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| Registros recuperados : 17 | |
| 4. |  | ROMERO, D.; BROM, S.; MARTINEZ SALAZAR, J.; GIRARD, M. DE L.; PALACIOS, R.; DAVILA, G. Amplification and deletion of a nod-nif region in the symbiotic plasmid of Rhizobium phaseoli. J. Bacteriol., v.173, n.8, p.2435-2441, 1991.| Biblioteca(s): Embrapa Agrobiologia. |
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| 5. | | GIRARD, M. DE L.; FLORES, M.; BROM, S.; ROMERO, D.; PALACIOS, R.; DAVILA, G. Structural complexity of the symbiotic plasmid of Rhizobium leguminosarum bv. phaseoli. J. Bacteriol., v.173, n.8, p.2411-2419, 1991.| Biblioteca(s): Embrapa Agrobiologia. |
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| 6. | | FLORES, M.; BROM, S.; STEPKOWSKI, T.; GIRARD, M. DE L.; DAVILA, G.; ROMERO, D.; PALACIOS, R. Gene amplification in Rhizobium: identification and in vivo cloning of discrete amplifiable DNA regions (amplicons) from Rhizobium leguminosarum biovar phaseoli. Proc. Natl. Acad. Sci., v.90, p.4932-4936, 1993.| Biblioteca(s): Embrapa Agrobiologia. |
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| 7. | | ROMERO, D.; SINGLETON, P. W.; SEGOVIA, L.; MORETT, E.; BOHLOOL, B. B.; PALACIOS, R.; DAVILA, G. Effect of naturally occurring nif reiterations on symbiotic effectiveness in Rhizobium phaseoli. Appl. Environ. Microbiol., v. 54, n. 3, p. 848-850, 1988.| Biblioteca(s): Embrapa Agrobiologia. |
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| 9. | | FLORES, M.; GONZALEZ, V.; BROM, S.; MARTINEZ, E.; PINERO, D.; ROMERO, D.; DAVILA, G.; PALACIOS, R. Reiterated DNA sequences in Rhizobium and Agrobacterium spp. J. Bacteriol., v.169, n.12, p.5782-5788, 1987.| Biblioteca(s): Embrapa Agrobiologia. |
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| 10. | | MARTINEZ, E.; FLORES, M.; BROM, S.; ROMERO, D.; DAVILA, G.; PALACIOS, R. Rhizobium phaseoli: A molecular genetics view. Plant Soil, v. 108, n. 1, p. 179-184, 1988.| Biblioteca(s): Embrapa Agrobiologia. |
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| 11. | | FLORES, M.; GONZALEZ, V.; PARDO, M. A.; LEIJA, A.; MARTINEZ, E.; ROMERO, D.; PINERO, D.; DAVILA, G.; PALACIOS, R. Genomic instability in Rhizobium phaseoli. J. Bacteriol., v.170, n.3, p.1191-1196, 1988.| Biblioteca(s): Embrapa Agrobiologia. |
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| 12. | | BROM, S.; LOS SANTOS, A. G. DE; GIRARD, M. DE L.; DAVILA, G.; PALACIOS, R.; ROMERO, D. High-frequency rearrangements in Rhizobium leguminosarum bv. phaseoli plasmids. J. Bacteriol., v.173, n.3, p.1344-1346, 1991.| Biblioteca(s): Embrapa Agrobiologia. |
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| 13. | | BROM, S.; SANTOS, A. G. DE LOS; STEPKOWSKY, T.; FLORES, M.; DAVILA, G.; ROMERO, D.; PALACIOS, R. Different plasmids of Rhizobium leguminosarum bv. phaseoli are required for optimal symbiotic performance. J. Bacteriol., v.174, n.16, p.5183-5189, 1992.| Biblioteca(s): Embrapa Agrobiologia. |
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| 14. | | MORA, J.; DAVILA, G.; ESPIN, G.; GONZALEZ, A.; GUZMAN, J.; HERNANDEZ, G.; HUMMELT, G.; LARA, M.; MARTINEZ, E.; MORA.; ROMERO, D. Glutamine metabolism in Neurospora crassa. In: Glutamine: Metabolism, Enzymology and Regulation., v., p.185-212, 1980.| Biblioteca(s): Embrapa Agrobiologia. |
