49 results on '"Piedade, M. T."'
Search Results
2. Very High Productivity of the C₄ Aquatic Grass Echinochloa polystachya in the Amazon Floodplain Confirmed by Net Ecosystem CO₂ Flux Measurements
- Author
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Morison, J. I. L., Piedade, M. T. F., Müller, E., Long, S. P., Junk, W. J., and Jones, M. B.
- Published
- 2000
3. Nutrient Dynamics of the Highly Productive C4 Macrophyte Echinochloa polystachya on the Amazon Floodplain
- Author
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Piedade, M. T. F., Junk, W. J., and Long, S. P.
- Published
- 1997
4. Natural history of the hyperdominant tree, Pentaclethra macroloba (Willd.) Kuntze, in the Amazon River estuary.
- Author
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Dantas, A. R., Vasconcelos, C. C., Guedes, M. C., Lira-Guedes, A. C., and Piedade, M. T. F.
- Subjects
NATURAL history ,RAINFALL ,SEED size ,FLOWERING trees ,PLANT colonization - Abstract
Copyright of Brazilian Journal of Biology is the property of Instituto Internacional de Ecologia and its content may not be copied or emailed to multiple sites or posted to a listserv without the copyright holder's express written permission. However, users may print, download, or email articles for individual use. This abstract may be abridged. No warranty is given about the accuracy of the copy. Users should refer to the original published version of the material for the full abstract. (Copyright applies to all Abstracts.)
- Published
- 2024
- Full Text
- View/download PDF
5. Growth models based on tree-ring data for the Neotropical tree species Calophyllum brasiliense across different Brazilian wetlands: implications for conservation and management
- Author
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Rosa, Sejana Artiaga, Barbosa, A. C. M. C., Junk, W. J., da Cunha, C. Nunes, Piedade, M. T. F., Scabin, A. B., Ceccantini, G. C. T., and Schöngart, J.
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- 2017
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6. Co-limitation towards lower latitudes shapes global forest diversity gradients
- Author
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Liang, J., Gamarra, J. G. P., Picard, N., Zhou, M., Pijanowski, B., Jacobs, D. F., Reich, P. B., Crowther, T. W., Nabuurs, G. -J., de-Miguel, S., Fang, J., Pfautsch, S., Phillips, O. L., Piedade, M. T. F., Piotto, D., Pollastrini, M., Poorter, L., Poulsen, J. R., Poulsen, A. D., Pretzsch, H., Keppel, G., Gonzalez-Elizondo, M. S., Rodeghiero, M., Rolim, S. G., Rovero, F., Rutishauser, E., Sagheb-Talebi, K., Saikia, P., Sainge, M. N., Salas-Eljatib, C., Salis, A., Schall, P., Gorenstein, L., Hengeveld, G. M., Schepaschenko, D., Scherer-Lorenzen, M., Schmid, B., Schöngart, J., Šebeň, V., Sellan, G., Selvi, F., Serra-Diaz, J. M., Sheil, D., Habonayo, R., Shvidenko, A. Z., Ibisch, P. L., Sist, P., Souza, A. F., Stereńczak, K. J., Sullivan, M. J. P., Sundarapandian, S., Svoboda, M., Swaine, M. D., Targhetta, N., Hardy, O. J., Tchebakova, N., Trethowan, L. A., Silva, C. A., Tropek, R., Mukendi, J. T., Umunay, P. M., Usoltsev, V. A., Vaglio, Laurin, G., Valentini, R., Valladares, F., Harris, D. J., van, der, Plas, F., Vega-Nieva, D. J., Verbeeck, H., ter, Steege, H., Viana, H., Vibrans, A. C., Vieira, S. A., Vleminckx, J., Waite, C. E., Wang, H. -F., Hector, A., Wasingya, E. K., Wekesa, C., Westerlund, B., Wittmann, F., Peri, P. L., Wortel, V., Zawiła-Niedźwiecki, T., Zhang, C., Zhao, X., Zhu, J., Hemp, A., Zhu, X., Zhu, Z. -X., Zo-Bi, I. C., Hui, C., Coomes, D. A., Searle, E. B., von, Gadow, K., Jaroszewicz, B., Abbasi, A. O., Abegg, M., Herold, M., Yao, Y. C. A., Aguirre-Gutiérrez, J., Zambrano, A. M. A., Altman, J., Alvarez-Dávila, E., Álvarez-González, J. G., Alves, L. F., Amani, B. H. K., Amani, C. A., Ammer, C., Hillers, A., Ilondea, B. A., Antón-Fernández, C., Avitabile, V., Aymard, G. A., Azihou, A. F., Baard, J. A., Baker, T. R., Balazy, R., Bastian, M. L., Batumike, R., Hubau, W., Bauters, M., Beeckman, H., Benu, N. M. H., Bitariho, R., Boeckx, P., Bogaert, J., Bongers, F., Bouriaud, O., Brancalion, P. H. S., Brandl, S., Woodall, C. W., Brearley, F. Q., Briseno-Reyes, J., Broadbent, E. N., Bruelheide, H., Bulte, E., Catlin, A. C., Cazzolla, Gatti, R., César, R. G., Chen, H. Y. H., Chisholm, C., Ibanez, T., Cienciala, E., Colletta, G. D., Corral-Rivas, J. J., Cuchietti, A., Cuni-Sanchez, A., Dar, J. A., Dayanandan, S., de, Haulleville, T., Decuyper, M., Delabye, S., Imai, N., Derroire, G., DeVries, B., Diisi, J., Do, T. V., Dolezal, J., Dourdain, A., Durrheim, G. P., Obiang, N. L. E., Ewango, C. E. N., Eyre, T. J., Imani, G., Fayle, T. M., Feunang, L. F. N., Finér, L., Fischer, M., Fridman, J., Frizzera, L., de, Gasper, A. L., Gianelle, D., Glick, H. B., Jagodzinski, A. M., Janecek, S., Johannsen, V. K., Joly, C. A., Jumbam, B., Kabelong, B. L. P. R., Kahsay, G. A., Svenning, J. -C., Karminov, V., Kartawinata, K., Kassi, J. N., Kearsley, E., Kennard, D. K., Kepfer-Rojas, S., Khan, M. L., Kigomo, J. N., Kim, H. S., Klauberg, C., Jucker, T., Klomberg, Y., Korjus, H., Kothandaraman, S., Kraxner, F., Kumar, A., Kuswandi, R., Lang, M., Lawes, M. J., Leite, R. V., Lentner, G., Bastin, J. -F., Lewis, S. L., Libalah, M. B., Lisingo, J., López-Serrano, P. M., Lu, H., Lukina, N. V., Lykke, A. M., Maicher, V., Maitner, B. S., Marcon, E., Wiser, S. K., Marshall, A. R., Martin, E. H., Martynenko, O., Mbayu, F. M., Mbuvi, M. T. E., Meave, J. A., Merow, C., Miscicki, S., Moreno, V. S., Morera, A., Slik, F., Mukul, S. A., Müller, J. C., Murdjoko, A., Nava-Miranda, M. G., Ndive, L. E., Neldner, V. J., Nevenic, R. V., Nforbelie, L. N., Ngoh, M. L., N’Guessan, A. E., Hérault, B., Ngugi, M. R., Ngute, A. S. K., Njila, E. N. N., Nyako, M. C., Ochuodho, T. O., Oleksyn, J., Paquette, A., Parfenova, E. I., Park, M., Parren, M., Alberti, G., Parthasarathy, N., Liang, J., Gamarra, J. G. P., Picard, N., Zhou, M., Pijanowski, B., Jacobs, D. F., Reich, P. B., Crowther, T. W., Nabuurs, G. -J., de-Miguel, S., Fang, J., Pfautsch, S., Phillips, O. L., Piedade, M. T. F., Piotto, D., Pollastrini, M., Poorter, L., Poulsen, J. R., Poulsen, A. D., Pretzsch, H., Keppel, G., Gonzalez-Elizondo, M. S., Rodeghiero, M., Rolim, S. G., Rovero, F., Rutishauser, E., Sagheb-Talebi, K., Saikia, P., Sainge, M. N., Salas-Eljatib, C., Salis, A., Schall, P., Gorenstein, L., Hengeveld, G. M., Schepaschenko, D., Scherer-Lorenzen, M., Schmid, B., Schöngart, J., Šebeň, V., Sellan, G., Selvi, F., Serra-Diaz, J. M., Sheil, D., Habonayo, R., Shvidenko, A. Z., Ibisch, P. L., Sist, P., Souza, A. F., Stereńczak, K. J., Sullivan, M. J. P., Sundarapandian, S., Svoboda, M., Swaine, M. D., Targhetta, N., Hardy, O. J., Tchebakova, N., Trethowan, L. A., Silva, C. A., Tropek, R., Mukendi, J. T., Umunay, P. M., Usoltsev, V. A., Vaglio, Laurin, G., Valentini, R., Valladares, F., Harris, D. J., van, der, Plas, F., Vega-Nieva, D. J., Verbeeck, H., ter, Steege, H., Viana, H., Vibrans, A. C., Vieira, S. A., Vleminckx, J., Waite, C. E., Wang, H. -F., Hector, A., Wasingya, E. K., Wekesa, C., Westerlund, B., Wittmann, F., Peri, P. L., Wortel, V., Zawiła-Niedźwiecki, T., Zhang, C., Zhao, X., Zhu, J., Hemp, A., Zhu, X., Zhu, Z. -X., Zo-Bi, I. C., Hui, C., Coomes, D. A., Searle, E. B., von, Gadow, K., Jaroszewicz, B., Abbasi, A. O., Abegg, M., Herold, M., Yao, Y. C. A., Aguirre-Gutiérrez, J., Zambrano, A. M. A., Altman, J., Alvarez-Dávila, E., Álvarez-González, J. G., Alves, L. F., Amani, B. H. K., Amani, C. A., Ammer, C., Hillers, A., Ilondea, B. A., Antón-Fernández, C., Avitabile, V., Aymard, G. A., Azihou, A. F., Baard, J. A., Baker, T. R., Balazy, R., Bastian, M. L., Batumike, R., Hubau, W., Bauters, M., Beeckman, H., Benu, N. M. H., Bitariho, R., Boeckx, P., Bogaert, J., Bongers, F., Bouriaud, O., Brancalion, P. H. S., Brandl, S., Woodall, C. W., Brearley, F. Q., Briseno-Reyes, J., Broadbent, E. N., Bruelheide, H., Bulte, E., Catlin, A. C., Cazzolla, Gatti, R., César, R. G., Chen, H. Y. H., Chisholm, C., Ibanez, T., Cienciala, E., Colletta, G. D., Corral-Rivas, J. J., Cuchietti, A., Cuni-Sanchez, A., Dar, J. A., Dayanandan, S., de, Haulleville, T., Decuyper, M., Delabye, S., Imai, N., Derroire, G., DeVries, B., Diisi, J., Do, T. V., Dolezal, J., Dourdain, A., Durrheim, G. P., Obiang, N. L. E., Ewango, C. E. N., Eyre, T. J., Imani, G., Fayle, T. M., Feunang, L. F. N., Finér, L., Fischer, M., Fridman, J., Frizzera, L., de, Gasper, A. L., Gianelle, D., Glick, H. B., Jagodzinski, A. M., Janecek, S., Johannsen, V. K., Joly, C. A., Jumbam, B., Kabelong, B. L. P. R., Kahsay, G. A., Svenning, J. -C., Karminov, V., Kartawinata, K., Kassi, J. N., Kearsley, E., Kennard, D. K., Kepfer-Rojas, S., Khan, M. L., Kigomo, J. N., Kim, H. S., Klauberg, C., Jucker, T., Klomberg, Y., Korjus, H., Kothandaraman, S., Kraxner, F., Kumar, A., Kuswandi, R., Lang, M., Lawes, M. J., Leite, R. V., Lentner, G., Bastin, J. -F., Lewis, S. L., Libalah, M. B., Lisingo, J., López-Serrano, P. M., Lu, H., Lukina, N. V., Lykke, A. M., Maicher, V., Maitner, B. S., Marcon, E., Wiser, S. K., Marshall, A. R., Martin, E. H., Martynenko, O., Mbayu, F. M., Mbuvi, M. T. E., Meave, J. A., Merow, C., Miscicki, S., Moreno, V. S., Morera, A., Slik, F., Mukul, S. A., Müller, J. C., Murdjoko, A., Nava-Miranda, M. G., Ndive, L. E., Neldner, V. J., Nevenic, R. V., Nforbelie, L. N., Ngoh, M. L., N’Guessan, A. E., Hérault, B., Ngugi, M. R., Ngute, A. S. K., Njila, E. N. N., Nyako, M. C., Ochuodho, T. O., Oleksyn, J., Paquette, A., Parfenova, E. I., Park, M., Parren, M., Alberti, G., and Parthasarathy, N.
- Abstract
The latitudinal diversity gradient (LDG) is one of the most recognized global patterns of species richness exhibited across a wide range of taxa. Numerous hypotheses have been proposed in the past two centuries to explain LDG, but rigorous tests of the drivers of LDGs have been limited by a lack of high-quality global species richness data. Here we produce a high-resolution (0.025° × 0.025°) map of local tree species richness using a global forest inventory database with individual tree information and local biophysical characteristics from ~1.3 million sample plots. We then quantify drivers of local tree species richness patterns across latitudes. Generally, annual mean temperature was a dominant predictor of tree species richness, which is most consistent with the metabolic theory of biodiversity (MTB). However, MTB underestimated LDG in the tropics, where high species richness was also moderated by topographic, soil and anthropogenic factors operating at local scales. Given that local landscape variables operate synergistically with bioclimatic factors in shaping the global LDG pattern, we suggest that MTB be extended to account for co-limitation by subordinate drivers. © 2022, The Author(s), under exclusive licence to Springer Nature Limited.
- Published
- 2022
7. Seasonal shifts in isoprenoid emission composition from three hyperdominant tree species in central Amazonia
- Author
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Gomes Alves, E., primary, Taylor, T., additional, Robin, M., additional, Pinheiro Oliveira, D., additional, Schietti, J., additional, Duvoisin Júnior, S., additional, Zannoni, N., additional, Williams, J., additional, Hartmann, C., additional, Gonçalves, J. F. C., additional, Schöngart, J., additional, Wittmann, F., additional, and Piedade, M. T. F., additional
- Published
- 2022
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- View/download PDF
8. Leaf and Canopy Photosynthetic CO₂ Uptake of a Stand of Echinochloa polystachya on the Central Amazon Floodplain. Are the High Potential Rates Associated with the C₄ Syndrome Realized under the Near-Optimal Conditions Provided by This Exceptional Natural Habitat?
- Author
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Piedade, M. T. F., Long, S. P., and Junk, W. J.
- Published
- 1994
9. The Productivity of the C_4 Grass Echinochloa Polystachya on the Amazon Floodplain
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Piedade, M. T. F., Junk, W. J., and Long, S. P.
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- 1991
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10. Status of knowledge, ongoing research, and research needs in Amazonian wetlands
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Junk, W. J. and Piedade, M. T. F.
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- 2004
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11. River damming affects seedling communities of a floodplain forest in the Central Amazon
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Rocha, M. Da, Feitosa, Y. O., Wittmann, F., Piedade, M. T. F., Resende, A. F. De, and Assis, R. L. De
- Subjects
floodplain ,tropical rivers ,Geography & travel ,flood gradient ,seedlings ,hydrologic cycle ,dams ,ddc:910 ,environmental stress - Abstract
The flood pulse of black water rivers in the Amazon basin determines the composition of species along the flood gradient in igapó forests. The Balbina dam, built on the Uatumã River, has altered the flood pulse and caused changes in the floristic composition of adult trees throughout the downstream area. There is a lack of studies on how communities of seedlings in igapó forests respond to changes in the flood pulse. This study investigates the response of seedling communities in the igapó forest downstream the Balbina dam and compares it with two pristine areas. The areas were sampled with transects of 1x25 m within 36 plots (25x25 m) along the flood gradient. Richness and dominance were calculated by simple regression and ordination analyses. The pristine areas had the same pattern of richness, dominance and genera distribution along the flood gradient. However, the affected Uatumã area formed different groups of genera by NMDS analysis, which divided them along the flood gradient with significantly increased dominance of three genera. The insertion of the Balbina dam resulted a loss of lateral and longitudinal connectivity for the Uatumã River, and the alteration to seedling communities may alter the future landscape of downstream igapó forests.
- Published
- 2020
12. Population dynamics of Attalea excelsa (Arecaceae) in floodplain forest of the Amazonian Estuary
- Author
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DANTAS, A. R., LIRA-GUEDES, A. C., GUEDES, M. C., PIEDADE, M. T. F., BATISTA, A. P. B., ADELSON ROCHA DANTAS, INPA, ANA CLAUDIA LIRA GUEDES, CPAF-AP, MARCELINO CARNEIRO GUEDES, CPAF-AP, and MARIA TERESA FERNANDEZ PIEDADE, INPA.
- Subjects
Topography ,Ripley's K function ,Mortality ,Palm ,Urucum ,Aggregate distribution ,Flood gradient - Abstract
Attalea excelsa (urucurizeiro) is a dominant palm of the estuarine floodplains, with great potential for nontimber management. This study evaluated the population dynamics of urucurizeiro and the factors that contribute to colonising of this species in a flooded environment. Individuals with base height circumference ≥ 30 cm in 2011 and 2014 were measured in 55.95 ha of floodplain forest in southern Amapá, Brazil. The parameters of population dynamics (mortality, recruitment and growth) in high and low floodplain environments were determined. Ripley?s K function was used to analyse the spatial distribution. Population density in 2011 was 3.99 individual ha-1, and in 2014 the density increased to 4.09 individual ha-1. Mortality rate was zero and the recruitment rate was 1.05% year-1. Basal area in 2011 was 0.49 m² ha-1 and in 2014, it reached 0.72 m² ha-1. Diameter growth rate was 5.32 cm year-1. The population presented an aggregate distribution pattern. Structural differences in diameter (F = 9.15, p = 0.003) and basal area (F = 10.7, p = 0.001) were evident between high and low floodplain forests. The increase in diameter was higher in low floodplain (3.98 cm year-1) compared with high floodplain (1.35 cm year-1). The patterns shown by A. excelsa are reflections of its high adaptation to the daily flooded environment. Made available in DSpace on 2020-12-17T09:04:52Z (GMT). No. of bitstreams: 1 CPAF-AP-2020-Population-dynamics-of-attalea.pdf: 1237523 bytes, checksum: 79d7257d96958c2eaed0064dda9ddbc9 (MD5) Previous issue date: 2020
- Published
- 2020
13. Status of knowledge, ongoing research, and research needs in Amazonian wetlands
- Author
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Junk, W. J. and Piedade, M. T. F.
