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| Registros recuperados : 27 | |
| 4. |  | LANCHOTE, V. L.; CERDEIRA, A. L.; MARQUES, M. P. C.; QUEIROZ, R. H. C.; GRECO, P. P. Avaliacao de residuos de 2,4-D e picloram em sedimentos do corrego Espraiado em Ribeirao Preto. In: JORNADA FARMACEUTICA DE RIBEIRAO PRETO, 14, 1994, Ribeirao Preto, SP. Anais de Farmacia e Quimica, Ribeirao Preto, v.33/4, p.112, 1993/4. Resumo. Ref.K-2. XIV Jornada Farmaceutica de Ribeirao Preto, 9-12 de outubro de 1994. Resumo K-2.| Biblioteca(s): Embrapa Meio Ambiente. |
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| 5. | | CERDEIRA, A. L.; SANTOS, N. A. G.; PESSOA, M. C. P. Y.; GOMES, M. A. F.; LANCHOTE, V. L. Herbicide leaching on a recharge área of Guarany Aquifer, Brazil. In: CONGRESSO BRASILEIRO DA CIÊNCIA DAS PLANTAS DANINHAS, 24., 2004, São Pedro. Anais... Londrina: SBCPD, 2004. 2p. Resumos Expandidos n. 105. 1 CD-ROM.| Biblioteca(s): Embrapa Meio Ambiente. |
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| 6. | | CERDEIRA, A. L.; SANTOS, N. A. G.; PESSOA, M. C. P. Y.; GOMES, M. A. F.; LANCHOTE, V. L. Herbicide leaching on a recharge area of the Guarany Aquifer in Brazil. Journal of Environmental Science and Health. Part B, Pesticides, Food Contaminants, and Agricultural Wastes, New York, v. B40, n. 1, p. 159-165, 2005.| Biblioteca(s): Embrapa Meio Ambiente. |
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| 7. | | 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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| 8. | | CERDEIRA, A. L.; COUTINHO, H. L. da C.; SANTOS, N. A. G.; PARAIBA, L. C.; LANCHOTE, V. L. Comportamento de triazinas na bacia do Alto Taquari, Mato Grosso do Sul, Brasil. In: CONGRESSO BRASILEIRO DA CIÊNCIA DAS PLANTAS DANINHAS, 24., 2004, São Pedro. Anais... Londrina: SBCPD, 2004. 2p. Resumos Expandidos n. 104. 1 CD-ROM.| Biblioteca(s): Embrapa Meio Ambiente. |
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| 9. | | CERDEIRA, A. L.; PESSOA, M. C. P. Y.; BONATO. P. S.; QUEIROZ, R. H. C.; LANCHOTE, V. L. Metodologia analítica de resíduo do herbicida 2,4-d (ácido 2,4-diclorofenoxiacético) em água em área de cana-de-açúcar. Pesticidas: Revista de Ecotoxicologia e Meio Ambiente, Curitiba, v. 12, p. 99-110, jan./dez. 2002.| Biblioteca(s): Embrapa Meio Ambiente. |
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| 10. | | CERDEIRA, A. L.; PESSOA, M. C. P. Y.; BONATO, P. S.; QUEIROZ, R. H. C.; LANCHOTE, V. L. Resíduos e lixiviação do herbicida picloram em água, em área de cana-de-açúcar. Revista Brasileira de Herbicidas, Brasília, DF, v. 3, n. 1, p. 75-81, 2002.| Biblioteca(s): Embrapa Meio Ambiente. |
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| 13. | | CERDEIRA, A. L.; SANTOS, N. A. G.; UETA, J.; SHUHAMA, I. K.; PESSOA, M. C. P. Y.; SMITH JUNIOR, S.; LANCHOTE, V. L. Atrazine in water and biodegradation in a recharge area of Guarany Aquifer in Brazil. Bulletin of Environmental Contamination and Toxicology, New York, v. 73, n. 1, p. 117-124, 2004.| Biblioteca(s): Embrapa Meio Ambiente. |
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| 14. | | CERDEIRA, A. L.; LANCHOTE, V. L.; QUEIROZ, R. C.; BONATO, P. S.; GOMES, M. A. F.; PESSOA, M. C. P. Y.; UETA, J. Herbicides residues in soil and water from sugarcane area in Brazil. In: INTERNATIONAL CONFERENCE ON SUSTAINABLE AGRICULTURE IN TROPICAL AND SUBTROPICAL HIGHLANDS WITH SPECIAL REFERENCE TO LATIN AMERICA, 1998, Rio de Janeiro. Abstracts. Rio de Janeiro: INT / EMBRAPA-CNPS / University of Karlsruhe, 1998. 7 p.| Biblioteca(s): Embrapa Meio Ambiente. |
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| 15. | | SANTOS, N. A. G.; LANCHOTE, V. L.; DREOSSI, S. A. C.; GOMES, M. A. F.; CERDEIRA, A. L.; CARVALHO, D.; BONATO, P. S. GC-MS determination of chlorotriazines in aqueous environmental samples. In: CONGRESS OF PHARMACEUTICAL SCIENCES, 1., 1997, Ribeirao Preto, SP. Bolletino Chimico Farmaceutico, v.136, p.131, 1997. Abstract.| Biblioteca(s): Embrapa Meio Ambiente. |
