |
Data corrente: |
13/05/2010 |
Data da última atualização: |
02/02/2015 |
Tipo da produção científica: |
Artigo em Periódico Indexado |
Circulação/Nível: |
A - 1 |
Autoria: |
CHAER, G. M.; FERNANDES, M.; MYROLD, D.; BOTTOMLEY, P. |
Afiliação: |
GUILHERME MONTANDON CHAER, CNPAB; MARCELO FERNANDES DE OLIVEIRA, CNPSo; David Myrold, Oregon State University; Peter Bottomley, Oregon State University. |
Título: |
Comparative resistance and resilience of soil microbial communities and enzyme activities in adjacent native forest and agricultural soils. |
Ano de publicação: |
2009 |
Fonte/Imprenta: |
Microbial Ecology (2009) 58:414-424. |
Idioma: |
Português |
Palavras-Chave: |
Agrofloresta; Biologia de solo; Fauna do solo. |
Categoria do assunto: |
-- |
URL: |
https://download.springer.com/static/pdf/756/art%253A10.1007%252Fs00248-009-9508-x.pdf?auth66=1422896958_22ce43286f56a6c7fd93180dc42486a5&ext=.pdf
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Marc: |
LEADER 00560naa a2200181 a 4500 001 1783652 005 2015-02-02 008 2009 bl --- 0-- u #d 100 1 $aCHAER, G. M. 245 $aComparative resistance and resilience of soil microbial communities and enzyme activities in adjacent native forest and agricultural soils. 260 $c2009 653 $aAgrofloresta 653 $aBiologia de solo 653 $aFauna do solo 700 1 $aFERNANDES, M. 700 1 $aMYROLD, D. 700 1 $aBOTTOMLEY, P. 773 $tMicrobial Ecology (2009) 58:414-424.
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Registro original: |
Embrapa Agrobiologia (CNPAB) |
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Registro completo
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 |
Identificador: |
2826 |
Data corrente: |
09/05/2002 |
Data da última atualização: |
09/05/2002 |
Código do título: |
0900592 |
ISSN: |
0100-6967 |
Código CCN: |
027582-4 |
Título e Subtítulo: |
DIVULGACAO AGRONOMICA |
Entidade: |
Shell Quimica S.A. |
Local de publicação: |
Sao Paulo-SP |
Periodicidade: |
irregular |
Inicio de publicação: |
1959 |
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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