- Published
- 2005
14. Physicochemical features of Amazonian water typologies for water resources management
- Author
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Ríos-Villamizar, Eduardo A, primary, Adeney, J M, additional, Junk, W J, additional, and Piedade, M T F, additional
- Published
- 2020
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- View/download PDF
15. Climatic controls of decomposition drive the global biogeography of forest-tree symbioses
- Author
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Steidinger, B. S., Crowther, T. W., Liang, J., Van Nuland, M. E., Werner, G. D. A., Reich, P. B., Nabuurs, G., de-Miguel, S., Zhou, M., Picard, N., Herault, B., Karminov, V., Sist, P., Targhetta, N., Tchebakova, N., Steege, H., Johannsen, V., Iêda, A., Alvarez-Loayza, P., Thomas, R., Bastin, J. -F., Ibanez, T., Tikhonova, E., Umunay, P., Dayanandan, S., Imai, N., Derroire, G., Usoltsev, V. A., Valladares, F., van der Plas, F., Dourdain, A., Van Do, T., Abegg, M., Enquist, B., Vasquez Martinez, R., Verbeeck, H., Joly, C. A., Viana, H., Alves, L. F., Jagodzinski, A. M., Vieira, S., Ngugi, M., de Gasper, A. L., Keppel, G., Obiang, N. L. E., Neldner, V., von Gadow, K., Wang, H. -F., Watson, J., Westerlund, B., Wiser, S., Wittmann, F., Wortel, V., Khan, M. L., Kraxner, F., Jucker, T., Zagt, R., Birigazzi, L., Ortiz-Malavasi, E., Baker, T., Birnbaum, P., Bitariho, R., Kartawinata, K., Niklaus, P., Kennard, D., Laarmann, D., Boeckx, P., Bongers, F., Bouriaud, O., Kim, H. S., Silveira, M., Köhl, M., Brancalion, P. H. S., Brandl, S., Brearley, F. Q., Brienen, R., Lang, M., Broadbent, E., Bruelheide, H., Oleksyn, J., Bussotti, F., Searle, E., Nevenic, R., Kearsley, E., Schmid, B., Kitayama, K., Cazzolla Gatti, R., Zhang, C., Cesar, R., Cesljar, G., Chazdon, R., Chen, H. Y. H., Chisholm, C., Cienciala, E., Park, M., Ontikov, P., Clark, C. J., Eyre, T., Sonké, B., Clark, D., Sheil, D., DeVries, B., Fandohan, A. B., Fayle, T. M., Feldpausch, T. R., Seben, V., Parren, M., Kepfer-Rojas, S., Finér, L., Lewis, S., Fischer, M., Fletcher, C., Pan, Y., Almeyda Zambrano, A., Parada-Gutierrez, A., Fridman, J., Frizzera, L., Gamarra, J. G. P., Parthasarathy, N., Gianelle, D., Pfautsch, S., Glick, H. B., Harris, D., Serra-Diaz, J. M., Hector, A., Zhao, X., Schöngart, J., Hemp, A., Zhu, Z. -X., Paquette, A., Peri, P. L., Zawila-Niedzwiecki, T., Hengeveld, G., Herbohn, J., Herold, M., Hillers, A., Honorio, Coronado, E. N., Huber, M., Hui, C., Slik, F., Salas-Eljatib, C., Cho, H., Lu, H., Araujo-Murakami, A., Korjus, H., Lukina, N., Maitner, B., Shvidenko, A., Zo-Bi, I. C., Singh, J., Malhi, Y., Marcon, E., Marimon, B. S., Souza, A. F., Decuyper, M., Svenning, J. -C., Marimon-Junior, B. H., Marshall, A. R., Martin, E., Routh, D., Martynenko, O., Meave, J. A., Melo-Cruz, O., Coomes, D., Silva-Espejo, J., Ammer, C., Colletta, G., Stereńczak, K., Mendoza, C., Merow, C., Monteagudo Mendoza, A., Moreno, V., Mukul, S. A., Mundhenk, P., Nava-Miranda, M. G., Antón-Fernández, C., Bałazy, R., Peay, K. G., Phillips, O., Neill, D., Cumming, J., Parfenova, E., Piedade, M. T., Piotto, D., Adou Yao, C. Y., Cornejo Valverde, F., Alvarez-Davila, E., Banki, O., Pitman, N. C. A., Polo, I., Poorter, L., Arroyo, L., Kenfack, D., Aymard, G., Poulsen, A. D., Poulsen, J. R., Pretzsch, H., Ramirez Arevalo, F., Barroso, J., Restrepo-Correa, Z., Rodeghiero, M., Corral-Rivas, J. J., Rolim, S., Jaroszewicz, B., Condit, R., Alberti, G., Jung, I., Avitabile, V., Roopsind, A., Bastian, M., Rovero, F., Rutishauser, E., Saikia, P., Saner, P., Schall, P., Schelhaas, M. -J., Djordjevic, I., Crim, P., Schepaschenko, D., Svoboda, M., Killeen, T., Scherer-Lorenzen, M., Steidinger, B. S., Crowther, T. W., Liang, J., Van Nuland, M. E., Werner, G. D. A., Reich, P. B., Nabuurs, G., de-Miguel, S., Zhou, M., Picard, N., Herault, B., Karminov, V., Sist, P., Targhetta, N., Tchebakova, N., Steege, H., Johannsen, V., Iêda, A., Alvarez-Loayza, P., Thomas, R., Bastin, J. -F., Ibanez, T., Tikhonova, E., Umunay, P., Dayanandan, S., Imai, N., Derroire, G., Usoltsev, V. A., Valladares, F., van der Plas, F., Dourdain, A., Van Do, T., Abegg, M., Enquist, B., Vasquez Martinez, R., Verbeeck, H., Joly, C. A., Viana, H., Alves, L. F., Jagodzinski, A. M., Vieira, S., Ngugi, M., de Gasper, A. L., Keppel, G., Obiang, N. L. E., Neldner, V., von Gadow, K., Wang, H. -F., Watson, J., Westerlund, B., Wiser, S., Wittmann, F., Wortel, V., Khan, M. L., Kraxner, F., Jucker, T., Zagt, R., Birigazzi, L., Ortiz-Malavasi, E., Baker, T., Birnbaum, P., Bitariho, R., Kartawinata, K., Niklaus, P., Kennard, D., Laarmann, D., Boeckx, P., Bongers, F., Bouriaud, O., Kim, H. S., Silveira, M., Köhl, M., Brancalion, P. H. S., Brandl, S., Brearley, F. Q., Brienen, R., Lang, M., Broadbent, E., Bruelheide, H., Oleksyn, J., Bussotti, F., Searle, E., Nevenic, R., Kearsley, E., Schmid, B., Kitayama, K., Cazzolla Gatti, R., Zhang, C., Cesar, R., Cesljar, G., Chazdon, R., Chen, H. Y. H., Chisholm, C., Cienciala, E., Park, M., Ontikov, P., Clark, C. J., Eyre, T., Sonké, B., Clark, D., Sheil, D., DeVries, B., Fandohan, A. B., Fayle, T. M., Feldpausch, T. R., Seben, V., Parren, M., Kepfer-Rojas, S., Finér, L., Lewis, S., Fischer, M., Fletcher, C., Pan, Y., Almeyda Zambrano, A., Parada-Gutierrez, A., Fridman, J., Frizzera, L., Gamarra, J. G. P., Parthasarathy, N., Gianelle, D., Pfautsch, S., Glick, H. B., Harris, D., Serra-Diaz, J. M., Hector, A., Zhao, X., Schöngart, J., Hemp, A., Zhu, Z. -X., Paquette, A., Peri, P. L., Zawila-Niedzwiecki, T., Hengeveld, G., Herbohn, J., Herold, M., Hillers, A., Honorio, Coronado, E. N., Huber, M., Hui, C., Slik, F., Salas-Eljatib, C., Cho, H., Lu, H., Araujo-Murakami, A., Korjus, H., Lukina, N., Maitner, B., Shvidenko, A., Zo-Bi, I. C., Singh, J., Malhi, Y., Marcon, E., Marimon, B. S., Souza, A. F., Decuyper, M., Svenning, J. -C., Marimon-Junior, B. H., Marshall, A. R., Martin, E., Routh, D., Martynenko, O., Meave, J. A., Melo-Cruz, O., Coomes, D., Silva-Espejo, J., Ammer, C., Colletta, G., Stereńczak, K., Mendoza, C., Merow, C., Monteagudo Mendoza, A., Moreno, V., Mukul, S. A., Mundhenk, P., Nava-Miranda, M. G., Antón-Fernández, C., Bałazy, R., Peay, K. G., Phillips, O., Neill, D., Cumming, J., Parfenova, E., Piedade, M. T., Piotto, D., Adou Yao, C. Y., Cornejo Valverde, F., Alvarez-Davila, E., Banki, O., Pitman, N. C. A., Polo, I., Poorter, L., Arroyo, L., Kenfack, D., Aymard, G., Poulsen, A. D., Poulsen, J. R., Pretzsch, H., Ramirez Arevalo, F., Barroso, J., Restrepo-Correa, Z., Rodeghiero, M., Corral-Rivas, J. J., Rolim, S., Jaroszewicz, B., Condit, R., Alberti, G., Jung, I., Avitabile, V., Roopsind, A., Bastian, M., Rovero, F., Rutishauser, E., Saikia, P., Saner, P., Schall, P., Schelhaas, M. -J., Djordjevic, I., Crim, P., Schepaschenko, D., Svoboda, M., Killeen, T., and Scherer-Lorenzen, M.
