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143. | | CERDEIRA, A. L.; GOMES, M. A. F.; QUEIROZ, R. C.; BONATO, P. S.; FERRACINI, V. L.; LANCHOTE, V. L. Herbicide and nitrate residues in surface and groundwater from sugarcane area in Brazil. Bolletino Chimico Farmaceutico, v.138, n.2, p.131, 1999. Biblioteca(s): Embrapa Meio Ambiente. |
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146. | | FERRACINI, V. L.; QUEIROZ, S. C. N. de; CASTRO, I. M. de; BLOCH JUNIOR, C.; NOGUEIRA, A. R. de A. Resíduos químicos e contaminantes em produtos de origem animal e vegetal. In: SIMPÓSIO SOBRE INOVAÇÃO E CRIATIVIDADE CIENTÍFICA NA EMBRAPA, 2., 2010, Brasília, DF. Posteres. Brasília, DF: Embrapa, 2010. Biblioteca(s): Embrapa Agroindústria de Alimentos. |
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147. | | BARIZON, R. R. M.; FIGUEIREDO, R. de O.; SOUZA, D. R. C. de; REGITANO, J. B.; FERRACINI, V. L. Pesticides in the surface waters of the Camanducaia River watershed, Brazil. Journal of Environmental Science and Health, Part B, New York, p. 1-10, 2019. Biblioteca(s): Embrapa Meio Ambiente. |
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148. | | ASSALIN, M. R.; MORAES, S. G. de; QUEIROZ, S. C. do N. de; FERRACINI, V. L.; DURÁN, N. Studies on degradation of glyphosate by several oxidative chemical processes: Ozonation, photolysis and heterogeneous photocatalysis. Journal of Environmental Science and Health, Part B, v. 45, n. 1, p. 89-94, 2010. Biblioteca(s): Embrapa Meio Ambiente. |
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149. | | CUNHA, J. P. A. R. da; BARIZON, R. R. M.; FERRACINI, V. L.; ASSALIN, M. R.; ANTUNIASSI, U. R. Spray drift and pest control from aerial applications on soybeans. Engenharia Agrícola, Jaboticabal, v. 37, n. 3, p. 493-501, 2017. Biblioteca(s): Embrapa Meio Ambiente. |
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152. | | COSCIONE, A. R.; SILVA, L. F. M.; De MARIA, I. C.; ANDRADE, C. A. de; FERRACINI, V. L. Solução do solo e análise de componentes principais para monitoramento da aplicação de lodo de esgoto. Revista Brasileira de Ciência do Solo, Viçosa, v. 38, n. 5, p. 1654-1662, 2014. Biblioteca(s): Embrapa Meio Ambiente. |
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153. | | PARAIBA, L. C.; KATAGUIRI, K.; CERDEIRA, A. L.; QUEIROZ, S. C. do N. de; FERRACINI, V. L. Sugarcane herbicide leaching risk evaluation in Guarany Aquifer. In: CONGRESSO BRASILEIRO DE ÁGUAS SUBTERRÂNEAS, 15.; ENCONTRO NACIONAL DE PERFURADORES DE POÇOS, 16., 2008, Natal. Anais... Natal: ABAS, 2008. 6p. CD-ROM. Biblioteca(s): Embrapa Meio Ambiente. |
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154. | | PARAIBA, L. C.; KATAGUIRI, K.; CERDEIRA, A. L.; QUEIROZ, S. C. do N. de; FERRACINI, V. L. Sugarcane herbicide leaching risk evaluation in Guarany Aquifer. In: CONGRESSO BRASILEIRO DE ÁGUAS SUBTERRÂNEAS, 15.; ENCONTRO NACIONAL DE PERFURADORES DE POÇOS, 16., 2008, Natal. Livro de resumos. Natal: ABAS, 2008. p.189. Biblioteca(s): Embrapa Meio Ambiente. |