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| 15. | | PNCE-MENDOZA, A.; ROMERO, D.; ASTUDILLO, M.; LÓPEZ, A.; CARRILLO, Y.; TORRES, C.; RODRÍGUEZ, I.; ROGRÍGUEZ, M.; JARQUIN, A.; HUERTA, E. Abundance of macrofauna in perturbate and not perturbate areas in a tropical forest of tabasco, Mexico. 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.| Biblioteca(s): Embrapa Florestas. |
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| 16. | | ROMERO, D. J.; BEN-DOR, E.; DEMATTÊ, J. A. M.; SOUZA, A. B. e; VICENTE, L. E.; TAVARES, T. R.; MARTELLO, M.; STRABELI, T. F.; BARROS, P. P. da S.; FIORIO, P. R.; GALLO, B. C.; SATO, M. V.; EITELWEIN, M. T. Internal soil standard method for the Brazilian soil spectral library: performance and proximate analysis. Geoderma, v. 312, p. 95-103, 2018.| Biblioteca(s): Embrapa Meio Ambiente. |
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| 17. | | ZUFFA, S.; SCHMID, R.; BAUERMEISTER, A.; GOMES, P. W. P.; CARABALLO-RODRIGUEZ, A. M.; EL ABIEAD, Y.; ARON, A. T.; GENTRY, E. C.; ZEMLIN, J.; MEEHAN, M. J.; AVALON, N. E.; CICHEWICZ, R. H.; BUZUN, E.; CARRILLO TERRAZAS, M.; HSU, C. Y.; OLES, R.; AYALA, A. V.; ZHAO, J.; CHU, H.; KUIJPERS, M. C. M.; JACKREL, S. L.; TUGIZIMANA, F.; NEPHALI, L. P.; DUBERY, I. A.; MADALA, N. E.; MOREIRA, E. A.; COSTA-LOTUFO, L. V.; LOPES, N. P.; REZENDE-TEIXEIRA, P.; JIMENEZ, P. C.; RIMAL, B.; PATTERSON, A. D.; TRAXLER, M. F.; PESSOTTI, R. de C.; ALVARADO-VILLALOBOS, D.; TAMAYO-CASTILLO, G.; CHAVERRI, P.; ESCUDERO-LEYVA, E.; QUIROS-GUERRERO, L. M.; BORY, A. J.; JOUBERT, J.; RUTZ, A.; WOLFENDER, J. L.; ALLARD, P. M.; SICHERT, A.; PONTRELLI, S.; PULLMAN, B. S.; BANDEIRA, N.; GERWICK, W. H.; GINDRO, K.; MASSANA-CODINA, J.; WAGNER, B. C.; FORCHHAMMER, K.; PETRAS, D.; AIOSA, N.; GARG, N.; LIEBEKE, M.; BOURCEAU, P.; KANG, K. B.; GADHAVI, H.; CARVALHO, L. P. S. de; SANTOS, M. S. dos; PÉREZ-LORENTE, A. I.; MOLINA-SANTIAGO, C.; ROMERO, D.; FRANKE, R.; BRÖNSTRUP, M.; PONCE DE LEÓN, A. V.; POPE, P. B.; LA ROSA, S. L.; LA BARBERA, G.; ROAGER, H. M.; LAURSEN, M. F.; HAMMERLE, F.; SIEWERT, B.; PEINTNER, U.; LICONA-CASSANI, C.; RODRIGUEZ-ORDUÑA, L.; RAMPLER, E.; HILDEBRAND, F.; KOELLENSPERGER, G.; SCHOENY, H.; HOHENWALLNER, K.; PANZENBOECK, L.; GREGOR, R.; O'NEILL, E. C.; ROXBOROUGH, E. T.; ODOI, J.; BALE, N. J.; DING, S.; DAMSTÉ, J. S. S.; GUAN, X. L.; CUI, J. J.; JU, K. S.; SILVA, D. B.; SILVA, F. M. R.; SILVA, G. F. da; KOOLEN, H. H. F.; GRUNDMANN, C.; CLEMENT, J. A.; MOHIMANI, H.; BRODERS, K.; McPHAIL, K. L.; OBER-SINGLETON, S. E.; RATH, C. M.; McDONALD, D.; KNIGHT, R.; WANG, M.; DORRESTEIN, P. C. MicrobeMASST: a taxonomically informed mass spectrometry search tool for microbial metabolomics data. Nature Microbiology, v. 9, p. 336-345, Feb. 2024.| Biblioteca(s): Embrapa Amazônia Ocidental. |
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| Registros recuperados : 17 | |
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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. |
Registro Completo
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Biblioteca(s): |
Embrapa Florestas. |
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Data corrente: |
16/09/2008 |
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Data da última atualização: |
16/09/2008 |
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Autoria: |
PNCE-MENDOZA, A.; ROMERO, D.; ASTUDILLO, M.; LÓPEZ, A.; CARRILLO, Y.; TORRES, C.; RODRÍGUEZ, I.; ROGRÍGUEZ, M.; JARQUIN, A.; HUERTA, E. |
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Título: |
