Glyphosate as an acetylcholinesterase inhibitor in cnesterodon decemmaculatus

The toxic effect of sublethal concentrations (1, 17.5 and 35 mg L -1) of pure glyphosate was evaluated on acetylcholinesterase (AChE) activity in the fish species, Cnesterodon decemmaculatus. Acute bioassays (96 h) under laboratory conditions were conducted and homogenates for each specimen correspo...

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Autor principal: Menéndez-Helman, R.J
Otros Autores: Ferreyroa, G.V, Dos Santos Afonso, M., Salibián, A.
Formato: Capítulo de libro
Lenguaje:Inglés
Publicado: 2012
Acceso en línea:Registro en Scopus
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Registro en la Biblioteca Digital
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024 7 |2 scopus  |a 2-s2.0-84856624315 
024 7 |2 cas  |a acetylcholinesterase, 9000-81-1; glycine, 56-40-6, 6000-43-7, 6000-44-8; glyphosate, 1071-83-6; Acetylcholinesterase, 3.1.1.7; Cholinesterase Inhibitors; Glycine, 56-40-6; Water Pollutants, Chemical; glyphosate, 1071-83-6 
040 |a Scopus  |b spa  |c AR-BaUEN  |d AR-BaUEN 
030 |a BECTA 
100 1 |a Menéndez-Helman, R.J. 
245 1 0 |a Glyphosate as an acetylcholinesterase inhibitor in cnesterodon decemmaculatus 
260 |c 2012 
270 1 0 |m Dos Santos Afonso, M.; INQUIMAE, Facultad de Ciencias Exactas y Naturales, Universidad de Buenos Aires, Ciudad Universitaria-Pabellón 2, C1428EHA Buenos Aires, Argentina; email: dosantos@qi.fcen.uba.ar 
506 |2 openaire  |e Política editorial 
504 |a Behra, M., Cousin, X., Bertrand, C., Vonesch, J.-L., Biellmann, D., Chatonnet, A., Strahle, U., Acetylcholinesterase is required for neuronal and muscular development in the zebrafish embryo (2002) Nature Neuroscience, 5 (2), pp. 111-118. , DOI 10.1038/nn788 
504 |a Carriquiriborde, P., Toxicidad de Glifosato en peces autóctonos. Estudios de laboratorio y campo (2010) Taller de Aspectos Ambientales Del Uso de Glifosato, pp. 57-68. , V. Aparicio M. Camino (eds). INTA-EEBalcarce Argentina 
504 |a Ellman, G.L., Courtney, K.D., Andres Jr., V., Featherstone, R.M., A new and rapid colorimetric determination of acetylcholinesterase activity (1961) Biochem Pharmacol, 7, pp. 88-95. , 10.1016/0006-2952(61)90145-9 1:CAS:528:DyaF3MXht1Gns7o%3D 
504 |a Ferrari, L., García, M.E., De La Torre, F.R., Demichelis, S.O., Evaluación ecotoxicológica del agua de un río urbano mediante bioensayos con especies nativas (1998) Museo Argentino Ciencias Naturales B Rivadavia, Nueva Serie, 148, pp. 1-16 
504 |a Giesy, J.P., Dobson, S., Solomon, K.R., Ecotoxicological risk assessment for Roundup ® herbicide. Rev (2000) Environ Contam Toxicol, 167, pp. 35-120. , 10.1007/978-1-4612-1156-3-2 1:CAS:528:DC%2BD3cXntVyls74%3D 
504 |a Glusczak, L., Miron, D.D.S., Moraes, B.S., Simoes, R.R., Schetinger, M.R.C., Morsch, V.M., Loro, V.L., Acute effects of glyphosate herbicide on metabolic and enzymatic parameters of silver catfish (Rhamdia quelen) (2007) Comparative Biochemistry and Physiology - C Toxicology and Pharmacology, 146 (4), pp. 519-524. , DOI 10.1016/j.cbpc.2007.06.004, PII S1532045607001470 
504 |a Lowry, O.H., Rosebrough, N.J., Farr, A.L., Randall, R.J., Protein measurements with Folin phenol reagent (1951) J Biol Chem, 193, pp. 265-275. , 1:CAS:528:DyaG38XhsVyrsw%3D%3D 
504 |a Modesto, K.A., Martinez, C.B.R., Effects of Roundup Transorb on fish: Hematology, antioxidant defenses and acetylcholinesterase activity (2010) Chemosphere, 81, pp. 781-787. , 10.1016/j.chemosphere.2010.07.005 1:CAS:528:DC%2BC3cXht1Cmu7vJ 
504 |a Nunes, B., Carvalho, F., Guilhermino, L., Characterization and use of the total head soluble cholinesterases from mosquitofish (Gambusia holbrooki) for screening of anticholinesterase activity (2005) Journal of Enzyme Inhibition and Medicinal Chemistry, 20 (4), pp. 369-376. , DOI 10.1080/14756360500094094 
504 |a Pérez, G.L., Solange Vera, M., Miranda, L.A., Effects of herbicide glyphosate and glyphosate-based formulations on aquatic ecosystems (2011) Herbicides and Environment, pp. 343-368. , A. Kortekamp (eds). InTech Argentina 