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155. | | BOEIRA, R. C.; SOUZA, M. D. de; MAIA, A. de H. N.; FERRACINI, V. L.; GOMES, M. A. F. Procedimentos de avaliação de isotermas de adsorção de tebutiurom. In: CONGRESO VIRTUAL IBEROAMERICANO SOBRE GESTIÓN DE CALIDAD EN LABORATORIOS, 3., 2005, Madrid. Libro de comunicaciones: tomo I. Madrid: Ministério da Agricultura, Pesca y Alimentación, 2005. p. 181-184. Biblioteca(s): Embrapa Meio Ambiente. |
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156. | | BOEIRA, R. C.; SOUZA, M. D. de; MAIA, A. de H. N.; FERRACINI, V. L.; GOMES, M. A. F. Procedimentos de avaliação de isotermas de adsorção de tebutiurom. In: CONGRESO VIRTUAL IBEROAMERICANO SOBRE GESTIÓN DE CALIDAD EN LABORATORIOS, 3., 2005, Madrid. Libro de comunicaciones: tomo I. Madrid: Ministério da Agricultura, Pesca y Alimentación, 2005. Biblioteca(s): Embrapa Meio Ambiente. |
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157. | | GUERREIRO, C. P. V.; MARQUES, M. O. M.; FERRACINI, V. L.; QUEIROZ, S. C. do N. de; MING, L. C. Produção de B-ecdisona em Pfaffia glomerata (Spreng.) Pedersen em função da adubação orgânica em 6 épocas de crescimento. Revista Brasileira de Plantas Medicinais, Botucatu, v. 11, n. 4, p. 392-398, 2009. Biblioteca(s): Embrapa Meio Ambiente. |
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Registros recuperados : 256 | |
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Registro Completo
Biblioteca(s): |
Embrapa Meio Ambiente. |
Data corrente: |
08/01/2009 |
Data da última atualização: |
10/10/2016 |
Tipo da produção científica: |
Artigo em Anais de Congresso |
Autoria: |
PARAIBA, L. C.; KATAGUIRI, K.; CERDEIRA, A. L.; QUEIROZ, S. C. do N. de; FERRACINI, V. L. |
Afiliação: |
LOURIVAL COSTA PARAIBA, CNPMA; Karen Kataguiri, Estagiária-Embrapa Maio Ambiente; ANTONIO LUIZ CERDEIRA, CNPMA; SONIA CLAUDIA DO N DE QUEIROZ, CNPMA; VERA LUCIA FERRACINI, CNPMA. |
Título: |
Sugarcane herbicide leaching risk evaluation in Guarany Aquifer. |
Ano de publicação: |
2008 |
Fonte/Imprenta: |
In: CONGRESSO BRASILEIRO DE ÁGUAS SUBTERRÂNEAS, 15.; ENCONTRO NACIONAL DE PERFURADORES DE POÇOS, 16., 2008, Natal. Anais... Natal: ABAS, 2008. 6p. CD-ROM. |
Idioma: |
Português |
Conteúdo: |
he region of Ribeirão Preto, São Paulo State, Brazil, is located over recharge area of the Guarany aquifer, the most important source of groundwater in the South Central region of the country. This region is also the most important sugarcane producing area of the country which produces a large amount of the ethanol. This study was conducted to determine the potential risk of herbicide groundwater contamination. The leaching risk potential of herbicides to groundwater was conducted using the weather simulator ?Weather Generator? (WGEN) coupled with the model ?Chemical Movement Trough Layered Soils? (CMLS94). The following herbicides were evaluated in clayey and sandy soils (Typic Haplorthox and Typic Quartzipsamment soils) found in the region: ametryn (N-ethyl-N\'-(1- methylethyl)-6-(methylthio)-1,3,5-triazine-2,4-diamine), atrazine (6-chloro-N-ethyl-N\'-(1-methylethyl)-1,3,5-triazine- 2,4-diamine), clomazone (2-[(2-chlorophenyl)methyl]-4,4-dimethyl-3-isoxazolidinone), diuron (3,4-dichlorophenyl)- N,N-dimethylurea), halosulfuron (3-chloro-5-[(4,6-dimethoxy-2-pyrimidinyl)amino]carbonyl], hexazinone (3- cyclohexyl-6-(dimethylamino)-1-methyl-1,3,5-triazine-2,4 (1H,3H)-dione), imazapic ((±)-2-[4,5-dihydro-4-methyl-4- (1-methylethyl)-5-oxo-1H-imidazol-2-yl]-5-methyl-3-pyridinecarboxylic acid), imazapyr ((±)-2-[4,5-dihydro-4-methyl- 4-(1-methylethyl)-5-oxo-1H-imidazol-2-yl]-3-pyridinecarboxylic acid), MCPA (4-chloro-2-methylphenoxy)acetic acid), metribuzin (4-amino-6-(1,1-dimethylethyl)-3-(methylthio)-1,2,4-triazin-5(4H)-one), MSMA (Amonosodium salt of MAA), paraquat (1,1\'-dimethyl-4,4\'-bipyridinium ion), pendimethalin (N-(1-ethylpropyl)-3,4-dimethyl-2,6- dinitrobenzenamine), picloram (4-amino-3,5,6-trichloro-2-pyridinecarboxylic acid), simazine (6-chloro-N,N\'-diethyl- 1,3,5-triazine-2,4-diamine), sulfentrazone [N-[2,4-dichloro-5-[4-(difluoromethyl)-4,5-dihydro-3-methyl-5-oxo-1H- 1,2,4-triazol-1-yl]phenyl]methanesulfonamide], and tebuthiuron [N-[5-(1,1-dimethylethyl)-1,3,4-thiadiazol-2-yl]-N,N\'- dimethylurea]. Results obtained by our simulation study have shown that the herbicides picloram, tebuthiuron, and metribuzin have the highest leaching potential, in either sandy or clayey soils, with picloram reaching the root zone of sugarcane at 0.6m in less than 150 days. Menoshe region of Ribeirão Preto, São Paulo State, Brazil, is located over recharge area of the Guarany aquifer, the most important source of groundwater in the South Central region of the country. This region is also the most important sugarcane producing area of the country which produces a large amount of the ethanol. This study was conducted to determine the potential risk of herbicide groundwater contamination. The leaching risk potential of herbicides to groundwater was conducted using the weather simulator ?Weather Generator? (WGEN) coupled with the model ?Chemical Movement Trough Layered Soils? (CMLS94). The following herbicides were evaluated in clayey and sandy soils (Typic Haplorthox and Typic Quartzipsamment soils) found in the region: ametryn (N-ethyl-N\'-(1- methylethyl)-6-(methylthio)-1,3,5-triazine-2,4-diamine), atrazine (6-chloro-N-ethyl-N\'-(1-methylethyl)-1,3,5-triazine- 2,4-diamine), clomazone (2-[(2-chlorophenyl)methyl]-4,4-dimethyl-3-isoxazolidinone), diuron (3,4-dichlorophenyl)- N,N-dimethylurea), halosulfuron (3-chloro-5-[(4,6-dimethoxy-2-pyrimidinyl)amino]carbonyl], hexazinone (3- cyclohexyl-6-(dimethylamino)-1-methyl-1,3,5-triazine-2,4 (1H,3H)-dione), imazapic ((±)-2-[4,5-dihydro-4-methyl-4- (1-methylethyl)-5-oxo-1H-imidazol-2-yl]-5-methyl-3-pyridinecarboxylic acid), imazapyr ((±)-2-[4,5-dihydro-4-methyl- 4-(1-methylethyl)-5-oxo-1H-imidazol-2-yl]-3-pyridinecarboxylic acid), MCPA (4-chloro-2-methylphenoxy)acetic acid), metribuzin (4-amino-6-(1,1-dimethyle... Mostrar Tudo |
Palavras-Chave: |
Água subterrânea. |