Abundance of macrofauna in perturbate and not perturbate areas in a tropical forest of tabasco, Mexico. |
|
Ano de publicação: |
2008 |
|
Fonte/Imprenta: |
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. |
|
Idioma: |
Inglês |
|
Conteúdo: |
Land use change in tropical regions has been characterized from forest to agriculture land or
grasslands. After this, the modified environment reduce theirs nutrients and then it is abandoned
by the farmers, like a bush old area (Acahual). The Acahual can be an important recovering area
for the future of the Forest dynamic. Comparisons between natural Forest habitats and disturbed
systems help us to gain insight into mechanisms leading to diversity changes by studying the
changes in habitat characteristics. The objective of this study was to know the effect of land use
change in macrofauna of soil (>2mm). We hypothesis that total macrofauna and every taxa
groups (Blattodea, Coleoptera, Diptera, Oligochaeta, Diplura, Hemiptera, Isoptera, Aranea,
Diplopoda, Hymenoptera, Isopoda, Miriapoda) will decrease in this order: Forest > Acahual >
Agriculture land > Grassland. The study area was in the mountain regions of Tabasco state in
Mexico (17° 30?N - 18° 30?N and 91° 00?W - 94° 00?W). Three different sites were selected with
two replicate each one: Forest-Agriculture (F-A), Forest-Grassland (F-G) and Forest-Acahual
(F-A). Three transect of 75m long with nine monoliths (four monoliths in the Forest, one in the
border and four in the modified ecosystem) were installed; the size of monolith was of 25 x 25 x
30 cm (TSBF, Anderson and Ingram, 1993) with a total of 54 monoliths per site. The soil
macrofauna of soil were divided in two layer: first layer from 0-10 cm and second from 10-30
cm. The abundance of macrofauna of soil in Forest was 1.3 times larger than the sum of the
modified environments. The first layer was significant higher in Forest (26.5 ± 3.6 individuals m-
2), Acahual (30.9 ± 7 individuals m-2) and Grassland (9.6 ± 2.1 individuals m-2) than the second
layer. Forest (20.0 ± 2.22 individuals m-2) and Acahual (23.3 ± 4.17 individuals m-2) were
significant larger than Grassland (7.7 ± 1.4 individuals m-2) and Agriculture land (9.9 ± 1.5
individuals m-2). The Acahual was larger (e.g. Coleoptera, Hemiptera, Aranea and Diplopoda)
than Forest and not significant differences (Blattodea, Oligochaeta, Isoptera, Hymenoptera and
Myriapoda) with the Forest. Therefore, the Acahual has an important function to restore the
original abundance of fauna. MenosLand use change in tropical regions has been characterized from forest to agriculture land or
grasslands. After this, the modified environment reduce theirs nutrients and then it is abandoned
by the farmers, like a bush old area (Acahual). The Acahual can be an important recovering area
for the future of the Forest dynamic. Comparisons between natural Forest habitats and disturbed
systems help us to gain insight into mechanisms leading to diversity changes by studying the
changes in habitat characteristics. The objective of this study was to know the effect of land use
change in macrofauna of soil (>2mm). We hypothesis that total macrofauna and every taxa
groups (Blattodea, Coleoptera, Diptera, Oligochaeta, Diplura, Hemiptera, Isoptera, Aranea,
Diplopoda, Hymenoptera, Isopoda, Miriapoda) will decrease in this order: Forest > Acahual >
Agriculture land > Grassland. The study area was in the mountain regions of Tabasco state in
