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Biblioteca(s): |
Embrapa Agroindústria Tropical; Embrapa Agropecuária Oeste; Embrapa Algodão; Embrapa Amapá; Embrapa Amazônia Ocidental; Embrapa Cerrados; Embrapa Gado de Corte; Embrapa Meio Ambiente; Embrapa Meio Norte / UEP-Parnaíba; Embrapa Meio-Norte; Embrapa Pantanal; Embrapa Semiárido; Embrapa Soja. MenosEmbrapa Agroindústria Tropical; Embrapa Agropecuária Oeste; Embrapa Algodão; Embrapa Amapá; Embrapa Amazônia Ocidental; Embrapa Cerrados; Embrapa Gado de Corte; Embrapa Meio Ambiente; Embrapa Meio Norte / UEP-Parnaíba; Embrapa Meio-Norte... Mostrar Todas |
Data corrente: |
17/03/2003 |
Data da última atualização: |
21/03/2003 |
Autoria: |
SCORZA JUNIOR, R. P. |
Título: |
Pesticide leaching in macroporous clay soils: field experiment and modeling. |
Ano de publicação: |
2002 |
Fonte/Imprenta: |
2002. |
Páginas: |
234 p. |
ISBN: |
905808745X |
Idioma: |
Inglês Português |
Notas: |
Doctoral Thesis, Wageningen University and Research Centre. |
Conteúdo: |
The presence of macropores (i.e. shrinkage cracks, earthworm and root channels) in the unsaturated zone can enhance pesticide leaching to groundwater and therefore increase the risk of groundwater contamination. In this thesis, experimental and modeling approaches were used to obtain a better understanding of the processes that affect pesticide leaching in cracked clay soils at the field scale. A field experiment (1.2 ha) was
conducted to study the movement of water and bromide, and of two pesticides with contrasting mobility (bentazone and imidacloprid). A rapid breakthrough of bromide and pesticides in drain water and groundwater was observed, which is a strong evidence for preferential transport in this soil. Two pesticide leaching models were tested using the data from the field experiment: (i) the chromatographic flow model PEARL and (ii) the preferential flow model MACRO. The calibration of PEARL indicated that a large dispersion length was necessary to simulate bromide leaching in this soil correctly, which implies a large non-uniformity of solute transport. This calibration worked well for the mobile pesticide bentazone but not for imidacloprid, which is moderately adsorbed. So the solute transport in this cracked clay soil could not be described with the convection-dispersion
equation even after increasing the dispersion length. The bulk of bentazone leaching was underestimated with MACRO although it simulated the leaching of imidacloprid reasonably well. The fast transport of all substances via macropore flow could be simulated well with MACRO although calibration of some sensitive and difficult to measure parameters was necessary. Considering that preferential flow may depend on the processes at the soil surface, a model that simulates water infiltration, overland flow, macropore flow and water storage at soil surface was developed. Simulations revealed that macropores at the soil surface can receive water before the maximum water storage at soil is reached. Therefore, the frequently used assumption that overland flow only starts after the maximum water storage at soil surface is attained can lead to underestimation of macropore flow for short showers. MenosThe presence of macropores (i.e. shrinkage cracks, earthworm and root channels) in the unsaturated zone can enhance pesticide leaching to groundwater and therefore increase the risk of groundwater contamination. In this thesis, experimental and modeling approaches were used to obtain a better understanding of the processes that affect pesticide leaching in cracked clay soils at the field scale. A field experiment (1.2 ha) was
