Comparative toxicity of two glyphosate-based formulations to Eisenia andrei under laboratory conditions
Glyphosate-based products are the leading post-emergent agricultural herbicides in the world, particularly in association with glyphosate tolerant crops. However, studies on the effects of glyphosate-based formulations on terrestrial receptors are scarce. This study was conducted to evaluate the com...
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2013
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| LEADER | 12240caa a22014057a 4500 | ||
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| 001 | PAPER-11659 | ||
| 003 | AR-BaUEN | ||
| 005 | 20230518204149.0 | ||
| 008 | 190411s2013 xx ||||fo|||| 00| 0 eng|d | ||
| 024 | 7 | |2 scopus |a 2-s2.0-84875050352 | |
| 024 | 7 | |2 cas |a glyphosate, 1071-83-6; Glycine, 56-40-6; Herbicides; Soil Pollutants; glyphosate, 1071-83-6 | |
| 040 | |a Scopus |b spa |c AR-BaUEN |d AR-BaUEN | ||
| 030 | |a CMSHA | ||
| 100 | 1 | |a Piola, L. | |
| 245 | 1 | 0 | |a Comparative toxicity of two glyphosate-based formulations to Eisenia andrei under laboratory conditions |
| 260 | |c 2013 | ||
| 270 | 1 | 0 | |m Casabé, N.; Toxicology and Legal Chemistry, Department of Biological Chemistry, Faculty of Exact and Natural Sciences, University of Buenos Aires, Pabellón 2, 4o piso, Ciudad Universitaria, 1428 Buenos Aires, Argentina; email: nbcm@qb.fcen.uba.ar |
| 506 | |2 openaire |e Política editorial | ||
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| 504 | |a Casabé, N., Piola, L., Fuchs, J., Oneto, M.L., Pamparato, L., Basack, S., Giménez, R., Kesten, E., Ecotoxicological assessment of the effects of glyphosate and chlorpyrifos in an argentine soya field (2007) J. Soils Sediments, 7, pp. 232-239 | ||
| 504 | |a (2011), http://www.casafe.org/estadisticas.php, Casafe. Cámara de sanidad agropecuaria y fertilizantes; Correia, F.V., Moreira, J.C., Effects of glyphosate and 2,4-D on earthworms (Eisenia foetida) in laboratory tests (2010) Bull. Environ. Contam. Toxicol., 85, pp. 264-268 | ||
| 504 | |a Domingues, I.S., Agra, A.R., Monaghan, K., Soares, A.M.V.M., Nogueira, A.J.A., Cholinesterase and glutathione-S-transferase activities in freshwater invertebrates as biomarkers to assess pesticide contamination (2010) Environ. Toxicol. Chem., 29, pp. 5-18 | ||
| 504 | |a (2009), Environment Agency,. Standard Operating Procedures for Bioassays in Ecological Risk Assessment. Science report - SC070009. Environment Agency, Bristol; Fuchs, J., Piola, L., Prieto González, E., Oneto, M.L., Basack, S., Kesten, E., Casabé, N., Coelomocyte biomarkers in the earthworm Eisenia fetida exposed to 2,4,6-trinitrotoluene (TNT) (2011) Environ. Monit. Assess., 175, pp. 127-137 | ||
| 504 | |a Hwang, H.M., Wade, T.L., Sericano, J.L., Destabilized lysosomes and elimination of polycyclic aromatic hydrocarbons and polychlorinated biphenyls in eastern oysters (Crassostrea virginica) (2004) Environ. Toxicol. Chem., 23, pp. 1991-1995 | ||
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| 504 | |a Lajmanovich, R., Attademo, A., Peltzer, P., Junges, C., Cabagna, M., Toxicity of four herbicide formulations with glyphosate on Rhinella arenarum (Anura: Bufonidae) tadpoles: B-esterases and glutathione-S-transferase inhibitors (2011) Arch. Environ. Contam. Toxicol., 60, pp. 681-689 | ||
| 504 | |a Lamb, D.C., Kelly, D.E., Hanley, S.Z., Mehmood, Z., Kelly, S.L., Glyphosate is an inhibitor of plant cytochrome P450: functional expression of Thlaspi arvensae cytochrome P45071B1/reductase fusion protein in Escherichia coli (1998) Biochem. Biophys. Res. Commun., 244, pp. 110-114 | ||
| 504 | |a Monteiro, D., Cavalcante, D.G., Viléla, M.V., Sofia, S.H., Martinez, C.B.R., In vivo and in vitro exposures for the evaluation of the genotoxic effects of lead on the Neotropical freshwater fish Prochilodus lineatus (2011) Aquat. Toxicol., 104, pp. 291-298 | ||