- Abstract
The identity of the dominant root-associated microbial symbionts in a forest determines the ability of trees to access limiting nutrients from atmospheric or soil pools 1,2 , sequester carbon 3,4 and withstand the effects of climate change 5,6 . Characterizing the global distribution of these symbioses and identifying the factors that control this distribution are thus integral to understanding the present and future functioning of forest ecosystems. Here we generate a spatially explicit global map of the symbiotic status of forests, using a database of over 1.1 million forest inventory plots that collectively contain over 28,000 tree species. Our analyses indicate that climate variables—in particular, climatically controlled variation in the rate of decomposition—are the primary drivers of the global distribution of major symbioses. We estimate that ectomycorrhizal trees, which represent only 2% of all plant species 7 , constitute approximately 60% of tree stems on Earth. Ectomycorrhizal symbiosis dominates forests in which seasonally cold and dry climates inhibit decomposition, and is the predominant form of symbiosis at high latitudes and elevation. By contrast, arbuscular mycorrhizal trees dominate in aseasonal, warm tropical forests, and occur with ectomycorrhizal trees in temperate biomes in which seasonally warm-and-wet climates enhance decomposition. Continental transitions between forests dominated by ectomycorrhizal or arbuscular mycorrhizal trees occur relatively abruptly along climate-driven decomposition gradients; these transitions are probably caused by positive feedback effects between plants and microorganisms. Symbiotic nitrogen fixers—which are insensitive to climatic controls on decomposition (compared with mycorrhizal fungi)—are most abundant in arid biomes with alkaline soils and high maximum temperatures. The climatically driven global symbiosis gradient that we document provides a spatially explicit quantitative understanding of microbial sym, 33Smithsonian’s National Zoo and Conservation Biology Institute, Washington, DC, USA. 34Institute of Tropical Forest Conservation, Mbarara University of Sciences and Technology, Mbarara, Uganda. 35Isotope Bioscience Laboratory - ISOFYS, Ghent University, Ghent, Belgium. 36Integrated Center for Research, Development and Innovation in Advanced Materials, Nanotechnologies, and Distributed Systems for Fabrication and Control (MANSiD), Stefan cel Mare University of Suceava, Suceava, Romania. 37Department of Forest Sciences, Luiz de Queiroz College of Agriculture, University of São Paulo, Piracicaba, Brazil. 38Bavarian State Institute of Forestry, Freising, Germany. 39Manchester Metropolitan University, Manchester, UK. 40Institute of Biology, Geobotany and Botanical Garden, Martin Luther University Halle-Wittenberg, Halle-Wittenberg, Germany. 41German Centre for Integrative Biodiversity Research (iDiv) Halle-Jena-Leipzig, Leipzig, Germany. 42Department of Agriculture, Food, Environment and Forest (DAGRI), University of Firenze, Florence, Italy. 43Biological Institute, Tomsk State University, Tomsk, Russia. 44Department of Spatial Regulation, GIS and Forest Policy, Institute of Forestry, Belgrade, Serbia. 45Department of Ecology and Evolutionary Biology, University of Connecticut, Storrs, CT, USA. 46Tropical Forests and People Research Centre, University of the Sunshine Coast, Maroochydore, Queensland, Australia. 47Faculty of Natural Resources Management, Lakehead University, Thunder Bay, Ontario, Canada. 48Key Laboratory for Humid Subtropical Eco-Geographical Processes of the Ministry of Education, Fujian Normal University, Fuzhou, China. 49Institute of Integrative Biology, ETH Zürich, Zurich, Switzerland. 50IFER - Institute of Forest Ecosystem Research, Jilove u Prahy, Czech Republic. 51Global Change Research Institute CAS, Brno, Czech Republic. 52Nicholas School of the Environment, Duke University, Durham, NC, USA. 53Department of Biology, University of Missouri-St Loui
- Published
- 2019
16. Primary productivity of natural grass ecosystems of the tropics: A reappraisal
- Author
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Long, S. P., Garcia Moya, E., Imbamba, S. K., Kamnalrut, A., Piedade, M. T. F., Scurlock, J. M. O., Shen, Y. K., Hall, D. O., Clarholm, M., editor, and Bergström, L., editor
- Published
- 1989
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17. The effect of flooding on the exchange of the volatile C2-compounds ethanol, acetaldehyde and acetic acid between leaves of Amazonian floodplain tree species and the atmosphere
- Author
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Rottenberger, S., Kleiss, B., Kuhn, U., Wolf, A., Piedade, M. T. F., Junk, W., Kesselmeier, J., and EGU, Publication
- Subjects
lcsh:Geology ,lcsh:QH501-531 ,[PHYS.ASTR.CO] Physics [physics]/Astrophysics [astro-ph]/Cosmology and Extra-Galactic Astrophysics [astro-ph.CO] ,[SDU.OCEAN] Sciences of the Universe [physics]/Ocean, Atmosphere ,lcsh:QH540-549.5 ,lcsh:QE1-996.5 ,[SDU.STU] Sciences of the Universe [physics]/Earth Sciences ,lcsh:Life ,lcsh:Ecology ,[SDU.ASTR] Sciences of the Universe [physics]/Astrophysics [astro-ph] ,[SDU.ENVI] Sciences of the Universe [physics]/Continental interfaces, environment - Abstract
The effect of root inundation on the leaf emissions of ethanol, acetaldehyde and acetic acid in relation to assimilation and transpiration was investigated with 2–3 years old tree seedlings of four Amazonian floodplain species by applying dynamic cuvette systems under greenhouse conditions. Emissions were monitored over a period of several days of inundation using a combination of Proton Transfer Reaction Mass Spectrometry (PTR-MS) and conventional techniques (HPLC, ion chromatography). Under non-flooded conditions, none of the species exhibited measurable emissions of any of the compounds, but rather low deposition of acetaldehyde and acetic acid was observed instead. Tree species specific variations in deposition velocities were largely due to variations in stomatal conductance. Flooding of the roots resulted in leaf emissions of ethanol and acetaldehyde by all species, while emissions of acetic acid were only observed from the species exhibiting the highest ethanol and acetaldehyde emission rates. All three compounds showed a similar diurnal emission profile, each displaying an emission burst in the morning, followed by a decline in the evening. This concurrent behavior supports the conclusion, that all three compounds emitted by the leaves are derived from ethanol produced in the roots by alcoholic fermentation, transported to the leaves with the transpiration stream and finally partly converted to acetaldehyde and acetic acid by enzymatic processes. Co-emissions and peaking in the early morning suggest that root ethanol, after transportation with the transpiration stream to the leaves and enzymatic oxidation to acetaldehyde and acetate, is the metabolic precursor for all compounds emitted, though we can not totally exclude other production pathways. Emission rates substantially varied among tree species, with maxima differing by up to two orders of magnitude (25–1700 nmol m−2 min−1 for ethanol and 5–500 nmol m−2 min−1 for acetaldehyde). Acetic acid emissions reached 12 nmol m−2 min−1. The observed differences in emission rates between the tree species are discussed with respect to their root adaptive strategies to tolerate long term flooding, providing an indirect line of evidence that the root ethanol production is a major factor determining the foliar emissions. Species which develop morphological root structures allowing for enhanced root aeration produced less ethanol and showed much lower emissions compared to species which lack gas transporting systems, and respond to flooding with substantially enhanced fermentation rates and a non-trivial loss of carbon to the atmosphere. The pronounced differences in the relative emissions of ethanol to acetaldehyde and acetic acid between the tree species indicate that not only the ethanol production in the roots but also the metabolic conversion in the leaf is an important factor determining the release of these compounds to the atmosphere.
- Published
- 2008
18. Growth models based on tree-ring data for the Neotropical tree species Calophyllum brasiliense across different Brazilian wetlands: implications for conservation and management
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Rosa, Sejana Artiaga, primary, Barbosa, A. C. M. C., additional, Junk, W. J., additional, da Cunha, C. Nunes, additional, Piedade, M. T. F., additional, Scabin, A. B., additional, Ceccantini, G. C. T., additional, and Schöngart, J., additional
- Published
- 2016
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19. ESTRATÉGIAS DE DISPERSÃO, PRODUÇÃO DE FRUTOS E EXTRATIVISMO DA PALMEIRA Astrocaryum jauari MART. NOS IGAPÓS DO RIO NEGRO: IMPLICAÇÕES PARA A ICTIOFAUNA
- Author
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Piedade, M. T. F., primary, Parolin, P., additional, and Junk, W. J., additional
- Published
- 2016
- Full Text
- View/download PDF
20. Brazilian wetlands: their definition, delineation, and classification for research, sustainable management, and protection
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Junk, W. J., Piedade, M. T. F., Lourival, R., Wittmann, F., Kandus, P., Lacerda, Luiz Drude de, Bozelli, R. L., Esteves, F. A., Cunha, C. Nunes da, Maltchik, L., Schöngart, J., Schaeffer-Novelli, Y., and Agostinho, A. A.
