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Resumen
Glyphosate (GLY) and AMPA concentrations were determined in sandy soil profiles, during pre- and post-application events in two agricultural soybean fields (S1 and S2). Streamwater and sediment samples were also analyzed. Post-application sampling was carried out one month later from the event. Concentrations of GLY + AMPA in surface soils (0–5 cm depth) during pre-application period showed values 20-fold higher (0.093–0.163 μg/g d.w.) than control area [ver mas...]
dc.contributor.authorLupi, Leonardo
dc.contributor.authorMiglioranza, Karina Silvia Beatriz
dc.contributor.authorAparicio, Virginia Carolina
dc.contributor.authorMarino, Damian Jose Gabriel
dc.contributor.authorBedmar, Francisco
dc.contributor.authorWunderlin, Daniel Alberto
dc.date.accessioned2018-12-04T15:26:59Z
dc.date.available2018-12-04T15:26:59Z
dc.date.issued2015-12-01
dc.identifier.issn0048-9697
dc.identifier.issn1879-1026
dc.identifier.otherhttps://doi.org/10.1016/j.scitotenv.2015.07.090
dc.identifier.urihttps://www.sciencedirect.com/science/article/pii/S0048969715304320
dc.identifier.urihttp://hdl.handle.net/20.500.12123/4013
dc.description.abstractGlyphosate (GLY) and AMPA concentrations were determined in sandy soil profiles, during pre- and post-application events in two agricultural soybean fields (S1 and S2). Streamwater and sediment samples were also analyzed. Post-application sampling was carried out one month later from the event. Concentrations of GLY + AMPA in surface soils (0–5 cm depth) during pre-application period showed values 20-fold higher (0.093–0.163 μg/g d.w.) than control area (0.005 μg/g d.w.). After application event soils showed markedly higher pesticide concentrations. A predominance of AMPA (80%) was observed in S1 (early application), while 34% in S2 for surface soils. GLY + AMPA concentrations decreased with depth and correlated strongly with organic carbon (r between 0.74 and 0.88, p < 0.05) and pH (r between − 0.81 and − 0.76, p < 0.001). The slight enrichment of pesticides observed from 25 cm depth to deeper layer, in addition to the alkaline pH along the profile, is of high concern about groundwater contamination. Sediments from pre-application period showed relatively lower pesticide levels (0.0053–0.0263 μg/g d.w.) than surface soil with a predominance of glyphosate, indicating a limited degradation. Levels of contaminants (mainly AMPA) in streamwater (ND-0.5 ng/mL) denote the low persistence of these compounds. However, a direct relationship in AMPA concentration was observed between sediment and streamwater. Despite the known relatively short half-life of glyphosate in soils, GLY + AMPA occurrence is registered in almost all matrices at different sampling times (pre- and post-application events). The physicochemical characteristics (organic carbon, texture, pH) and structure of soils and sediment in addition to the time elapsed from application determined the behavior of these contaminants in the environment. As a whole, the results warn us about vertical transport trough soil profile with the possibility of reaching groundwater.eng
dc.formatapplication/pdfes_AR
dc.language.isoenges_AR
dc.publisherElsevieres_AR
dc.rightsinfo:eu-repo/semantics/restrictedAccesses_AR
dc.sourceScience of The Total Environment 536 : 687-694 (December 2015)es_AR
dc.subjectGlifosatoes_AR
dc.subjectGlyphosateeng
dc.subjectSueloes_AR
dc.subjectSoileng
dc.subjectPerfil del Sueloes_AR
dc.subjectSoil Profileseng
dc.subjectCuencas Hidrográficases_AR
dc.subjectWatershedseng
dc.subjectPoluciónes_AR
dc.subjectPollutioneng
dc.subjectCarbonoes_AR
dc.subjectCarboneng
dc.subject.otherAMPAes_AR
dc.subject.otherCarbono Orgánicoes_AR
dc.subject.otherArgentina
dc.titleOccurrence of glyphosate and AMPA in an agricultural watershed from the southeastern region of Argentinaes_AR
dc.typeinfo:ar-repo/semantics/artículoes_AR
dc.typeinfo:eu-repo/semantics/articlees_AR
dc.typeinfo:eu-repo/semantics/publishedVersiones_AR
dc.description.origenEEA Balcarcees_AR
dc.description.filFil: Lupi, Leonardo. Consejo Nacional de Investigaciones Científicas y Técnicas. Centro Científico Tecnológico Conicet - Mar del Plata. Instituto de Investigaciones Marinas y Costeras. Laboratorio de Ecotoxicología y Contaminación Ambiental. Universidad Nacional de Mar del Plata. Facultad de Ciencia Exactas y Naturales. Instituto de Investigaciones Marinas y Costeras. Laboratorio de Ecotoxicología y Contaminación Ambiental; Argentinaes_AR
dc.description.filFil: Miglioranza, Karina Silvia Beatriz. Consejo Nacional de Investigaciones Científicas y Técnicas. Centro Científico Tecnológico Conicet - Mar del Plata. Instituto de Investigaciones Marinas y Costeras. Laboratorio de Ecotoxicología y Contaminación Ambiental. Universidad Nacional de Mar del Plata. Facultad de Ciencia Exactas y Naturales. Instituto de Investigaciones Marinas y Costeras. Laboratorio de Ecotoxicología y Contaminación Ambiental; Argentinaes_AR
dc.description.filFil: Aparicio, Virginia. Instituto Nacional de Tecnología Agropecuaria (INTA). Estación Experimental Agropecuaria Balcarce; Argentinaes_AR
dc.description.filFil: Marino, Damian Jose Gabriel. Consejo Nacional de Investigaciones Científicas y Técnicas; Argentina. Universidad Nacional de La Plata. Facultad de Ciencias Exactas; Argentinaes_AR
dc.description.filFil: Bedmar, Francisco. Instituto Nacional de Tecnología Agropecuaria (INTA). Estación Experimental Agropecuaria Balcarce; Argentinaes_AR
dc.description.filFil: Wunderlin, Daniel Alberto. Consejo Nacional de Investigaciones Científicas y Técnicas. Centro Científico Tecnológico Conicet - Córdoba. Instituto de Ciencia y Tecnología de Alimentos Córdoba. Universidad Nacional de Córdoba. Facultad de Ciencias Químicas. Instituto de Ciencia y Tecnología de Alimentos Córdoba; Argentinaes_AR
dc.subtypecientifico


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