504 |a Peruzzo, P.J., Porta, A.A., Ronco, A.E., Levels of glyphosate in surface waters, sediments and soils associated with direct sowing soybean cultivation in North pampasic region of Argentina (2008) Environ Pollut, 156, pp. 61-66. , 10.1016/j.envpol.2008.01.015 1:CAS:528:DC%2BD1cXhtV2jsLbI 
504 |a Thompson, H.M., Esterases as markers of exposure to organophosphates and carbamates (1999) Ecotoxicology, 8 (5), pp. 369-384. , DOI 10.1023/A:1008934505370 
504 |a Tierney, K., Casselman, M., Takeda, S., Farrell, T., Kennedy, C., The relationship between cholinesterase inhibition and two types of swimming performance in chlorpyrifos-exposed coho salmon (Oncorhynchus kisutch) (2007) Environmental Toxicology and Chemistry, 26 (5), pp. 998-1004. , DOI 10.1897/06-459R.1 
504 |a (1993) Method for Measuring the Acute Toxicity of Effluents and Receiving to Freshwater and Marine Organism, , USEPA (US Environmental Protection Agency) (4th edn). EPA/600/4-90/027F 
504 |a Varó, I., Amat, F., Navarro, J.C., Acute toxicity of dichlorvos to Aphanius iberus (Cuvier & Valenciennes, 1846) and its anti-cholinesterase effects on this species (2008) Aquat Toxicol, 88, pp. 53-61. , 10.1016/j.aquatox.2008.03.004 
504 |a (1994) Glyphosate. Environmental Health Criteria 159, , WHO (World Health Organization) Geneva 
504 |a Zhu, Y., Zhang, F., Tong, C., Liu, W., Determination of glyphosate by ion chromatography (1999) Journal of Chromatography A, 850 (1-2), pp. 297-301. , DOI 10.1016/S0021-9673(99)00558-0, PII S0021967399005580 
520 3 |a The toxic effect of sublethal concentrations (1, 17.5 and 35 mg L -1) of pure glyphosate was evaluated on acetylcholinesterase (AChE) activity in the fish species, Cnesterodon decemmaculatus. Acute bioassays (96 h) under laboratory conditions were conducted and homogenates for each specimen corresponding to the anterior, middle and posterior body sections were performed. Fish survival was 100%, even at the highest concentration tested (35 mg L -1), in accordance with the low lethal toxicity reported for glyphosate. However, a significant inhibitory effect on AChE activity was recorded even for the lowest herbicide concentration tested (1 mg L -1), in the homogenates corresponding to the anterior body section. The inhibition ranged from 23 to 36%. The analytical determination of glyphosate in assay media by ion chromatography, was used to verify its stability. These results indicate that AChE-a neurotoxicity biomarker-in C. decemmaculatus may be affected by exposure to environmentally relevant concentrations of glyphosate. © 2011 Springer Science+Business Media, LLC.  |l eng 
593 |a INQUIMAE, Facultad de Ciencias Exactas y Naturales, Universidad de Buenos Aires, Ciudad Universitaria-Pabellón 2, C1428EHA Buenos Aires, Argentina 
593 |a PRODEA-INEDES, Universidad Nacional de Luján, Luján B6700ZBA, Argentina 
593 |a Academia Nacional de Farmacia y Bioquímica, Buenos Aires, Argentina 
690 1 0 |a ACHE 
690 1 0 |a CNESTERODON DECEMMACULATUS 
690 1 0 |a GLYPHOSATE 
690 1 0 |a TOXICITY BIOASSAY 
690 1 0 |a ACETYLCHOLINESTERASE 
690 1 0 |a ACHE 
690 1 0 |a ANALYTICAL DETERMINATION 
690 1 0 |a CNESTERODON DECEMMACULATUS 
690 1 0 |a FISH SPECIES 
690 1 0 |a FISH SURVIVAL 
690 1 0 |a GLYPHOSATE 
690 1 0 |a GLYPHOSATES 
690 1 0 |a HERBICIDE CONCENTRATION 
690 1 0 |a INHIBITORY EFFECT 
690 1 0 |a LABORATORY CONDITIONS 
690 1 0 |a NEUROTOXICITY 
690 1 0 |a TOXIC EFFECT 
690 1 0 |a BIOASSAY 
690 1 0 |a TOXICITY 
690 1 0 |a HERBICIDES 
690 1 0 |a ACETYLCHOLINESTERASE 
690 1 0 |a CHOLINESTERASE INHIBITOR 
690 1 0 |a DRUG DERIVATIVE 
690 1 0 |a GLYCINE 
690 1 0 |a GLYPHOSATE 
690 1 0 |a ANIMAL 
690 1 0 |a ARTICLE 
690 1 0 |a CYPRINODONTIFORMES 
690 1 0 |a DOSE RESPONSE 
690 1 0 |a METABOLISM 
690 1 0 |a PHYSIOLOGY 
690 1 0 |a WATER POLLUTANT 
690 1 0 |a ACETYLCHOLINESTERASE 
690 1 0 |a ANIMALS 
690 1 0 |a CHOLINESTERASE INHIBITORS 
690 1 0 |a CYPRINODONTIFORMES 
690 1 0 |a DOSE-RESPONSE RELATIONSHIP, DRUG 
690 1 0 |a GLYCINE 
690 1 0 |a WATER POLLUTANTS, CHEMICAL 
690 1 0 |a CNESTERODON DECEMMACULATUS 
700 1 |a Ferreyroa, G.V. 
700 1 |a Dos Santos Afonso, M. 
700 1 |a Salibián, A. 
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