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| 16. | | DREOSSI, S. A. C.; LANCHOTE, V. L.; SANTOS, N. A. G.; CERDEIRA, A. L.; GOMES, M. A. F.; CARVALHO, D.; BONATO, P. S. GC-MS method for the determination of tebuthiuron in water. In: CONGRESS OF PHARMACEUTICAL SCIENCES, 1., 1997, Ribeirao Preto, SP. Bollettino Chimico Farmaceutico,v. 136, p.132, 1997. Abstract.| Biblioteca(s): Embrapa Meio Ambiente. |
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| 17. | | QUEIROZ, R. H. C.; LANCHOTE, V. L.; BONATO, P. S.; TOZZATO, E.; CARVALHO, D. de; GOMES, M. A.; CERDEIRA, A. L. Determination of ametryn herbicide by bioassay and gas chromatography-mass spectrometry in analysis of residues in drinking water. Bolletino Chimico Farmaceutico, v.138, n.5, p.251-254, 1999.| Biblioteca(s): Embrapa Meio Ambiente. |
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| 18. | | SANTOS, N. A. G.; BONATO, P. S.; DREOSSI, S. A. C.; GOMES, M. A. F.; CERDEIRA, A. L.; CARVALHO, D.; LANCHOTE, V. L. Multiresidue method for the analysis of herbicides in surface and groundwater. In: CONGRESS OF PHARMACEUTICAL SCIENCES, 1., 1997, Ribeirao Preto, SP. Bolletino Chimico Farmaceutico, v.136, p.133, 1997. Abstract.| Biblioteca(s): Embrapa Meio Ambiente. |
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| 19. | | SANTOS, A. C.; LANCHOTE, V. L.; BONATO, P. S.; QUEIROZ, R. H. C.; SANTOS, N. A. G.; CERDEIRA, A. L.; CARVALHO, D. Quantificação de resíduos do 2,4 D em amostras de água por cromatografia a gás. Revista Brasileira de Toxicologia, v.6, 1993. Suplemento. n.p.| Biblioteca(s): Embrapa Meio Ambiente. |
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| 20. | | SANTILI, M. B.; LANCHOTE, V. L.; BONATO, P. S.; SANTOS, A. C.; QUEIROZ, R. N. C.; CERDEIRA, A. L.; CARVALHO, D. Quantificação de resíduos de 2,4 D em amostras de água por cromatografia liquida de alta eficiencia. Revista Brasileira de Toxicologia, v.6, 1993. Suplemento. n.p.| Biblioteca(s): Embrapa Meio Ambiente. |
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| Registros recuperados : 27 | |
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Registro Completo
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Biblioteca(s): |
Embrapa Meio Ambiente. |
|
Data corrente: |
21/05/1998 |
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Data da última atualização: |
04/11/2015 |
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Autoria: |
SANTOS, N. A. G.; LANCHOTE, V. L.; DREOSSI, S. A. C.; GOMES, M. A. F.; CERDEIRA, A. L.; CARVALHO, D.; BONATO, P. S. |
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Afiliação: |
USP; USP; USP; MARCO ANTONIO FERREIRA GOMES, CNPMA; ANTONIO LUIZ CERDEIRA, CNPMA; USP; USP. |
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Título: |
GC-MS determination of chlorotriazines in aqueous environmental samples. |
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Ano de publicação: |
1997 |
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Fonte/Imprenta: |
In: CONGRESS OF PHARMACEUTICAL SCIENCES, 1., 1997, Ribeirao Preto, SP. Bolletino Chimico Farmaceutico, v.136, p.131, 1997. Abstract. |
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Idioma: |
Inglês |
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Conteúdo: |