- Subjects
Políticas - Zona úmida ,Vegetação - Zona úmida ,Wetland vegetation ,Wetland policy ,Amazônia - Zona úmida ,Amazonian Wetland - Abstract
Although 20% of Brazilian territory is covered by wetlands, wetland inventories are still incomplete. In 1993,Brazil signed the Ramsar Convention but a coherent national policy for the sustainable management andprotection of wetlands has yet to be established.2. Major gaps in the definition of a specific wetland policy are twofold: (1) the lack of standardized criteria bywhich wetlands are defined and delineated that reflects the specific ecological conditions of the country and (2)the lack of a national classification of wetlands that takes into account specific hydrological conditions andrespective plant communities.3. In recent years, efforts have been made at a regional level to improve public awareness of the ecology ofBrazilian wetlands, their benefits to society, and the major threats endangering them. Studies have shown thatwetlands play a crucial role in the regional hydrological cycle and provide multiple benefits for localpopulations. Furthermore, Brazilian wetlands contribute significantly to South American biodiversity.Therefore, wetland conservation and sustainable management should be given high legislative priority.4. This article provides a synthesis of the current body of knowledge on the distribution, hydrology, and vegetationcover of Brazilian wetlands. Their definition, delineation, and classification at the national level are proposed in orderto establish a scientific basis for discussions on a national wetland policy that mandates the sustainable management ofBrazil’s extremely diverse and complex wetlands. This goal is particularly urgent in the face of the continuing and ramatic deterioration of wetlands resulting from large-scale agro-industrial expansion, and hydroelectric projects aswell as the projected impact of global climate change on hydrological cycles.
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- 2014
21. Leaf level emissions of volatile organic compounds (VOC) from some Amazonian and Mediterranean plants
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Bracho-Nunez, A., Knothe, N. M., Welter, S., Staudt, M., Costa, W. R., Liberato, M. A. R., Piedade, M. T. F., and Kesselmeier, J.
- Subjects
lcsh:Geology ,lcsh:QH501-531 ,lcsh:QH540-549.5 ,lcsh:QE1-996.5 ,lcsh:Life ,lcsh:Ecology - Abstract
As volatile organic compounds (VOCs) significantly affect atmospheric chemistry (oxidative capacity) and physics (secondary organic aerosol formation and effects), emission inventories defining regional and global biogenic VOC emission strengths are important. The aim of this work was to achieve a description of VOC emissions from poorly described tropical vegetation to be compared with the quite well investigated and highly heterogeneous emissions from Mediterranean vegetation. For this task, common plant species of both ecosystems were investigated. Sixteen plant species from the Mediterranean area, which is known for its special diversity in VOC emitting plant species, were chosen. In contrast, little information is currently available regarding emissions of VOCs from tropical tree species at the leaf level. Twelve plant species from different environments of the Amazon basin, i.e. Terra firme, Várzea and Igapó, were screened for emission of VOCs at leaf level with a branch enclosure system. Analysis of the volatile organics was performed online by a proton-transfer-reaction mass spectrometer (PTR-MS) and offline by collection on adsorbent tubes and subsequent gas chromatographic analysis. Isoprene was quantitatively the most dominant compound emitted followed by monoterpenes, methanol and acetone. Most of the Mediterranean species emitted a variety of monoterpenes, whereas only five tropical species were monoterpene emitters exhibiting a quite conservative emission pattern (α-pinene > limonene > sabinene > β-pinene). Mediterranean plants showed additional emissions of sesquiterpenes, whereas in the case of plants from the Amazon region no sesquiterpenes were detected probably due to a lack of sensitivity in the measuring systems. On the other hand methanol emissions, an indicator of growth, were common in most of the tropical and Mediterranean species. A few species from both ecosystems showed acetone emissions. The observed heterogeneous emissions including reactive VOC species which are not easily detected by flux measurements, give reason to perform more screening at leaf level and, whenever possible, within the forests under ambient conditions.
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- 2012
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22. The Amazon Tall Tower Observatory (ATTO): overview of pilot measurements on ecosystem ecology, meteorology, trace gases, and aerosols
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Andreae, M. O., primary, Acevedo, O. C., additional, Araùjo, A., additional, Artaxo, P., additional, Barbosa, C. G. G., additional, Barbosa, H. M. J., additional, Brito, J., additional, Carbone, S., additional, Chi, X., additional, Cintra, B. B. L., additional, da Silva, N. F., additional, Dias, N. L., additional, Dias-Júnior, C. Q., additional, Ditas, F., additional, Ditz, R., additional, Godoi, A. F. L., additional, Godoi, R. H. M., additional, Heimann, M., additional, Hoffmann, T., additional, Kesselmeier, J., additional, Könemann, T., additional, Krüger, M. L., additional, Lavric, J. V., additional, Manzi, A. O., additional, Lopes, A. P., additional, Martins, D. L., additional, Mikhailov, E. F., additional, Moran-Zuloaga, D., additional, Nelson, B. W., additional, Nölscher, A. C., additional, Santos Nogueira, D., additional, Piedade, M. T. F., additional, Pöhlker, C., additional, Pöschl, U., additional, Quesada, C. A., additional, Rizzo, L. V., additional, Ro, C.-U., additional, Ruckteschler, N., additional, Sá, L. D. A., additional, de Oliveira Sá, M., additional, Sales, C. B., additional, dos Santos, R. M. N., additional, Saturno, J., additional, Schöngart, J., additional, Sörgel, M., additional, de Souza, C. M., additional, de Souza, R. A. F., additional, Su, H., additional, Targhetta, N., additional, Tóta, J., additional, Trebs, I., additional, Trumbore, S., additional, van Eijck, A., additional, Walter, D., additional, Wang, Z., additional, Weber, B., additional, Williams, J., additional, Winderlich, J., additional, Wittmann, F., additional, Wolff, S., additional, and Yáñez-Serrano, A. M., additional
- Published
- 2015
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23. The Amazon Tall Tower Observatory (ATTO) in the remote Amazon Basin: overview of first results from ecosystem ecology, meteorology, trace gas, and aerosol measurements
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Andreae, M. O., primary, Acevedo, O. C., additional, Araùjo, A., additional, Artaxo, P., additional, Barbosa, C. G. G., additional, Barbosa, H. M. J., additional, Brito, J., additional, Carbone, S., additional, Chi, X., additional, Cintra, B. B. L., additional, da Silva, N. F., additional, Dias, N. L., additional, Dias-Júnior, C. Q., additional, Ditas, F., additional, Ditz, R., additional, Godoi, A. F. L., additional, Godoi, R. H. M., additional, Heimann, M., additional, Hoffmann, T., additional, Kesselmeier, J., additional, Könemann, T., additional, Krüger, M. L., additional, Lavric, J. V., additional, Manzi, A. O., additional, Moran-Zuloaga, D., additional, Nölscher, A. C., additional, Santos Nogueira, D., additional, Piedade, M. T. F., additional, Pöhlker, C., additional, Pöschl, U., additional, Rizzo, L. V., additional, Ro, C.-U., additional, Ruckteschler, N., additional, Sá, L. D. A., additional, Sá, M. D. O., additional, Sales, C. B., additional, Santos, R. M. N. D., additional, Saturno, J., additional, Schöngart, J., additional, Sörgel, M., additional, de Souza, C. M., additional, de Souza, R. A. F., additional, Su, H., additional, Targhetta, N., additional, Tóta, J., additional, Trebs, I., additional, Trumbore, S., additional, van Eijck, A., additional, Walter, D., additional, Wang, Z., additional, Weber, B., additional, Williams, J., additional, Winderlich, J., additional, Wittmann, F., additional, Wolff, S., additional, and Yáñez-Serrano, A. M., additional
- Published
- 2015
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24. Structural Dynamics of Pristine Headwater Streams from Southern Brazilian Amazon
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Bleich, M. E., primary, Mortati, A. F., additional, André, T., additional, and Piedade, M. T. F., additional
- Published
- 2015
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- View/download PDF
25. Leaf level emissions of volatile organic compounds (VOC) from some Amazonian and Mediterranean plants
- Author
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Bracho-Nunez, A., primary, Knothe,, N. M., additional, Welter, S., additional, Staudt, M., additional, Costa, W. R., additional, Liberato, M. A. R., additional, Piedade, M. T. F., additional, and Kesselmeier, J., additional
- Published
- 2013
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26. Chemistry of different Amazonian water types for river classification: a preliminary review
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Ríos-Villamizar, E. A., primary, Piedade, M. T. F., additional, Da Costa, J. G., additional, Adeney, J. M., additional, and Junk, W. J., additional
- Published
- 2013
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27. Brazilian wetlands: their definition, delineation, and classification for research, sustainable management, and protection
- Author
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Junk, W. J., primary, Piedade, M. T. F., additional, Lourival, R., additional, Wittmann, F., additional, Kandus, P., additional, Lacerda, L. D., additional, Bozelli, R. L., additional, Esteves, F. A., additional, Nunes da Cunha, C., additional, Maltchik, L., additional, Schöngart, J., additional, Schaeffer-Novelli, Y., additional, and Agostinho, A. A., additional
- Published
- 2013
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28. Structural Dynamics of Pristine Headwater Streams from Southern Brazilian Amazon.
- Author
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Bleich, M. E., Mortati, A. F., André, T., and Piedade, M. T. F.