conducted to study the movement of water and bromide, and of two pesticides with contrasting mobility (bentazone and imidacloprid). A rapid breakthrough of bromide and pesticides in drain water and groundwater was observed, which is a strong evidence for preferential transport in this soil. Two pesticide leaching models were tested using the data from the field experiment: (i) the chromatographic flow model PEARL and (ii) the preferential flow model MACRO. The calibration of PEARL indicated that a large dispersion length was necessary to simulate bromide leaching in this soil correctly, which implies a large non-uniformity of solute transport. This calibration worked well for the mobile pesticide bentazone but not for imidacloprid, which is moderately adsorbed. So the solute transport in this cracked clay soil could not be described with the convection-dispersion
equation even after increasing the dispersion length. The bulk of bentazone leaching was underestimated with MACRO although it simulated the leaching of imidacloprid reasonably well. The fast t... Mostrar Tudo |
Palavras-Chave: |
Água subterrânea; Bacia; Bentazona; Bentazone; Contaminacao - Agua subterranea; Contamination; Cracked clay soil; Experimento de campo; Inverse modeling; Macroporo; Macroporosidade; Mobilidade; Modelagem matemática; Modeling; Modeling pesticide fate; Modelo; Pesticida - Lixiviacao; Pesticide leaching; Pesticide leaching models; Preferential transport; Soils; Transporte preferencial. |
Thesagro: |
Águas Subterrâneas; Contaminação; Lixiviação; Modelo de Simulação; Pesticida; Solo; Solo Argiloso. |
Thesaurus Nal: |
groundwater; groundwater contamination; imidacloprid; leaching; macropores; models; pesticides; preferential flow. |
Categoria do assunto: |
-- |
Marc: |
LEADER 03790nam a2200589 a 4500 001 1566560 005 2003-03-21 008 2002 bl uuuu m 00u1 u #d 020 $a905808745X 100 1 $aSCORZA JUNIOR, R. P. 245 $aPesticide leaching in macroporous clay soils$bfield experiment and modeling. 260 $a2002.$c2002 300 $a234 p. 500 $aDoctoral Thesis, Wageningen University and Research Centre. 520 $aThe presence of macropores (i.e. shrinkage cracks, earthworm and root channels) in the unsaturated zone can enhance pesticide leaching to groundwater and therefore increase the risk of groundwater contamination. In this thesis, experimental and modeling approaches were used to obtain a better understanding of the processes that affect pesticide leaching in cracked clay soils at the field scale. A field experiment (1.2 ha) was conducted to study the movement of water and bromide, and of two pesticides with contrasting mobility (bentazone and imidacloprid). A rapid breakthrough of bromide and pesticides in drain water and groundwater was observed, which is a strong evidence for preferential transport in this soil. Two pesticide leaching models were tested using the data from the field experiment: (i) the chromatographic flow model PEARL and (ii) the preferential flow model MACRO. The calibration of PEARL indicated that a large dispersion length was necessary to simulate bromide leaching in this soil correctly, which implies a large non-uniformity of solute transport. This calibration worked well for the mobile pesticide bentazone but not for imidacloprid, which is moderately adsorbed. So the solute transport in this cracked clay soil could not be described with the convection-dispersion equation even after increasing the dispersion length. The bulk of bentazone leaching was underestimated with MACRO although it simulated the leaching of imidacloprid reasonably well. The fast transport of all substances via macropore flow could be simulated well with MACRO although calibration of some sensitive and difficult to measure parameters was necessary. Considering that preferential flow may depend on the processes at the soil surface, a model that simulates water infiltration, overland flow, macropore flow and water storage at soil surface was developed. Simulations revealed that macropores at the soil surface can receive water before the maximum water storage at soil is reached. Therefore, the frequently used assumption that overland flow only starts after the maximum water storage at soil surface is attained can lead to underestimation of macropore flow for short showers. 