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| Registros recuperados : 41 | |
| 14. |  | NOGUEIRA, A.; COSTA, F. R. C.; VILELA-SANTOS, M. C.; CASTILHO, C. V. de; ANDRADE, A.; CAMARGO, J. L. C.; LAURANCE, W. F.; BURNHAM, R. J. Liana assemblage structure in four sites across the Brazilian Amazon. In: SCHNITZER, S. A.; BONGERS, F.; BURNHAM, R. J.; PUTZ, F. E. Ecology of Lianas. Wiley-Blackwell, 2014.| Biblioteca(s): Embrapa Roraima. |
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| 15. | | SAMPAIO, P. T. B.; BARBOSA, A. P.; VIEIRA, G.; SPIRONELLO, W. R.; FERRAZ, I. D. K.; CAMARGO, J. L. C.; QUISEN, R. C. Silvicultura do pau rosa (Aniba rosaeodora Ducke). In: HIGUCHI, N.; SANTOS, J. dos; SAMPAIO, P. de T. B.; MARENCO, R. A.; FERRAZ, J.; SALES, P. C. de; SAITO, M.; MATSUMOTO, S. (Org.). Projeto Jacaranda fase II: pesquisas florestais na Amazônia Central. Manaus: Inpa, 2003. p. 179-190.| Biblioteca(s): Embrapa Amazônia Ocidental. |
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| 16. | | STARK, S. C.; BRESHEARS, D. D.; ARAGÓN, S.; VILLEGAS, J. C.; LAW, D. J.; SMITH, M. N.; MINOR, D. M.; ASSIS, R. L. de; ALMEIDA, D. R. A. de; OLIVEIRA, G. de; SALESKA, S. R.; SWANN, A. S.; MOURA, J. M. S.; CAMARGO, J. L.; SILVA, R. da; ARAGÃO, L. E. O. C.; OLIVEIRA JUNIOR, R. C. de. Reframing tropical savannization: linking changes in canopy structure to energy balance alterations that impact climate. Ecosphere, v. 11, n. 9, e03231, 2020.| Biblioteca(s): Embrapa Amazônia Oriental. |
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| 17. | | SMITH, M. N.; SCHITTI, J.; GONÇALVES, N.; MINOR, D.; ALMEIDA, D. R. A. de; ROCHA, D. G.; ARAGÓN, S.; MENIN, M.; GUEDES, M. C.; TONINI, H.; SILVA, K. E. da; ROSA, D. M.; NELSON, B. W.; CORDEIRO, C. L. O.; OLIVEIRA JUNIOR, R. C. de; SHAO, G.; SOUZA, M. S.; MCMAHON, S.; ALMEIDA, D.; ARAGÃO, L. E. O. C.; LIMA, N. Z. de; OLIVEIRA, G. de; ASSIS, R. L. de; CAMARGO, J. L.; MESQUITA, R. G.; SALESKA, S. R.; BRESHEARS, D. D.; COSTA, F. R. C.; STARK, S. C. Variations in Amazonian forest canopy structure and light environments across environmental and disturbance gradients. In: AGU FALL MEETING, 2019, San Francisco. Anais... San Francisco: AGU, 2019. Paper 499657.| Biblioteca(s): Embrapa Amazônia Ocidental; Embrapa Amazônia Oriental; Embrapa Pecuária Sul. |
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| 18. | | SMITH, M. N.; SCHITTI, J.; GONÇALVES, N.; MINOR, D.; ALMEIDA, D. R. A. de; ROCHA, D. G.; ARAGÓN, S.; MENIN, M.; GUEDES, M. C.; TONINI, H.; SILVA, K. E. da; ROSA, D. M.; NELSON, B. W.; CORDEIRO, C. L. O.; OLIVEIRA JUNIOR, R. C. de; SHAO, G.; SOUZA, M. S.; MCMAHON, S.; ALMEIDA, D.; ARAGÃO, L. E. O. C.; LIMA, N. Z. de; OLIVEIRA, G. de; ASSIS, R. L. de; CAMARGO, J. L.; MESQUITA, R. G.; SALESKA, S. R.; BRESHEARS, D. D.; COSTA, F. R. C.; STARK, S. C. Variations in Amazonian forest canopy structure and light environments across environmental and disturbance gradients. In: AGU FALL MEETING, 2019, San Francisco. Anais... San Francisco: AGU, 2019. Paper 499657.| Biblioteca(s): Embrapa Amapá. |
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| 19. | | SMITH, M. N.; STARK, S. C.; TAYLOR, T. C.; SCHIETTI, J.; ALMEIDA, D. R. A. de; ARAGÓN, S.; TORRALVO, K.; LIMA, A. P.; OLIVEIRA, G. de; ASSIS, R. L. de; LEITOLD, V.; PONTES-LOPES, A.; SCOLES, R.; VIEIRA, L. C. de S.; RESENDE, A. F.; COPPOLA, A. I.; BRANDÃO, D. O.; SILVA JUNIOR, J. de A.; LOBATO, L. F.; FREITAS, W.; ALMEIDA, D.; SOUZA, M. S.; MINOR, D. M.; VILLEGAS, J. C.; LAW, D. J.; GONÇALVES, N.; ROCHA, D. G. da; GUEDES, M. C.; TONINI, H.; SILVA, K. E. da; HAREN, J. van; ROSA, D. M.; VALLE, D. F. do; CORDEIRO, C. L.; LIMA, N. Z. de; SHAO, G.; MENOR, I. O.; CONTI, G.; FLORENTINO, A. P.; MONTTI, L.; ARAGÃO, L. E. O. C.; McMAHON, S. M.; PARKER, G. G.; BRESHEARS, D. D.; COSTA, A. C. L. da; MAGNUSSON, W. E.; MESQUITA, R.; CAMARGO, J. L. C.; OLIVEIRA JUNIOR, R. C. de; CAMARGO, P. B. de; SALESKA, S. R.; NELSON, B. W. Diverse anthropogenic disturbances shift Amazon forests along a structural spectrum. Frontiers in Ecology an the Environment, v. 21, n. 1, p. 24-32, 2023.| Biblioteca(s): Embrapa Amapá; Embrapa Amazônia Ocidental; Embrapa Amazônia Oriental; Embrapa Pecuária Sul. |