- Subjects
STRUCTURAL dynamics ,RIVERS ,GEOMORPHOLOGY ,HYDROLOGY ,DEFORESTATION ,RAINFALL - Abstract
Amazonian headwater streams trail a heterogeneous landscape, with marked natural variation of geomorphological conditions and hydrological periods. Southern Brazilian Amazon is subjected to high degradation pressure, mainly from deforestation. Hence, we characterize pristine headwaters structure (hydromorphology and water physical-chemical variables) and variation among hydrological periods (dry, beginning of the rainy period and end of the rainy period), to define reference conditions for conservation-oriented classification, monitoring and rehabilitation of the southern Brazilian Amazon streams. Stretches of 10 pristine streams from the Teles Pires River, a major tributary of the Tapajós River, were analysed for hydromorphology, water physical-chemical variables and controlled for habitat integrity (forested proportion on buffer zones and habitat integrity index). We found variation among hydrological periods and spatial heterogeneity on pristine stream structure. Most variables showed great variation ranges at the same hydrological period and high variation coefficient values, reflecting the natural environmental heterogeneity among streams protected by a riparian forest. Variation among hydrological periods and spatial heterogeneity between streams in this region, combined with current high levels of deforestation, indicates the need for the conservation of a high proportion of streams and their respective riparian forests. Here, we have presented reference range values for monitoring and rehabilitation programs integrated in the Amazonian aquatic conservation efforts. Copyright © 2015 John Wiley & Sons, Ltd. [ABSTRACT FROM AUTHOR]
- Published
- 2016
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29. Leaf level emissions of volatile organic compounds (VOC) from some Amazonian and Mediterranean plants
- Author
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Bracho-Nunez, A., primary, Knothe, N. M., additional, Welter, S., additional, Staudt, M., additional, Costa, W. R., additional, Liberato, M. A. R., additional, Piedade, M. T. F., additional, and Kesselmeier, J., additional
- Published
- 2012
- Full Text
- View/download PDF
30. The effect of flooding on the exchange of the volatile C<sub>2</sub>-compounds ethanol, acetaldehyde and acetic acid between leaves of Amazonian floodplain tree species and the atmosphere
- Author
-
Rottenberger, S., primary, Kleiss, B., additional, Kuhn, U., additional, Wolf, A., additional, Piedade, M. T. F., additional, Junk, W., additional, and Kesselmeier, J., additional
- Published
- 2008
- Full Text
- View/download PDF
31. Central Amazonian Floodplain Forests: Tree Adaptations in a Pulsing System
- Author
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Parolin, P., primary, De Simone, O., additional, Haase, K., additional, Waldhoff, D., additional, Rottenberger, S., additional, Kuhn, U., additional, Kesselmeier, J., additional, Kleiss, B., additional, Schmidt, W., additional, Piedade, M. T F., additional, and Junk, W. J., additional
- Published
- 2004
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- View/download PDF
32. Exchange fluxes of NO2 and O3 at soil and leaf surfaces in an Amazonian rain forest
- Author
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Gut, A., primary, Scheibe, M., additional, Rottenberger, S., additional, Rummel, U., additional, Welling, M., additional, Ammann, C., additional, Kirkman, G. A., additional, Kuhn, U., additional, Meixner, F. X., additional, Kesselmeier, J., additional, Lehmann, B. E., additional, Schmidt, W., additional, Müller, E., additional, and Piedade, M. T. F., additional
- Published
- 2002
- Full Text
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33. The Amazon's Floodplain: The Promise and the Challenge
- Author
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Lovejoy, Thomas E., primary, Junk, W. J., additional, Ohly, J. J., additional, Piedade, M. T. F., additional, and Soares, M. G. M., additional
- Published
- 2002
- Full Text
- View/download PDF
34. NPP TROPICAL FOREST: MANAUS, BRAZIL, 1963-1990
- Author
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JUNK, W. J., primary and PIEDADE, M. T. F., additional
- Published
- 2001
- Full Text
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35. A floodplain grassland of the central Amazon
- Author
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Piedade, M. T. F., Junk, W. J., Mello, J. A. N. de, Piedade, M. T. F., Junk, W. J., and Mello, J. A. N. de
- Abstract
Pages: 127-158
- Published
- 1992
36. Influence of flood-pulse and land-use on the composition of herbaceous species on a floodplain in Central Amazonia
- Author
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Conserva, A., primary and Piedade, M. T. F., additional
- Published
- 1998
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37. The effect of flooding on the exchange of the volatile C2-compounds ethanol, acetaldehyde and acetic acid between leaves of Amazonian floodplain tree species and the atmosphere.
- Author
-
Rottenberger, S., Kleiss, B., Kuhn, U., Wolf, A., Piedade, M. T. F., Junk, W., and Kesselmeier, J.
- Subjects
FLOODS ,ALCOHOL ,ACETALDEHYDE ,ACETIC acid ,LEAVES ,ATMOSPHERE - Abstract
The effect of root inundation on the leaf emissions of ethanol, acetaldehyde and acetic acid in relation to assimilation and transpiration was investigated with 2-3 years old tree seedlings of four Amazonian floodplain species by applying dynamic cuvette systems under greenhouse conditions. Emissions were monitored over a period of several days of inundation using a combination of Proton Transfer Reaction Mass Spectrometry (PTR-MS) and conventional techniques (HPLC, ion chromatography). Under non-flooded conditions, none of the species exhibited measurable emissions of any of the compounds, but rather low deposition of acetaldehyde and acetic acid was observed instead. Tree species specific variations in deposition velocities were largely due to variations in stomatal conductance. Flooding of the roots resulted in leaf emissions of ethanol and acetaldehyde by all species, while emissions of acetic acid were only observed from the species exhibiting the highest ethanol and acetaldehyde emission rates. All three compounds showed a similar diurnal emission profile, each displaying an emission burst in the morning, followed by a decline in the evening. This concurrent behavior supports the conclusion, that all three compounds emitted by the leaves are derived from ethanol produced in the roots by alcoholic fermentation, transported to the leaves with the transpiration stream and finally partly converted to acetaldehyde and acetic acid by enzymatic processes. Co-emissions and peaking in the early morning suggest that root ethanol, after transportation with the transpiration stream to the leaves and enzymatic oxidation to acetaldehyde and acetate, is the metabolic precursor for all compounds emitted, though we can not totally exclude other production pathways. Emission rates substantially varied among tree species, with maxima differing by up to two orders of magnitude (25-1700 nmol m
-2 min-1 for ethanol and 5-500 nmol m-2 min-1 for acetaldehyde). Acetic acid emissions reached 12 nmol m-2 min-1 . The observed differences in emission rates between the tree species are discussed with respect to their root adaptive strategies to tolerate long term flooding, providing an indirect line of evidence that the root ethanol production is a major factor determining the foliar emissions. Species which develop morphological root structures allowing for enhanced root aeration produced less ethanol and showed much lower emissions compared to species which lack gas transporting systems, and respond to flooding with substantially enhanced fermentation rates and a non-trivial loss of carbon to the atmosphere. The pronounced differences in the relative emissions of ethanol to acetaldehyde and acetic acid between the tree species indicate that not only the ethanol production in the roots but also the metabolic conversion in the leaf is an important factor determining the release of these compounds to the atmosphere. [ABSTRACT FROM AUTHOR]- Published
- 2008
- Full Text
- View/download PDF
38. ESTRATÉGIAS DE DISPERSÃO, PRODUÇÃO DE FRUTOS E EXTRATIVISMO DA PALMEIRA Astrocaryum jauari MART. NOS IGAPÓS DO RIO NEGRO: IMPLICAÇÕES PARA A ICTIOFAUNA.
- Author
-
Piedade, M. T. F., Parolin, P., and Junk, W. J.
- Subjects
- *
PALMS , *FRUIT development , *BOTANY , *BIOMASS , *FOREST ecology - Abstract
Astrocaryum jauari is the most frequent palmin the floodplains (igapó) of the Rio Negro, in Brazilian Amazonia. It grows to 20 m of height and is rarely found isolated. More commonly, 4-6 individuals of different sizes stand together which originate from the same rhizome. Fruit abscission occurs at highest water levels and dispersal occurs by fish. The palm has commercial value: until 1998, for 20 years 'palmito' was the basis of the industrial production in Central Amazonia. In the present study, seasonal dynamics and biomass of fruit production in A. jauari are described in relation to water level and annual flood duration. Systematic studies were performed at the Ecological Station of the Anavilhanas Archipelago, with an inventory area covering 5.000 m². Fruit production was monitored at weekly intervals and biomass was determined. Data on the dispersing fishes was obtained by collection in the field and by interviews of local people. A. jauari occurs from the higher levels to the lowest in the flooding gradient, being waterlogged up to 270-340 days/year. 125 individuals of A. jauari occorred in the sampled 5.000 m², which is equivalent to a density of 250 ind/ha in the Anavilhanas. Only adult trees which were directly exposed to light produced fruits. 16 species of fish feed on the fruits of A. jauari. Ten of these act as possible dispersers, 3 as predators. The high contents of vitamine A may be attractive for the fishes. Since the fruits do not have structures enhancing floatation, hydrochoric dispersal does not occur and the seeds succumb to the hypoxic conditions under water. In habitats with short periods of flooding, the fruits may be accumulated near the adult plant (barochory). Other trees occurring in the habitats colonized by A. jauari have hydrochoric and ichthyochoric dispersal syndromes and show high flooding tolerance. In the main area of extractivism of the past, in the Município Barcelos, the density of the species varied between the islands, and had densities between 250 and 2.000 ind/ha. Here, one worker could fell up to 90 palms at high water (May, June) and up to 25 in the low water period (december, january). For each tree, 0.5 to 1 bin of processed bin of "palmito" is produced. Assuming a mean number of ten workers in the area, 900 to 250 palms are exploited per day, corresponding to 1-0.5 ha destroyed forest. If we consid the densities of the palm and its productivity as calculated for the Anavilhanas islands (whcih was 165 kg), extractivism without replacement of new palm trees implies a fast extinction and exclusion of this ressource for the ichthyofauna of the archipelago with all consequences for the local people. [ABSTRACT FROM AUTHOR]
- Published
- 2003
39. Exchange fluxes of NO2 and O3 at soil and leaf surfaces in an Amazonian rain forest.
- Author
-
Gut, A., Scheibe, M., Rottenberger, S., Rummel, U., Welling, M., Ammann, C., Kirkman, G. A., Kuhn, U., Meixner, F. X., Kesselmeier, J., Lehmann, B. E., Schmidt, W., Müller, E., and Piedade, M. T. F.