650 $agroundwater 650 $agroundwater contamination 650 $aimidacloprid 650 $aleaching 650 $amacropores 650 $amodels 650 $apesticides 650 $apreferential flow 650 $aÁguas Subterrâneas 650 $aContaminação 650 $aLixiviação 650 $aModelo de Simulação 650 $aPesticida 650 $aSolo 650 $aSolo Argiloso 653 $aÁgua subterrânea 653 $aBacia 653 $aBentazona 653 $aBentazone 653 $aContaminacao - Agua subterranea 653 $aContamination 653 $aCracked clay soil 653 $aExperimento de campo 653 $aInverse modeling 653 $aMacroporo 653 $aMacroporosidade 653 $aMobilidade 653 $aModelagem matemática 653 $aModeling 653 $aModeling pesticide fate 653 $aModelo 653 $aPesticida - Lixiviacao 653 $aPesticide leaching 653 $aPesticide leaching models 653 $aPreferential transport 653 $aSoils 653 $aTransporte preferencial
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Registros recuperados : 29 | |
24. | ![Imagem marcado/desmarcado](/consulta/web/img/desmarcado.png) | QUADROS, B. R. de; RIBEIRO, O. D.; RODRIGUES JUNIOR, O. M.; NASCIMENTO, W. M. O. do; CAVARIANI, C.; NASCIMENTO, E. Biometria do endocarpo de taperebá (Spondias mombin L. - Anacardiaceae). Revista Cultivando o Saber, v. 8, n. 3, p. 250-256, 2015.Tipo: Artigo em Periódico Indexado | Circulação/Nível: B - 5 |
Biblioteca(s): Embrapa Amazônia Oriental. |
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25. | ![Imagem marcado/desmarcado](/consulta/web/img/desmarcado.png) | RIBEIRO, O. D.; NASCIMENTO, W. M. O. do; ALMEIDA, E. G. L. de; OLIVEIRA, J. C. de. Caracterização morfológica de plantas em acessos de camucamuzeiro do banco de germoplasma da Embrapa Amazônia Oriental. In: SEMINÁRIO DE INICIAÇÃO CIENTÍFICA DA EMBRAPA, 14., 2010, Belém, PA. Bolsista de iniciação científica: um aporte ao desenvolvimento da pesquisa agropecuária: anais. Belém, PA: Embrapa Amazônia Oriental, 2010. 1 CD-ROM. PIBIC 2010.Tipo: Artigo em Anais de Congresso |
Biblioteca(s): Embrapa Amazônia Oriental. |
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27. | ![Imagem marcado/desmarcado](/consulta/web/img/desmarcado.png) | PANTOJA, J. dos S.; NASCIMENTO, W. M. O. do; RIBEIRO, O. D.; OLIVEIRA, M. do S. P. de. Superação da dormência em sementes de tucumã-do-pará com ácido giberélico. In: SEMINÁRIO DE INICIAÇÃO CIENTÍFICA DA EMBRAPA, 16., 2012, Belém, PA. Anais... Belém, PA: Embrapa Amazônia Oriental, 2012. 1 CD-ROM.Tipo: Artigo em Anais de Congresso |
Biblioteca(s): Embrapa Amazônia Oriental. |
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28. | ![Imagem marcado/desmarcado](/consulta/web/img/desmarcado.png) | NASCIMENTO, W. M. O. do; CARVALHO, J. E. U. de; ALMEIDA, E. G. L. de; RIBEIRO, O. D.; OLIVEIRA, J. C. Caracterização física do fruto e semente em acessos de camucamuzeiro. In: CONGRESSO BRASILEIRO DE RECURSOS GENÉTICOS; WORKSHOP EM BIOPROSPECÇÃO E CONSERVAÇÃO DE PLANTAS NATIVAS DO SEMI-ÁRIDO, 3.; WORKSHOP INTERNACIONAL SOBRE BIOENERGIA E MEIO AMBIENTE, 2010, Salvador. Bancos de germoplasma: descobrir a riqueza, garantir o futuro: anais. Brasília, DF: Embrapa Recursos Genéticos e Biotecnologia, 2010. p. 207. (Embrapa Recursos Genéticos e Biotecnologia. Documentos, 304). Editora técnica Clara Oliveira Goedert.Tipo: Resumo em Anais de Congresso |
Biblioteca(s): Embrapa Amazônia Oriental. |
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29. | ![Imagem marcado/desmarcado](/consulta/web/img/desmarcado.png) | RIBEIRO, O. D.; CRUZ, E. D.; SILVA, M. F. da; CHAVES, B. de A. C.; RIBEIRO, O. M. D.; GURGEL, E. S. C. Hymenaea parvifolia Huber: dormancy breaking, morphology of fruit, seed and seedling. Revista Ceres, v. 68, n. 2, p. 83-93, mar./abr. 2021.Tipo: Artigo em Periódico Indexado | Circulação/Nível: B - 1 |
Biblioteca(s): Embrapa Amazônia Oriental. |
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