| 504 | |a Muangphra, P., Kwankua, W., Gooneratne, R., Genotoxic effects of glyphosate or paraquat on earthworm coelomocytes. Environ. Toxicol. (2012), 13. doi: 10.1002/tox.21787. (Article first published online: 30 May 2012); (1984) Guideline for Testing of Chemicals No. 207. Earthworm Acute Toxicity Tests, , OECD. Organization for Economic Cooperation and Development, Paris, France | ||
| 504 | |a Pereira, J.L., Antunes, S.C., Castro, B.B., Marques, C.R., Gonçalves, A.M.M., Gonçalves, F., Pereira, R., Toxicity evaluation of three pesticides on non-target aquatic and soil organisms: commercial formulation versus active ingredient (2009) Ecotoxicology, 18, pp. 455-463 | ||
| 504 | |a Reinecke, S., Reinecke, A., The comet assay as biomarker of heavy metal genotoxicity in earthworms (2004) Arch. Environ. Contam. Toxicol., 46, pp. 208-215 | ||
| 504 | |a Roberts, B.L., Dorough, H.W., Relative toxicities of chemicals to the earthworm Eisenia foetida (1984) Environ. Toxicol. Chem., 3, pp. 67-68 | ||
| 504 | |a Robidoux, P.Y., Svendsen, C., Sarrazin, M., Hawari, J., Thiboutot, S., Ampleman, G., Weeks, J.M., Sunahara, G.I., Evaluation of tissue and cellular biomarkers to assess 2,4,6-trinitrotoluene (TNT) exposure in earthworms: effects-based assessment in laboratory studies using Eisenia andrei (2002) Biomarkers, 7, pp. 306-321 | ||
| 504 | |a Römbke, J., Heimbach, F., Hoy, S., Kula, C., Scott-Fordsmand, J., Sousa, J.P., Stephenson, G., Weeks, J., (2003) Effects of Plant Protection Products on Functional Endpoints in Soil (EPFES), p. 109. , SETAC Press, Pensacola, USA | ||
| 504 | |a Sánchez-Hernández, J.C., Earthworm biomarkers in ecological risk assessment (2006) Rev. Environ. Contam. Toxicol., 188, pp. 85-126 | ||
| 504 | |a Santos, M.J., Morgado, R., Ferreira, N.G., Soares, A.M., Loureiro, S., Evaluation of the joint effect of glyphosate and dimethoate using a small-scale terrestrial ecosystem (2011) Ecotoxicol. Environ. Saf., 74, pp. 1994-2001 | ||
| 504 | |a Scott-Fordsmand, J.J., Weeks, J.M., Biomarkers in earthworms (2000) Rev. Environ. Contam. Toxicol., 165, pp. 117-159 | ||
| 504 | |a , p. 336. , http://www.fs.fed.us/foresthealth/pesticide/pdfs/Glyphosate_SERA_TR-052-22-03b.pdf, USDA/FS, 2011. United States Department of Agriculture/Forest service. Glyphosate - human health and ecological risk assessment (SERA TR-052-22-03b). Final report, March 2011; Wang, Y., Wu, S., Chen, L., Wu, C., Yu, R., Wang, Q., Zhao, X., Toxicity assessment of 45 pesticides to the epigeic earthworm Eisenia fetida (2012) Chemosphere, 88, pp. 484-491 | ||
| 504 | |a Weeks, J., Svendsen, C., Neutral red retention by lysosomes from earthworm (Lumbricus rubellus) coelomocytes: a simple biomarker of exposure to soil copper (1996) Environ. Toxicol. Chem., 15, pp. 1801-1805 | ||
| 504 | |a (1994) Environmental Health Criteria 159 (Glyphosate), , WHO. World Health Organization, Geneva | ||
| 504 | |a Xiao, N.W., Song, Y., Ge, F., Liu, X.H., Ou-Yang, Z.Y., Biomarker responses of the earthworm Eisenia fetida to acetochlor exposure in OECD soil (2006) Chemosphere, 65, pp. 907-912 | ||
| 504 | |a Yasmin, S., D'Souza, D., Effect of pesticides on the reproductive output of Eisenia fetida (2007) Bull. Environ. Contam. Toxicol., 79, pp. 529-532 | ||
| 520 | 3 | |a Glyphosate-based products are the leading post-emergent agricultural herbicides in the world, particularly in association with glyphosate tolerant crops. However, studies on the effects of glyphosate-based formulations on terrestrial receptors are scarce. This study was conducted to evaluate the comparative toxicity of two glyphosate-based products: Roundup FG (monoammonium salt, 72% acid equivalent, glyphosate-A) and Mon 8750 (monoammonium salt, 85.4% acid equivalent, glyphosate-B), towards the earthworm Eisenia andrei. Median lethal concentration (LC50) showed that glyphosate-A