- Published
- 2002
- Full Text
- View/download PDF
40. Very high productivity of the C4 aquatic grass Echinochloa polystachya in the Amazon floodplain confirmed by net ecosystem CO2 flux measurements.
- Author
-
Morison, J. I. L., Piedade, M. T. F., Müller, E., Long, S. P., Junk, W. J., and Jones, M. B.
- Subjects
PRIMARY productivity (Biology) ,BIOLOGICAL productivity ,WETLANDS ,WATER use ,ECHINOCHLOA ,GRASSES - Abstract
Fluxes of CO
2 and H2 O vapour from dense stands of the C4 emergent macrophyte grass Echinochloa polystachya were measured by eddy covariance in both the low water (LW) and high water (HW, flooded) phases of the annual Amazon river cycle at Manaus, Brazil. Typical clear-sky midday CO2 uptake rates by the vegetation stand (including detritus, sediment or water surface) were 30 and 35 µmol CO2 (ground) m–2 s–1 in the LW and HW periods, respectively. A rectangular hyperbola model fitted the responses of "instantaneous" (20- or 30-min average) net CO2 exchange rates to incident photosynthetic photon flux densities (PFD) well. Stand evaporation rates were linearly related to PFD. The major difference in CO2 uptake rates between the two periods was the larger respiration flux during LW due to the CO2 efflux from sediment, roots and litter. Integrated 20- or 30-min fluxes were used to derive relationships between daily CO2 and H2 O vapour fluxes and incident radiation. The daily CO2 fluxes were almost linearly related to incident radiation, but there was evidence of saturation at the highest daily radiation totals. Annual productivity estimated from the daily model in 1996–1997 agreed closely with that previously estimated for 1985–1986 from a leaf-scale photosynthetic model, but were some 15% less than those derived at that time from biomass harvests. Both CO2 uptake and water use efficiency were comparable with those found in fertilised maize fields in warm temperate conditions. [ABSTRACT FROM AUTHOR]- Published
- 2000
- Full Text
- View/download PDF
41. Leaf and canopy photosynthetic CO2 uptake of a stand of Echinochloa polystachya on the Central Amazon floodplain
- Author
-
Piedade, M. T. F., Long, S. P., and Junk, W. J.
- Abstract
The C
4 grass Echinochloa polystachya, which forms dense and extensive monotypic stands on the Varzea floodplains of the Amazon region, provides the most productive natural higher plant communities known. The seasonal cycle of growth of this plant is closely linked to the annual rise and fall of water level over the floodplain surface. Diurnal cycles of leaf photosynthesis and transpiration were measured at monthly intervals, in parallel with measurements of leaf area index, canopy light interception and biomass. By artificial manipulation of the light flux incident on leaves in the field light-response curves of photosynthesis at the top and near to the base of the canopy were generated. Fitted light-response curves of CO2 uptake were combined with information of leaf area index, incident light and light penetration of the canopy to estimate canopy rates of photosynthesis. Throughout the period in which the floodplains were submerged photosynthetic rates of CO2 uptake (A) for the emergent leaves were high with a mean of c. 30 µmol m-2 s-1 at mid-day and occasional values of 40 µmol m-2 s-1 . During the brief dry phase, when the floodplain surface is uncovered, there was a significant depression of A, with mid-day mean values of c. 17 µmol m-2 s-1 . This corresponded with a c. 50% decrease in stomatal conductance, and a c. 35% depression in the ratio of the leaf inter-cellular to external CO2 concentration (ci /ca ). During the dry phase, a midday depression of rates of CO2 assimilation was observed. The lowest leaf area index (F) was c. 2 in November–December, when the flood plain was dry, and again in May, when the rising floodwaters were submerging leaves faster than they were replaced. The maximum F of c. 5 was in August when the floodwaters were receding rapidly. Canopy light interception efficiency varied from 0.90 to 0.98. Calculated rates of canopy photosynthesis exceeded 18 mol C m-2 mo-1 throughout the period of flooding, with a peak of 37 mol C m-2 mo-1 in August, but declined to 13 mol C m-2 mo-1 in November during the dry phase. Estimated uptake of carbon by the canopy from the atmosphere, over 12 months, was 3.57 kg C m-2 . This was insufficient to account for the 3.99 kg C m-2 of net primary production, measured simultaneously by destructive harvesting. It is postulated that this discrepancy might be accounted for by internal diffusion of CO2 from the CO2 -rich waters and sediments via the roots and stems to the sites of assimilation in the leaves.- Published
- 1994
- Full Text
- View/download PDF
42. The effect of flooding on the exchange of the volatile C-2-compounds ethanol, acetaldehyde and acetic acid between leaves of Amazonian floodplain tree species and the atmosphere
- Author
-
Rottenberger, S., Kleiss, B., Kuhn, U., Wolf, A., Piedade, M. T. F., Junk, W., and Jürgen Kesselmeier
- Abstract
The effect of root inundation on the leaf emissions of ethanol, acetaldehyde and acetic acid in relation to assimilation and transpiration was investigated with 2–3 years old tree seedlings of four Amazonian floodplain species by applying dynamic cuvette systems under greenhouse conditions. Emissions were monitored over a period of several days of inundation using a combination of Proton Transfer Reaction Mass Spectrometry (PTR-MS) and conventional techniques (HPLC, ion chromatography). Under non-flooded conditions, none of the species exhibited measurable emissions of any of the compounds, but rather low deposition of acetaldehyde and acetic acid was observed instead. Tree species specific variations in deposition velocities were largely due to variations in stomatal conductance. Flooding of the roots resulted in leaf emissions of ethanol and acetaldehyde by all species, while emissions of acetic acid were only observed from the species exhibiting the highest ethanol and acetaldehyde emission rates. All three compounds showed a similar diurnal emission profile, each displaying an emission burst in the morning, followed by a decline in the evening. This concurrent behavior supports the conclusion, that all three compounds emitted by the leaves are derived from ethanol produced in the roots by alcoholic fermentation, transported to the leaves with the transpiration stream and finally partly converted to acetaldehyde and acetic acid by enzymatic processes. Co-emissions and peaking in the early morning suggest that root ethanol, after transportation with the transpiration stream to the leaves and enzymatic oxidation to acetaldehyde and acetate, is the metabolic precursor for all compounds emitted, though we can not totally exclude other production pathways. Emission rates substantially varied among tree species, with maxima differing by up to two orders of magnitude (25–1700 nmol m−2 min−1 for ethanol and 5–500 nmol m−2 min−1 for acetaldehyde). Acetic acid emissions reached 12 nmol m−2 min−1. The observed differences in emission rates between the tree species are discussed with respect to their root adaptive strategies to tolerate long term flooding, providing an indirect line of evidence that the root ethanol production is a major factor determining the foliar emissions. Species which develop morphological root structures allowing for enhanced root aeration produced less ethanol and showed much lower emissions compared to species which lack gas transporting systems, and respond to flooding with substantially enhanced fermentation rates and a non-trivial loss of carbon to the atmosphere. The pronounced differences in the relative emissions of ethanol to acetaldehyde and acetic acid between the tree species indicate that not only the ethanol production in the roots but also the metabolic conversion in the leaf is an important factor determining the release of these compounds to the atmosphere.
43. Phylogenetic classification of the world's tropical forests
- Author
-
Slik, J. W. F., Franklin, J., Arroyo-Rodríguez, V., Field, R., Aguilar, S., Aguirre, N., Ahumada, J., Aiba, S.-I., Alves, L. F., Anitha, K., Avella, A., Mora, F., Aymard, G. A. C., Báez, S., Balvanera, P., Bastian, M. L., Bastin, J.-F., Bellingham, P. J., Van Den Berg, E., Da Conceição Bispo, P., Boeckx, P., Boehning-Gaese, K., Bongers, F., Boyle, B., Brambach, F., Brearley, F. Q., Brown, S., Chai, S.-L., Chazdon, R. L., Chen, S., Chhang, P., Chuyong, G., Ewango, C., Coronado, I. M., Cristóbal-Azkarate, J., Culmsee, H., Damas, K., Dattaraja, H. S., Davidar, P., DeWalt, S. J., DIn, H., Drake, D. R., Duque, A., Durigan, G., Eichhorn, K., Eler, E. S., Enoki, T., Ensslin, A., Fandohan, A. B., Farwig, N., Feeley, K. J., Fischer, M., Forshed, O., Garcia, Q. S., Garkoti, S. C., Gillespie, T. W., Gillet, J.-F., Gonmadje, C., Granzow-De La Cerda, I., Griffith, D. M., Grogan, J., Hakeem, K. R., Harris, D. J., Harrison, R. D., Hector, A., Hemp, A., Homeier, J., Hussain, M. S., Ibarra-Manríquez, G., Hanum, I. F., Imai, N., Jansen, P. A., Joly, C. A., Joseph, S., Kartawinata, K., Kearsley, E., Kelly, D. L., Kessler, M., Killeen, T. J., Kooyman, R. M., Laumonier, Y., Laurance, S. G., Laurance, W. F., Lawes, M. J., Letcher, S. G., Lindsell, J., Lovett, J., Lozada, J., Lu, X., Lykke, A. M., Bin Mahmud, K., Mahayani, N. P. D., Mansor, A., Marshall, A. R., Martin, E. H., Matos, D. C. L., Meave, J. A., Melo, F. P. L., Mendoza, Z. H. A., Metali, F., Medjibe, V. P., Metzger, J. P., Metzker, T., Mohandass, D., Munguía-Rosas, M. A., Muñoz, R., Nurtjahy, E., De Oliveira, E. L., Onrizal, Parolin, P., Parren, M., Parthasarathy, N., Paudel, E., Perez, R., Pérez-García, E. A., Pommer, U., Poorter, L., Qi, L., Piedade, M. T. F., Pinto, J. R. R., Poulsen, A. D., Poulsen, J. R., Powers, J. S., Prasad, R. C., Puyravaud, J.-P., Rangel, O., Reitsma, J., Rocha, D. S. B., Rolim, S., Rovero, F., Rozak, A., Ruokolainen, K., Rutishauser, E., Rutten, G., Mohd Said, M. N., Saiter, F. Z., Saner, P., Santos, B., Dos Santos, J. R., Sarker, S. K., Schmitt, C. B., Schoengart, J., Schulze, M., Sheil, D., Sist, P., Souza, A. F., Spironello, W. R., Sposito, T., Steinmetz, R., Stevart, T., Suganuma, M. S., Sukri, R., Sultana, A., Sukumar, R., Sunderland, T., Supriyadi, Suresh, H. S., Suzuki, E., Tabarelli, M., Tang, J., Tanner, E. V. J., Targhetta, N., Theilade, I., Thomas, D., Timberlake, J., De Morisson Valeriano, M., Van Valkenburg, J., Van Do, T., Van Sam, H., Vandermeer, J. H., Verbeeck, H., Vetaas, O. R., Adekunle, V., Vieira, S. A., Webb, C. O., Webb, E. L., Whitfeld, T., Wich, S., Williams, J., Wiser, S., Wittmann, F., Yang, X., Yao, C. Y. A., Yap, S. L., Zahawi, R. A., Zakaria, R., and Zang, R.