The extensive use of chlorotriazines as selective herbicides in agriculture and their relatively high persistence imply that these compounds are now present in the environment, contaminating surface and groundwater. In European countries, United States and Canada, the drinking water ordinance demands a limited concentration of 0.5 ug/l for the sum of all pesticides and 0.1 ug/l with respect to each compound, with the consequent need for sensitive and selective analytical methods. Gas chromatography-mass spectrometry (GC-MS) is the most reliable technique for this kind of analysis and was employed in the present study to evaluate the contamination of aqueous environmental samples by atrazine, simazine and ametryne. Surface water samples (1 liter) were collected from the Espraido watershed (Ribeirao Preto, SP, Brazil) during the period from October 1995 to July 1996, at nine different points. Groundwater samples from sites near the river were collected during the same period. The extraction procedure consisted of the addition of 100 ml of water sample, previously filtered throw 0,22 um membranes, to a separatory funnel. After the addition of 25 ul of the internal standard solution (caffeine, 5 ug/ml) and akalinization with 25 ul of 4 M NaOH aqueous solution, the samples were extracted with 15 ml ethyl acetate by shaking for 1 hour. Volumes of 5 ml of the organic phase were transferred to conic tubes and evaporated to dryness under a nitrogen flow, at the temperature of 35oC. The residues were dissolved in 25 ul acetone and 2 ul were chromatographed on a DB-5 column (J&W Scientific, 0.25 mmx30m, film of 0,25 um) using a GC-MS QP5000 Shimadzu apparatus. Helium was used as carrier gas. The operation conditions were: injector temperature 240oC; oven temperature program - start at 60oC for 1 min, increase to 150oC at a rate of 20oC/min and then to 280oC at a rate of 10oC/min; detector temperature of 230oC in the ion source of the MS. Under the chromatographic conditions selected and by extracting 100 ml of water samples, the quantification limit was estimated to be 0.02 ug/l for each triazine herbicide. The results showed traces of ametryne in surface water samples collected in December, whereas the ground water samples used for human consumption did not show contamination. The other herbicides were not detected in the samples analyzed under the condition employed. MenosThe extensive use of chlorotriazines as selective herbicides in agriculture and their relatively high persistence imply that these compounds are now present in the environment, contaminating surface and groundwater. In European countries, United States and Canada, the drinking water ordinance demands a limited concentration of 0.5 ug/l for the sum of all pesticides and 0.1 ug/l with respect to each compound, with the consequent need for sensitive and selective analytical methods. Gas chromatography-mass spectrometry (GC-MS) is the most reliable technique for this kind of analysis and was employed in the present study to evaluate the contamination of aqueous environmental samples by atrazine, simazine and ametryne. Surface water samples (1 liter) were collected from the Espraido watershed (Ribeirao Preto, SP, Brazil) during the period from October 1995 to July 1996, at nine different points. Groundwater samples from sites near the river were collected during the same period. The extraction procedure consisted of the addition of 100 ml of water sample, previously filtered throw 0,22 um membranes, to a separatory funnel. After the addition of 25 ul of the internal standard solution (caffeine, 5 ug/ml) and akalinization with 25 ul of 4 M NaOH aqueous solution, the samples were extracted with 15 ml ethyl acetate by shaking for 1 hour. Volumes of 5 ml of the organic phase were transferred to conic tubes and evaporated to dryness under a nitrogen flow, at the temperature of 35oC. T... Mostrar Tudo |
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Palavras-Chave: |
Chlorotriazines; GC-MS. |
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Categoria do assunto: |
W Química e Física |
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URL: |
https://ainfo.cnptia.embrapa.br/digital/bitstream/item/87147/1/1997RAs-006.PDF
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|
Marc: |
LEADER 03082nam a2200205 a 4500
001 1012896
005 2015-11-04
008 1997 bl uuuu u00u1 u #d
100 1 $aSANTOS, N. A. G.
