Glyphosate removal by riparian vegetable species and isolation of associated bacteria

Autores
Giaccio, Graciela Marta; Aparicio, Virginia Carolina; Estévez, Maria Cristina; de Gerónimo, Eduardo; Corral, Raúl Alejandro; Dávila Costa, José Sebastián; Alvarez, Analia
Año de publicación
2019
Idioma
inglés
Tipo de recurso
documento de conferencia
Estado
versión publicada
Descripción
Glyphosate (Gly) is the most used herbicide in Argentina. Consequently, a higher occurrence of Gly and its major metabolite (AMPA) in differentenvironmental compartments are currently found. Plants growing in such environments can reduce pollutant loads. Contaminated soils andvegetation represent a source of potentially beneficial plant associated-bacteria that could be used within microbial-assisted remediation strategies.The objectives of this study were (1) to isolate bacterial strains from Gly contaminated soil and rhizosphere of Salix fragilis (Sf) and Festucaarundinacea (Fa) spontaneously grown on soils contaminated, and (2) to evaluate Gly and AMPA content in soil and plant tissue of Sf and Fagrown in a greenhouse experiment. Samples of top soils contaminated with Gly and samples of Sf and Fa growing in the surroundings of theClaromecó stream (Tres Arroyos) were collected. For the bacterial isolation, one g of bulk soil (S) and rhizosphere soil (R) was suspended in asterile solution. Soil suspensions were diluted and plated. After 7 days of incubation, distinct colony morphotypes isolated were screened accordingto use Gly (0.5 g L-1) as only carbon source (minimal medium+Gly) and to use Gly as only P source (mineral salt medium+sodium glutamate+Gly). For the greenhouse experiment, pots were filled with 2 kg of contaminated soil and one Sf cutting and 6 Fa seedlings were planted per pot, for 3months. Four pot replicates were prepared for each treatment, including control pots. At the end of the experiment, plants were harvested, and soilsamples were taken for Gly and AMPA analysis by UPLC-MS/MS. Sixty-nine different colonies morphotypes, 23 from S and 46 from R (26 fromFa and 20 from Sf) were isolated. Seventeen of the isolates were able to grow on Gly as source of P and 14 were able to grow using Gly as sourceof C. Five of different bacterial morphotypes were able to grow using Gly as source of P and C. In the greenhouse experiment, Gly and AMPAinitial content in soils were 5512 ± 1369 μg kg-1 and 2353 ± 181 μg kg-1, (respectively). At the end of the assay, Gly final content was 325 ± 23μg kg-1 (Sf) and 25 ± 2 μg kg-1 (Fa) showing both a noticeable decrease in planted soils. AMPA final content was also decreased in Fa (822 ± 104μg kg-1) while for Sf AMPA was enhanced (3853 ± 207 μg kg-1). Gly detected in plant biomass was 513 ± 97 μg kg-1 (Sf) and 164 ± 50 μg kg-1(Fa). AMPA content in plants was 2385 ± 726 μg kg-1 (Sf) and 575 ± 87 μg kg-1 (Fa). In control pots, differences in contaminant content were notsignificant during the assay. Since Fa treatment showed decreased values of Gly and AMPA both in plant and soil, and five of different bacterialmorphotypes were able to grow using Gly as a source of P and C, bioassays combining both bacterial inoculant and Fa are currently in course.The microbial-plant system could be considered a promising tool for the phytoremediation of Gly and AMPA.