- Subjects
15. Life on land
44. Primary productivity of natural grass ecosystems of the tropics: A reappraisal
- Author
-
Long, S. P., primary, Garcia Moya, E., additional, Imbamba, S. K., additional, Kamnalrut, A., additional, Piedade, M. T. F., additional, Scurlock, J. M. O., additional, Shen, Y. K., additional, and Hall, D. O., additional
- Published
- 1989
- Full Text
- View/download PDF
45. Biomass and primary-production of herbaceous plant communities in the Amazon floodplain
- Author
-
Piedade, M. T. F. and Junk, W. J.
- Subjects
BIOMASS ,FLOODPLAINS ,PLANTS - Published
- 1993
46. Nutrient dynamics of the highly productive C4 macrophyte Echinochloapolystachya on the Amazon floodplain
- Author
-
Junk, W. J., Long, S. P., and Piedade, M. T. F.
- Subjects
PHOSPHORUS ,PLANT physiology ,NITROGEN ,AQUATIC plants ,POTASSIUM - Abstract
Echinochloa polystachya forms extensive monotypic stands on the lower levels of the Amazon floodplains. During its annual growth cycle c.100 t (dry mass) ha{sup}-1{end} of biomass is formed as the floodplain is being submerged (December--September) and a phase of death and decomposition occurs when the water has retreated (October- -November). This study examines the mineral nutrient dynamics of this plant and its potential significance to the nutrient status of the flood plain. Echinochloa polystachya was sampled monthly from a study site in the central Amazon. N, P and K contents for different plant organs were determined and net uptake calculated from concurrent measurements of dry matter production and turnover. Leaf N, P and K contents were c. 20, 1.7 and 19 g kg{sup}-1{end}, values typical of nutrient-repletestands of C{sub}4{end} plants. Stem concentrations were c. 12% of those of the leaves. Net N and P uptake followed the rise in the river level, whilst K appeared independent of water level. The vegetation accumulated 377, 51 and 1136 kg ha{sup}-2{end} of N, P and K, respectively, during the growth phase. Over a possible 5000 km{sup}2{end} of these stands in the Varzea, this represents a massive sequestration of nutrients in the flood phase and a high release during the following low-water period. It is suggested that the E. polystachya stands could have a role in maintaining the nutrient status of the Amazon floodplain. [ABSTRACT FROM AUTHOR]
- Published
- 1997
47. POPULATION DYNAMICS OF ATTALEA EXCELSA (ARECACEAE) IN FLOODPLAIN FOREST OF THE AMAZONIAN ESTUARY.
- Author
-
Dantas A. R., Lira-Guedes A. C., Guedes M. C., Piedade M. T. F., and Batista A. P. B.
- Subjects
- *
FLOODPLAIN forests , *POPULATION dynamics , *PALMS , *FLOODPLAINS , *PARAMETERS (Statistics) , *ESTUARIES - Abstract
Attalea excelsa (urucurizeiro) is a dominant palm of the estuarine floodplains, with great potential for nontimber management. This study evaluated the population dynamics of urucurizeiro and the factors that contribute to colonising of this species in a flooded environment. Individuals with base height circumference ≥ 30 cm in 2011 and 2014 were measured in 55.95 ha of floodplain forest in southern Amapá, Brazil. The parameters of population dynamics (mortality, recruitment and growth) in high and low floodplain environments were determined. Ripley's K function was used to analyse the spatial distribution. Population density in 2011 was 3.99 individual ha-1, and in 2014 the density increased to 4.09 individual ha-1. Mortality rate was zero and the recruitment rate was 1.05% year-1. Basal area in 2011 was 0.49 m² ha-1 and in 2014, it reached 0.72 m² ha-1. Diameter growth rate was 5.32 cm year-1. The population presented an aggregate distribution pattern. Structural differences in diameter (F = 9.15, p = 0.003) and basal area (F = 10.7, p = 0.001) were evident between high and low floodplain forests. The increase in diameter was higher in low floodplain (3.98 cm year-1) compared with high floodplain (1.35 cm year-1). The patterns shown by A. excelsa are reflections of its high adaptation to the daily flooded environment. [ABSTRACT FROM AUTHOR]
- Published
- 2020
- Full Text
- View/download PDF
48. Natural history of the hyperdominant tree, Pentaclethra macroloba (Willd.) Kuntze, in the Amazon River estuary.
- Author
-
Dantas AR, Vasconcelos CC, Guedes MC, Lira-Guedes AC, and Piedade MTF
- Subjects
- Animals, Brazil, Estuaries, Floods, Trees physiology, Seeds physiology, Seeds growth & development, Rivers, Seasons
- Abstract
Pentaclethra macroloba is a hyperdominant species with multiple uses in the Amazon. This species tolerates varying flood amplitudes, however the effect of flood topographic gradient on its ecophysiology remains unclear. We want to know if individuals from the high (10 trees) and low (20 trees) várzea show distinct phenological patterns as a function of the flood gradient, as well as their colonization strategies and their seed predators. From February 2018 to December 2019, we monitored the phenology of P. macroloba. There was no difference in phenological patterns between the two environments, but flooding caused different phenological responses. The increase in temperature favored the production of flower buds and increased precipitation reduced the proportion of flowering trees in both environments. The increase in rainfall and river flood level favored the ripe fruit only in the low várzea where individuals were most exposed to flooding. When the flood level increased, there was a greater proportion of trees losing leaves in both environments. The species produces high variability in seed size (length: H = 49.2, p > 0.001; width: H = 62.5, p > 0.001; weight: H = 70.4, p > 0.001). The seed predation rate was 5%, mainly caused by Carmenta surinamensis moth larva. The flood gradient established different phenological responses in the species, directing trees to have a better reproductive performance. The low predation rate and the variability in seed size are factors that contribute to the formation of large population densities in the Amazon River estuary.
- Published
- 2025
- Full Text
- View/download PDF
49. Very high productivity of the C 4 aquatic grass Echinochloa polystachya in the Amazon floodplain confirmed by net ecosystem CO 2 flux measurements.
- Author
-
Morison JIL, Piedade MTF, Müller E, Long SP, Junk WJ, and Jones MB
- Abstract
Fluxes of CO
2 and H2 O vapour from dense stands of the C4 emergent macrophyte grass Echinochloa polystachya were measured by eddy covariance in both the low water (LW) and high water (HW, flooded) phases of the annual Amazon river cycle at Manaus, Brazil. Typical clear-sky midday CO2 uptake rates by the vegetation stand (including detritus, sediment or water surface) were 30 and 35 µmol CO2 (ground) m-2 s-1 in the LW and HW periods, respectively. A rectangular hyperbola model fitted the responses of "instantaneous" (20- or 30-min average) net CO2 exchange rates to incident photosynthetic photon flux densities (PFD) well. Stand evaporation rates were linearly related to PFD. The major difference in CO2 uptake rates between the two periods was the larger respiration flux during LW due to the CO2 efflux from sediment, roots and litter. Integrated 20- or 30-min fluxes were used to derive relationships between daily CO2 and H2 O vapour fluxes and incident radiation. The daily CO2 fluxes were almost linearly related to incident radiation, but there was evidence of saturation at the highest daily radiation totals. Annual productivity estimated from the daily model in 1996-1997 agreed closely with that previously estimated for 1985-1986 from a leaf-scale photosynthetic model, but were some 15% less than those derived at that time from biomass harvests. Both CO2 uptake and water use efficiency were comparable with those found in fertilised maize fields in warm temperate conditions.- Published
- 2000
- Full Text
- View/download PDF
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