was 4.5-fold more toxic than glyphosate-B. Sublethal concentrations caused a concentration-dependent weight loss, consistent with the reported effect of glyphosate as uncoupler of oxidative phosphorylation. Glyphosate-A showed deleterious effects on DNA and lysosomal damage at concentrations close to the applied environmental concentrations (14.4μg ae cm-2). With glyphosate-B toxic effects were observed at higher doses, close to its LC50, suggesting that the higher toxicity of formulate A could be attributed to the effects of some of the so-called "inert ingredients", either due to a direct intrinsic toxicity, or to an enhancement in the bioavailability and/or bioaccumulation of the active ingredient. Our results highlight the importance of ecotoxicological assessment not only of the active ingredients, but also of the different formulations usually employed in agricultural practices. © 2012 Elsevier Ltd. |l eng | |
| 536 | |a Detalles de la financiación: Universidad de Buenos Aires | ||
| 536 | |a Detalles de la financiación: Consejo Nacional de Investigaciones Científicas y Técnicas | ||
| 536 | |a Detalles de la financiación: This research was supported by the University of Buenos Aires and the CONICET. | ||
| 593 | |a Toxicology and Legal Chemistry, Department of Biological Chemistry, Faculty of Exact and Natural Sciences, University of Buenos Aires, Pabellón 2, 4o piso, Ciudad Universitaria, 1428 Buenos Aires, Argentina | ||
| 593 | |a IQUIBICEN-UBA/CONICET, Department of Biological Chemistry, FCEN, UBA, Pabellón 2, 4o piso, Ciudad Universitaria, Argentina | ||
| 690 | 1 | 0 | |a COMET ASSAY |
| 690 | 1 | 0 | |a EISENIA ANDREI |
| 690 | 1 | 0 | |a GLYPHOSATE FORMULATIONS |
| 690 | 1 | 0 | |a NEUTRAL RED RETENTION TIME |
| 690 | 1 | 0 | |a SUBLETHAL BIOMARKERS |
| 690 | 1 | 0 | |a COMET ASSAYS |
| 690 | 1 | 0 | |a ECOTOXICOLOGICAL ASSESSMENT |
| 690 | 1 | 0 | |a EISENIA ANDREI |
| 690 | 1 | 0 | |a ENVIRONMENTAL CONCENTRATION |
| 690 | 1 | 0 | |a GLYPHOSATES |
| 690 | 1 | 0 | |a MEDIAN LETHAL CONCENTRATION |
| 690 | 1 | 0 | |a OXIDATIVE PHOSPHORYLATION |
| 690 | 1 | 0 | |a RETENTION TIME |
| 690 | 1 | 0 | |a AGRICULTURE |
| 690 | 1 | 0 | |a BIOCHEMISTRY |
| 690 | 1 | 0 | |a TOXICITY |
| 690 | 1 | 0 | |a HERBICIDES |
| 690 | 1 | 0 | |a AMMONIUM DERIVATIVE |
| 690 | 1 | 0 | |a GLYPHOSATE |
| 690 | 1 | 0 | |a AGRICULTURAL PRACTICE |
| 690 | 1 | 0 | |a BIOAVAILABILITY |
| 690 | 1 | 0 | |a BIOMARKER |
| 690 | 1 | 0 | |a COMPARATIVE STUDY |
| 690 | 1 | 0 | |a CONCENTRATION (COMPOSITION) |
| 690 | 1 | 0 | |a DOSE-RESPONSE RELATIONSHIP |
| 690 | 1 | 0 | |a EARTHWORM |
| 690 | 1 | 0 | |a ECOTOXICOLOGY |
| 690 | 1 | 0 | |a GLYPHOSATE |
| 690 | 1 | 0 | |a LABORATORY METHOD |
| 690 | 1 | 0 | |a POLLUTION EFFECT |
| 690 | 1 | 0 | |a TOXICITY TEST |
| 690 | 1 | 0 | |a WEIGHT |
| 690 | 1 | 0 | |a ARTICLE |
| 690 | 1 | 0 | |a BIOACCUMULATION |
| 690 | 1 | 0 | |a BIOAVAILABILITY |
| 690 | 1 | 0 | |a CELL DAMAGE |
| 690 | 1 | 0 | |a COMET ASSAY |
| 690 | 1 | 0 | |a COMPARATIVE STUDY |
| 690 | 1 | 0 | |a CONTROLLED STUDY |
| 690 | 1 | 0 | |a DNA DAMAGE |
| 690 | 1 | 0 | |a EARTHWORM |
| 690 | 1 | 0 | |a EISENIA ANDREI |
| 690 | 1 | 0 | |a GROWTH |
| 690 | 1 | 0 | |a LC 50 |
| 690 | 1 | 0 | |a LYSOSOME |
| 690 | 1 | 0 | |a NONHUMAN |
| 690 | 1 | 0 | |a OXIDATIVE PHOSPHORYLATION |
| 690 | 1 | 0 | |a TOXICITY |
| 690 | 1 | 0 | |a WEIGHT REDUCTION |
| 690 | 1 | 0 | |a ANIMALS |
| 690 | 1 | 0 | |a GLYCINE |
| 690 | 1 | 0 | |a HERBICIDES |
| 690 | 1 | 0 | |a LABORATORIES |
| 690 | 1 | 0 | |a LETHAL DOSE 50 |
| 690 | 1 | 0 | |a OLIGOCHAETA |
| 690 | 1 | 0 | |a RISK ASSESSMENT |
| 690 | 1 | 0 | |a SOIL POLLUTANTS |
| 690 | 1 | 0 | |a EISENIA ANDREI |
| 700 | 1 | |a Fuchs, J. | |
| 700 | 1 | |a Oneto, M.L. | |
| 700 | 1 | |a Basack, S. | |
| 700 | 1 | |a Kesten, E. | |
| 700 | 1 | |a Casabé, N. | |
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