Fil: Giaccio, Graciela Marta. Instituto Nacional de Tecnología Agropecuaria. Centro Regional Buenos Aires Sur. Estación Experimental Agropecuaria Barrow; Argentina
Fil: Aparicio, Virginia Carolina. Instituto Nacional de Tecnología Agropecuaria; Argentina. Consejo Nacional de Investigaciones Científicas y Técnicas. Centro Científico Tecnológico Conicet - Mar del Plata. Instituto de Innovación para la Producción Agropecuaria y el Desarrollo Sostenible - Instituto Nacional de Tecnología Agropecuaria. Centro Regional Buenos Aires Sur. Estación Experimental Agropecuaria Balcarce. Instituto de Innovación para la Producción Agropecuaria y el Desarrollo Sostenible; Argentina
Fil: Estévez, Maria Cristina. Universidad Nacional de Tucumán; Argentina. Consejo Nacional de Investigaciones Científicas y Técnicas. Centro Científico Tecnológico Conicet - Tucumán. Planta Piloto de Procesos Industriales Microbiológicos; Argentina
Fil: de Gerónimo, Eduardo. Instituto Nacional de Tecnología Agropecuaria. Centro Regional Buenos Aires Sur. Estación Experimental Agropecuaria Balcarce. Agencia de Extensión Rural Balcarce; Argentina. Consejo Nacional de Investigaciones Científicas y Técnicas; Argentina
Fil: Corral, Raúl Alejandro. Instituto Nacional de Tecnología Agropecuaria. Centro Regional Buenos Aires Sur. Estación Experimental Agropecuaria Barrow; Argentina. Consejo Nacional de Investigaciones Científicas y Técnicas; Argentina
Fil: Dávila Costa, José Sebastián. Consejo Nacional de Investigaciones Científicas y Técnicas. Centro Científico Tecnológico Conicet - Tucumán. Planta Piloto de Procesos Industriales Microbiológicos; Argentina
Fil: Alvarez, Analia. Consejo Nacional de Investigaciones Científicas y Técnicas. Centro Científico Tecnológico Conicet - Tucumán. Planta Piloto de Procesos Industriales Microbiológicos; Argentina
The LV Annual SAIB Meeting and XIV PABMB Congress
Salta
Argentina
Sociedad Argentina de Investigación en Bioquímica y Biología Molecular
Materia
GLYPHOSATE
BIOREMEDIATION
VEGETABLE SPECIES
Nivel de accesibilidad
acceso abierto
Condiciones de uso
https://creativecommons.org/licenses/by-nc-sa/2.5/ar/
Repositorio
CONICET Digital (CONICET)
Institución
Consejo Nacional de Investigaciones Científicas y Técnicas
OAI Identificador
oai:ri.conicet.gov.ar:11336/181022

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network_acronym_str CONICETDig
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network_name_str CONICET Digital (CONICET)
spelling Glyphosate removal by riparian vegetable species and isolation of associated bacteriaGiaccio, Graciela MartaAparicio, Virginia CarolinaEstévez, Maria Cristinade Gerónimo, EduardoCorral, Raúl AlejandroDávila Costa, José SebastiánAlvarez, AnaliaGLYPHOSATEBIOREMEDIATIONVEGETABLE SPECIEShttps://purl.org/becyt/ford/2.8https://purl.org/becyt/ford/2Glyphosate (Gly) is the most used herbicide in Argentina. Consequently, a higher occurrence of Gly and its major metabolite (AMPA) in differentenvironmental compartments are currently found. Plants growing in such environments can reduce pollutant loads. Contaminated soils andvegetation represent a source of potentially beneficial plant associated-bacteria that could be used within microbial-assisted remediation strategies.The objectives of this study were (1) to isolate bacterial strains from Gly contaminated soil and rhizosphere of Salix fragilis (Sf) and Festucaarundinacea (Fa) spontaneously grown on soils contaminated, and (2) to evaluate Gly and AMPA content in soil and plant tissue of Sf and Fagrown in a greenhouse experiment. Samples of top soils contaminated with Gly and samples of Sf and Fa growing in the surroundings of theClaromecó stream (Tres Arroyos) were collected. For the bacterial isolation, one