245 $aGC-MS determination of chlorotriazines in aqueous environmental samples.$h[electronic resource]
260 $aIn: CONGRESS OF PHARMACEUTICAL SCIENCES, 1., 1997, Ribeirao Preto, SP. Bolletino Chimico Farmaceutico, v.136, p.131, 1997. Abstract.$c1997
520 $aThe extensive use of chlorotriazines as selective herbicides in agriculture and their relatively high persistence imply that these compounds are now present in the environment, contaminating surface and groundwater. In European countries, United States and Canada, the drinking water ordinance demands a limited concentration of 0.5 ug/l for the sum of all pesticides and 0.1 ug/l with respect to each compound, with the consequent need for sensitive and selective analytical methods. Gas chromatography-mass spectrometry (GC-MS) is the most reliable technique for this kind of analysis and was employed in the present study to evaluate the contamination of aqueous environmental samples by atrazine, simazine and ametryne. Surface water samples (1 liter) were collected from the Espraido watershed (Ribeirao Preto, SP, Brazil) during the period from October 1995 to July 1996, at nine different points. Groundwater samples from sites near the river were collected during the same period. The extraction procedure consisted of the addition of 100 ml of water sample, previously filtered throw 0,22 um membranes, to a separatory funnel. After the addition of 25 ul of the internal standard solution (caffeine, 5 ug/ml) and akalinization with 25 ul of 4 M NaOH aqueous solution, the samples were extracted with 15 ml ethyl acetate by shaking for 1 hour. Volumes of 5 ml of the organic phase were transferred to conic tubes and evaporated to dryness under a nitrogen flow, at the temperature of 35oC. The residues were dissolved in 25 ul acetone and 2 ul were chromatographed on a DB-5 column (J&W Scientific, 0.25 mmx30m, film of 0,25 um) using a GC-MS QP5000 Shimadzu apparatus. Helium was used as carrier gas. The operation conditions were: injector temperature 240oC; oven temperature program - start at 60oC for 1 min, increase to 150oC at a rate of 20oC/min and then to 280oC at a rate of 10oC/min; detector temperature of 230oC in the ion source of the MS. Under the chromatographic conditions selected and by extracting 100 ml of water samples, the quantification limit was estimated to be 0.02 ug/l for each triazine herbicide. The results showed traces of ametryne in surface water samples collected in December, whereas the ground water samples used for human consumption did not show contamination. The other herbicides were not detected in the samples analyzed under the condition employed.
653 $aChlorotriazines
653 $aGC-MS
700 1 $aLANCHOTE, V. L.
700 1 $aDREOSSI, S. A. C.
700 1 $aGOMES, M. A. F.
700 1 $aCERDEIRA, A. L.
700 1 $aCARVALHO, D.
700 1 $aBONATO, P. S.
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