Thesagro: |
Herbicida. |
Categoria do assunto: |
X Pesquisa, Tecnologia e Engenharia |
URL: |
https://ainfo.cnptia.embrapa.br/digital/bitstream/item/145701/1/2008AA-100.pdf
|
Marc: |
LEADER 02957nam a2200181 a 4500 001 1016122 005 2016-10-10 008 2008 bl uuuu u00u1 u #d 100 1 $aPARAIBA, L. C. 245 $aSugarcane herbicide leaching risk evaluation in Guarany Aquifer.$h[electronic resource] 260 $aIn: CONGRESSO BRASILEIRO DE ÁGUAS SUBTERRÂNEAS, 15.; ENCONTRO NACIONAL DE PERFURADORES DE POÇOS, 16., 2008, Natal. Anais... Natal: ABAS, 2008. 6p. CD-ROM.$c2008 520 $ahe region of Ribeirão Preto, São Paulo State, Brazil, is located over recharge area of the Guarany aquifer, the most important source of groundwater in the South Central region of the country. This region is also the most important sugarcane producing area of the country which produces a large amount of the ethanol. This study was conducted to determine the potential risk of herbicide groundwater contamination. The leaching risk potential of herbicides to groundwater was conducted using the weather simulator ?Weather Generator? (WGEN) coupled with the model ?Chemical Movement Trough Layered Soils? (CMLS94). The following herbicides were evaluated in clayey and sandy soils (Typic Haplorthox and Typic Quartzipsamment soils) found in the region: ametryn (N-ethyl-N\'-(1- methylethyl)-6-(methylthio)-1,3,5-triazine-2,4-diamine), atrazine (6-chloro-N-ethyl-N\'-(1-methylethyl)-1,3,5-triazine- 2,4-diamine), clomazone (2-[(2-chlorophenyl)methyl]-4,4-dimethyl-3-isoxazolidinone), diuron (3,4-dichlorophenyl)- N,N-dimethylurea), halosulfuron (3-chloro-5-[(4,6-dimethoxy-2-pyrimidinyl)amino]carbonyl], hexazinone (3- cyclohexyl-6-(dimethylamino)-1-methyl-1,3,5-triazine-2,4 (1H,3H)-dione), imazapic ((±)-2-[4,5-dihydro-4-methyl-4- (1-methylethyl)-5-oxo-1H-imidazol-2-yl]-5-methyl-3-pyridinecarboxylic acid), imazapyr ((±)-2-[4,5-dihydro-4-methyl- 4-(1-methylethyl)-5-oxo-1H-imidazol-2-yl]-3-pyridinecarboxylic acid), MCPA (4-chloro-2-methylphenoxy)acetic acid), metribuzin (4-amino-6-(1,1-dimethylethyl)-3-(methylthio)-1,2,4-triazin-5(4H)-one), MSMA (Amonosodium salt of MAA), paraquat (1,1\'-dimethyl-4,4\'-bipyridinium ion), pendimethalin (N-(1-ethylpropyl)-3,4-dimethyl-2,6- dinitrobenzenamine), picloram (4-amino-3,5,6-trichloro-2-pyridinecarboxylic acid), simazine (6-chloro-N,N\'-diethyl- 1,3,5-triazine-2,4-diamine), sulfentrazone [N-[2,4-dichloro-5-[4-(difluoromethyl)-4,5-dihydro-3-methyl-5-oxo-1H- 1,2,4-triazol-1-yl]phenyl]methanesulfonamide], and tebuthiuron [N-[5-(1,1-dimethylethyl)-1,3,4-thiadiazol-2-yl]-N,N\'- dimethylurea]. Results obtained by our simulation study have shown that the herbicides picloram, tebuthiuron, and metribuzin have the highest leaching potential, in either sandy or clayey soils, with picloram reaching the root zone of sugarcane at 0.6m in less than 150 days. 650 $aHerbicida 653 $aÁgua subterrânea 700 1 $aKATAGUIRI, K. 700 1 $aCERDEIRA, A. L. 700 1 $aQUEIROZ, S. C. do N. de 700 1 $aFERRACINI, V. L.
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