g of bulk soil (S) and rhizosphere soil (R) was suspended in asterile solution. Soil suspensions were diluted and plated. After 7 days of incubation, distinct colony morphotypes isolated were screened accordingto use Gly (0.5 g L-1) as only carbon source (minimal medium+Gly) and to use Gly as only P source (mineral salt medium+sodium glutamate+Gly). For the greenhouse experiment, pots were filled with 2 kg of contaminated soil and one Sf cutting and 6 Fa seedlings were planted per pot, for 3months. Four pot replicates were prepared for each treatment, including control pots. At the end of the experiment, plants were harvested, and soilsamples were taken for Gly and AMPA analysis by UPLC-MS/MS. Sixty-nine different colonies morphotypes, 23 from S and 46 from R (26 fromFa and 20 from Sf) were isolated. Seventeen of the isolates were able to grow on Gly as source of P and 14 were able to grow using Gly as sourceof C. Five of different bacterial morphotypes were able to grow using Gly as source of P and C. In the greenhouse experiment, Gly and AMPAinitial content in soils were 5512 ± 1369 μg kg-1 and 2353 ± 181 μg kg-1, (respectively). At the end of the assay, Gly final content was 325 ± 23μg kg-1 (Sf) and 25 ± 2 μg kg-1 (Fa) showing both a noticeable decrease in planted soils. AMPA final content was also decreased in Fa (822 ± 104μg kg-1) while for Sf AMPA was enhanced (3853 ± 207 μg kg-1). Gly detected in plant biomass was 513 ± 97 μg kg-1 (Sf) and 164 ± 50 μg kg-1(Fa). AMPA content in plants was 2385 ± 726 μg kg-1 (Sf) and 575 ± 87 μg kg-1 (Fa). In control pots, differences in contaminant content were notsignificant during the assay. Since Fa treatment showed decreased values of Gly and AMPA both in plant and soil, and five of different bacterialmorphotypes were able to grow using Gly as a source of P and C, bioassays combining both bacterial inoculant and Fa are currently in course.The microbial-plant system could be considered a promising tool for the phytoremediation of Gly and AMPA.Fil: Giaccio, Graciela Marta. Instituto Nacional de Tecnología Agropecuaria. Centro Regional Buenos Aires Sur. Estación Experimental Agropecuaria Barrow; ArgentinaFil: Aparicio, Virginia Carolina. Instituto Nacional de Tecnología Agropecuaria; Argentina. Consejo Nacional de Investigaciones Científicas y Técnicas. Centro Científico Tecnológico Conicet - Mar del Plata. Instituto de Innovación para la Producción Agropecuaria y el Desarrollo Sostenible - Instituto Nacional de Tecnología Agropecuaria. Centro Regional Buenos Aires Sur. Estación Experimental Agropecuaria Balcarce. Instituto de Innovación para la Producción Agropecuaria y el Desarrollo Sostenible; ArgentinaFil: Estévez, Maria Cristina. Universidad Nacional de Tucumán; Argentina. Consejo Nacional de Investigaciones Científicas y Técnicas. Centro Científico Tecnológico Conicet - Tucumán. Planta Piloto de Procesos Industriales Microbiológicos; ArgentinaFil: de Gerónimo, Eduardo. Instituto Nacional de Tecnología Agropecuaria. Centro Regional Buenos Aires Sur. Estación Experimental Agropecuaria Balcarce. Agencia de Extensión Rural Balcarce; Argentina. Consejo Nacional de Investigaciones Científicas y Técnicas; ArgentinaFil: Corral, Raúl Alejandro. Instituto Nacional de Tecnología Agropecuaria. Centro Regional Buenos Aires Sur. Estación Experimental Agropecuaria Barrow; Argentina. Consejo Nacional de Investigaciones Científicas y Técnicas; ArgentinaFil: Dávila Costa, José Sebastián. Consejo Nacional de Investigaciones Científicas y Técnicas. Centro Científico Tecnológico Conicet - Tucumán. Planta Piloto de Procesos Industriales Microbiológicos; ArgentinaFil: Alvarez, Analia. Consejo Nacional de Investigaciones Científicas y Técnicas. Centro