Mexico (17° 30?N - 18° 30?N and 91° 00?W - 94° 00?W). Three different sites were selected with
two replicate each one: Forest-Agriculture (F-A), Forest-Grassland (F-G) and Forest-Acahual
(F-A). Three transect of 75m long with nine monoliths (four monoliths in the Forest, one in the
border and four in the modified ecosystem) were installed; the size of monolith was of 25 x 25 x
30 cm (TSBF, Anderson and Ingram, 1993) with a total of 54 monoliths per site. The soil
macrofauna of soil were divided in two layer: first layer from 0-10 cm and second from 10-3... Mostrar Tudo |
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LEADER 03202naa a2200229 a 4500
001 1314828
005 2008-09-16
008 2008 bl uuuu u00u1 u #d
100 1 $aPNCE-MENDOZA, A.
245 $aAbundance of macrofauna in perturbate and not perturbate areas in a tropical forest of tabasco, Mexico.
260 $c2008
520 $aLand use change in tropical regions has been characterized from forest to agriculture land or grasslands. After this, the modified environment reduce theirs nutrients and then it is abandoned by the farmers, like a bush old area (Acahual). The Acahual can be an important recovering area for the future of the Forest dynamic. Comparisons between natural Forest habitats and disturbed systems help us to gain insight into mechanisms leading to diversity changes by studying the changes in habitat characteristics. The objective of this study was to know the effect of land use change in macrofauna of soil (>2mm). We hypothesis that total macrofauna and every taxa groups (Blattodea, Coleoptera, Diptera, Oligochaeta, Diplura, Hemiptera, Isoptera, Aranea, Diplopoda, Hymenoptera, Isopoda, Miriapoda) will decrease in this order: Forest > Acahual > Agriculture land > Grassland. The study area was in the mountain regions of Tabasco state in Mexico (17° 30?N - 18° 30?N and 91° 00?W - 94° 00?W). Three different sites were selected with two replicate each one: Forest-Agriculture (F-A), Forest-Grassland (F-G) and Forest-Acahual (F-A). Three transect of 75m long with nine monoliths (four monoliths in the Forest, one in the border and four in the modified ecosystem) were installed; the size of monolith was of 25 x 25 x 30 cm (TSBF, Anderson and Ingram, 1993) with a total of 54 monoliths per site. The soil macrofauna of soil were divided in two layer: first layer from 0-10 cm and second from 10-30 cm. The abundance of macrofauna of soil in Forest was 1.3 times larger than the sum of the modified environments. The first layer was significant higher in Forest (26.5 ± 3.6 individuals m- 2), Acahual (30.9 ± 7 individuals m-2) and Grassland (9.6 ± 2.1 individuals m-2) than the second layer. Forest (20.0 ± 2.22 individuals m-2) and Acahual (23.3 ± 4.17 individuals m-2) were significant larger than Grassland (7.7 ± 1.4 individuals m-2) and Agriculture land (9.9 ± 1.5 individuals m-2). The Acahual was larger (e.g. Coleoptera, Hemiptera, Aranea and Diplopoda) than Forest and not significant differences (Blattodea, Oligochaeta, Isoptera, Hymenoptera and Myriapoda) with the Forest. Therefore, the Acahual has an important function to restore the original abundance of fauna.
700 1 $aROMERO, D.
700 1 $aASTUDILLO, M.
700 1 $aLÓPEZ, A.
700 1 $aCARRILLO, Y.
700 1 $aTORRES, C.
700 1 $aRODRÍGUEZ, I.
700 1 $aROGRÍGUEZ, M.
700 1 $aJARQUIN, A.
700 1 $aHUERTA, E.
773 $tIn: 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.
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