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| 20. | | BRIENEN, R. J. W.; PHILLIPS, O. L.; FELDPAUSCH, T. R.; GLOOR, E.; BAKER, T. R.; LLOYD, J.; LOPEZ-GONZALEZ, G.; MONTEAGUDO, A.; MALHI, Y.; LEWIS, L. S.; VÁSQUEZ MARTINEZ, R.; ALEXIADES, M.; ALVAREZ DAVILA, E.; ALVAREZ-LOAYZA, P.; ANDRADE, A.; ARAGAO, L. E. O. C.; ARAUJO-MURAKAMI, A.; ARETS, E. J. M. M.; ARROYO, L.; AYMARD, G.; BANKI, O.; BARALOTO, C.; BARROSO, J.; BONAL, D.; BOOT, R. G. A.; CAMARGO, J. L. C.; CASTILHO, C. V. de; CHAMA, V.; CHAO, K. J.; CHAVE, J.; COMISKEY, J. A.; CORNEJO VALVERDE, F.; COSTA, L. da; OLIVEIRA, E. de; DI FIORE, A.; ERWIN, T.; FAUSET, S.; FORSTHOFER, M.; GALBRAITH, D.; GROOT, N.; HÉRAULT, B.; HIGUCHI, N.; HONORIO CORONADO, E. N.; KEELING, H.; KILLEEN, T. J.; LAURANCE, W. F.; LAURANCE, S. G. W.; LICONA, J.; MAGNUSSEN, W. E.; MARIMON, B. S.; MARIMON JUNIOR, B. H.; MENDOZA, C.; NEILL, D.; NOGUEIRA, E. M.; NUNEZ, P.; PALLQUI CAMACHO, N. C.; PARADA, A.; PARDO-MOLINA, G.; PEACOCK, J.; PEÑA-CLAROS, M.; PICKAVANCE, G. C.; PITMAN, N.; POORTER, L.; PRIETO, A.; QUESADA, C. A.; RAMIREZ, F.; RAMIREZ-ANGULO, H.; RESTREPO, Z.; ROOPSIND, A.; RUDAS, A.; SALOMÃO, R.; SCHWARZ, M.; SILVA, N.; SILVA-ESPEJO, J. E.; SILVEIRA, M.; STROPP, J.; TALBOT, J.; TER STEEGE, H.; TERAN-AGUILAR, J.; TERBORGH, J.; THOMAS-CAESAR, R.; TOLEDO, M.; TORELLO-RAVENTOS, M.; UMETSU, R. K.; VAN DER HEIJDEN, G. M. F.; VAN DER HOUT, P.; GUIMARÃES VIEIRA, I. C.; VIEIRA, S. A.; VILANOVA, E.; VOS, V. A.; ZAGT, R. J. Long-term decline of the Amazon carbon sink. Nature, v. 519, n.7543, p. 344-348, 2015.| Biblioteca(s): Embrapa Roraima. |
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| Registros recuperados : 41 | |
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Registro Completo
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Biblioteca(s): |
Embrapa Clima Temperado. |
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Data corrente: |
09/03/2022 |
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Data da última atualização: |
25/08/2023 |
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Tipo da produção científica: |
Artigo em Periódico Indexado |
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Circulação/Nível: |
A - 1 |
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Autoria: |
RIBEIRO, P. L.; BAMBERG, A. L.; PEREIRA, I. dos S.; MONTEIRO, A. B.; POTES, M. da L.; LIMA, C. L. R. de. |
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Afiliação: |
PABLO LACERDA RIBEIRO; ADILSON LUIS BAMBERG, CPACT; IVAN DOS SANTOS PEREIRA; ALEX BECKER MONTEIRO; MARIANA DA LUZ POTES; CLÁUDIA LIANE RODRIGUES DE LIMA. |
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Título: |
Water treatment residuals for ameliorating sandy soils: Implications in environmental, soil and plant growth parameters. |
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Ano de publicação: |
2022 |
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Fonte/Imprenta: |
Geoderma, v. 407, 115537, 1 Feb. 2022. |
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Páginas: |
13 p. |
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ISSN: |
0016-7061 |
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Idioma: |
Inglês |
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Conteúdo: |
Water treatment residuals (WTR) application may improve the quality of sandy soils; however, nutrient deficiency to plants and potentially toxic elements (PTEs) may be limiting. In contrast, adjusting the WTR pH, soil pH and WTR application rate might prevent adverse effects. This study aimed to evaluate the environmental safety and agronomic effectiveness of limed WTR for application in sandy soils. The tested treatments were increasing rates (0, 15, 30 and 60 Mg ha−1 of dry mass) of ground, dried and limed WTR in sandy soil under field conditions. Soil samples with disturbed and undisturbed structure were collected to determine selected soil physical, hydraulic and chemical parameters related to fertility, as well as the soil concentration of PTEs. Nutrients and PTEs content in plant tissue and the agronomic performance of maize and ryegrass were also evaluated. WTR were beneficial as they increased the content of fine and reactive particles (clay and silt). In general, WTR rates did not spoil soil chemical parameters related to soil