Científico Tecnológico Conicet - Tucumán. Planta Piloto de Procesos Industriales Microbiológicos; ArgentinaThe LV Annual SAIB Meeting and XIV PABMB CongressSaltaArgentinaSociedad Argentina de Investigación en Bioquímica y Biología MolecularTech Science Press2019info:eu-repo/semantics/publishedVersioninfo:eu-repo/semantics/conferenceObjectReuniónJournalhttp://purl.org/coar/resource_type/c_5794info:ar-repo/semantics/documentoDeConferenciaapplication/pdfapplication/pdfapplication/pdfhttp://hdl.handle.net/11336/181022Glyphosate removal by riparian vegetable species and isolation of associated bacteria; The LV Annual SAIB Meeting and XIV PABMB Congress; Salta; Argentina; 2019; 1470327-9545CONICET DigitalCONICETenginfo:eu-repo/semantics/altIdentifier/url/https://techscience.com/biocell/v39nSuppl.S/34055/pdfInternacionalinfo:eu-repo/semantics/openAccesshttps://creativecommons.org/licenses/by-nc-sa/2.5/ar/reponame:CONICET Digital (CONICET)instname:Consejo Nacional de Investigaciones Científicas y Técnicas2025-09-29T09:49:00Zoai:ri.conicet.gov.ar:11336/181022instacron:CONICETInstitucionalhttp://ri.conicet.gov.ar/Organismo científico-tecnológicoNo correspondehttp://ri.conicet.gov.ar/oai/requestdasensio@conicet.gov.ar; lcarlino@conicet.gov.arArgentinaNo correspondeNo correspondeNo correspondeopendoar:34982025-09-29 09:49:00.761CONICET Digital (CONICET) - Consejo Nacional de Investigaciones Científicas y Técnicasfalse
dc.title.none.fl_str_mv Glyphosate removal by riparian vegetable species and isolation of associated bacteria
title Glyphosate removal by riparian vegetable species and isolation of associated bacteria
spellingShingle Glyphosate removal by riparian vegetable species and isolation of associated bacteria
Giaccio, Graciela Marta
GLYPHOSATE
BIOREMEDIATION
VEGETABLE SPECIES
title_short Glyphosate removal by riparian vegetable species and isolation of associated bacteria
title_full Glyphosate removal by riparian vegetable species and isolation of associated bacteria
title_fullStr Glyphosate removal by riparian vegetable species and isolation of associated bacteria
title_full_unstemmed Glyphosate removal by riparian vegetable species and isolation of associated bacteria
title_sort Glyphosate removal by riparian vegetable species and isolation of associated bacteria
dc.creator.none.fl_str_mv Giaccio, Graciela Marta
Aparicio, Virginia Carolina
Estévez, Maria Cristina
de Gerónimo, Eduardo
Corral, Raúl Alejandro
Dávila Costa, José Sebastián
Alvarez, Analia
author Giaccio, Graciela Marta
author_facet Giaccio, Graciela Marta
Aparicio, Virginia Carolina
Estévez, Maria Cristina
de Gerónimo, Eduardo
Corral, Raúl Alejandro
Dávila Costa, José Sebastián
Alvarez, Analia
author_role author
author2 Aparicio, Virginia Carolina
Estévez, Maria Cristina
de Gerónimo, Eduardo
Corral, Raúl Alejandro
Dávila Costa, José Sebastián
Alvarez, Analia
author2_role author
author
author
author
author
author
dc.subject.none.fl_str_mv GLYPHOSATE
BIOREMEDIATION
VEGETABLE SPECIES
topic GLYPHOSATE
BIOREMEDIATION
VEGETABLE SPECIES
purl_subject.fl_str_mv https://purl.org/becyt/ford/2.8
https://purl.org/becyt/ford/2
dc.description.none.fl_txt_mv Glyphosate (Gly) is the most used herbicide in Argentina. Consequently, a higher occurrence of Gly and its major metabolite (AMPA) in differentenvironmental compartments are currently found. Plants growing in such environments can reduce pollutant loads. Contaminated soils andvegetation represent a source of potentially beneficial plant associated-bacteria that could be used within microbial-assisted remediation strategies.The objectives of this study were (1) to isolate bacterial strains from Gly contaminated soil and rhizosphere of Salix fragilis (Sf) and Festucaarundinacea (Fa) spontaneously