fertility; did not increase aluminium saturation; and did not change soil PTE contents which were below the limits indicated by environmental legislations. The tested WTR rates did not cause negative effects on the agronomic variables of maize and ryegrass plants. Thus, waste application rates up to 30 Mg ha−1 are recommended. Liming WTR and soil makes this material safe and suitable for application in sandy and acidic agricultural soils. MenosWater treatment residuals (WTR) application may improve the quality of sandy soils; however, nutrient deficiency to plants and potentially toxic elements (PTEs) may be limiting. In contrast, adjusting the WTR pH, soil pH and WTR application rate might prevent adverse effects. This study aimed to evaluate the environmental safety and agronomic effectiveness of limed WTR for application in sandy soils. The tested treatments were increasing rates (0, 15, 30 and 60 Mg ha−1 of dry mass) of ground, dried and limed WTR in sandy soil under field conditions. Soil samples with disturbed and undisturbed structure were collected to determine selected soil physical, hydraulic and chemical parameters related to fertility, as well as the soil concentration of PTEs. Nutrients and PTEs content in plant tissue and the agronomic performance of maize and ryegrass were also evaluated. WTR were beneficial as they increased the content of fine and reactive particles (clay and silt). In general, WTR rates did not spoil soil chemical parameters related to soil fertility; did not increase aluminium saturation; and did not change soil PTE contents which were below the limits indicated by environmental legislations. The tested WTR rates did not cause negative effects on the agronomic variables of maize and ryegrass plants. Thus, waste application rates up to 30 Mg ha−1 are recommended. Liming WTR and soil makes this material safe and suitable for application in sandy and acidic agricultural... Mostrar Tudo |
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Thesagro: |
Água; Solo Arenoso; Tratamento da Água. |
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Categoria do assunto: |
-- |
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Marc: |
LEADER 02211naa a2200241 a 4500
001 2140698
005 2023-08-25
008 2022 bl uuuu u00u1 u #d
022 $a0016-7061
100 1 $aRIBEIRO, P. L.
245 $aWater treatment residuals for ameliorating sandy soils$bImplications in environmental, soil and plant growth parameters.$h[electronic resource]
260 $c2022
300 $a13 p.
520 $aWater treatment residuals (WTR) application may improve the quality of sandy soils; however, nutrient deficiency to plants and potentially toxic elements (PTEs) may be limiting. In contrast, adjusting the WTR pH, soil pH and WTR application rate might prevent adverse effects. This study aimed to evaluate the environmental safety and agronomic effectiveness of limed WTR for application in sandy soils. The tested treatments were increasing rates (0, 15, 30 and 60 Mg ha−1 of dry mass) of ground, dried and limed WTR in sandy soil under field conditions. Soil samples with disturbed and undisturbed structure were collected to determine selected soil physical, hydraulic and chemical parameters related to fertility, as well as the soil concentration of PTEs. Nutrients and PTEs content in plant tissue and the agronomic performance of maize and ryegrass were also evaluated. WTR were beneficial as they increased the content of fine and reactive particles (clay and silt). In general, WTR rates did not spoil soil chemical parameters related to soil fertility; did not increase aluminium saturation; and did not change soil PTE contents which were below the limits indicated by environmental legislations. The tested WTR rates did not cause negative effects on the agronomic variables of maize and ryegrass plants. Thus, waste application rates up to 30 Mg ha−1 are recommended. Liming WTR and soil makes this material safe and suitable for application in sandy and acidic agricultural soils.
650 $aÁgua
650 $aSolo Arenoso
650 $aTratamento da Água
700 1 $aBAMBERG, A. L.
700 1 $aPEREIRA, I. dos S.
700 1 $aMONTEIRO, A. B.
700 1 $aPOTES, M. da L.
700 1 $aLIMA, C. L. R. de
773 $tGeoderma$gv. 407, 115537, 1 Feb. 2022.
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