grown on soils contaminated, and (2) to evaluate Gly and AMPA content in soil and plant tissue of Sf and Fagrown in a greenhouse experiment. Samples of top soils contaminated with Gly and samples of Sf and Fa growing in the surroundings of theClaromecó stream (Tres Arroyos) were collected. For the bacterial isolation, one g of bulk soil (S) and rhizosphere soil (R) was suspended in asterile solution. Soil suspensions were diluted and plated. After 7 days of incubation, distinct colony morphotypes isolated were screened accordingto use Gly (0.5 g L-1) as only carbon source (minimal medium+Gly) and to use Gly as only P source (mineral salt medium+sodium glutamate+Gly). For the greenhouse experiment, pots were filled with 2 kg of contaminated soil and one Sf cutting and 6 Fa seedlings were planted per pot, for 3months. Four pot replicates were prepared for each treatment, including control pots. At the end of the experiment, plants were harvested, and soilsamples were taken for Gly and AMPA analysis by UPLC-MS/MS. Sixty-nine different colonies morphotypes, 23 from S and 46 from R (26 fromFa and 20 from Sf) were isolated. Seventeen of the isolates were able to grow on Gly as source of P and 14 were able to grow using Gly as sourceof C. Five of different bacterial morphotypes were able to grow using Gly as source of P and C. In the greenhouse experiment, Gly and AMPAinitial content in soils were 5512 ± 1369 μg kg-1 and 2353 ± 181 μg kg-1, (respectively). At the end of the assay, Gly final content was 325 ± 23μg kg-1 (Sf) and 25 ± 2 μg kg-1 (Fa) showing both a noticeable decrease in planted soils. AMPA final content was also decreased in Fa (822 ± 104μg kg-1) while for Sf AMPA was enhanced (3853 ± 207 μg kg-1). Gly detected in plant biomass was 513 ± 97 μg kg-1 (Sf) and 164 ± 50 μg kg-1(Fa). AMPA content in plants was 2385 ± 726 μg kg-1 (Sf) and 575 ± 87 μg kg-1 (Fa). In control pots, differences in contaminant content were notsignificant during the assay. Since Fa treatment showed decreased values of Gly and AMPA both in plant and soil, and five of different bacterialmorphotypes were able to grow using Gly as a source of P and C, bioassays combining both bacterial inoculant and Fa are currently in course.The microbial-plant system could be considered a promising tool for the phytoremediation of Gly and AMPA.
Fil: Giaccio, Graciela Marta. Instituto Nacional de Tecnología Agropecuaria. Centro Regional Buenos Aires Sur. Estación Experimental Agropecuaria Barrow; Argentina
Fil: Aparicio, Virginia Carolina. Instituto Nacional de Tecnología Agropecuaria; Argentina. Consejo Nacional de Investigaciones Científicas y Técnicas. Centro Científico Tecnológico Conicet - Mar del Plata. Instituto de Innovación para la Producción Agropecuaria y el Desarrollo Sostenible - Instituto Nacional de Tecnología Agropecuaria. Centro Regional Buenos Aires Sur. Estación Experimental Agropecuaria Balcarce. Instituto de Innovación para la Producción Agropecuaria y el Desarrollo Sostenible; Argentina
Fil: Estévez, Maria Cristina. Universidad Nacional de Tucumán; Argentina. Consejo Nacional de Investigaciones Científicas y Técnicas. Centro Científico Tecnológico Conicet - Tucumán. Planta Piloto de Procesos Industriales Microbiológicos; Argentina
Fil: de Gerónimo, Eduardo. Instituto Nacional de Tecnología Agropecuaria. Centro Regional Buenos Aires Sur. Estación Experimental Agropecuaria Balcarce. Agencia de Extensión Rural Balcarce; Argentina. Consejo Nacional de Investigaciones Científicas y Técnicas; Argentina
Fil: Corral, Raúl Alejandro. Instituto Nacional de Tecnología Agropecuaria. Centro Regional Buenos Aires Sur. Estación Experimental Agropecuaria Barrow; Argentina. Consejo Nacional de Investigaciones Científicas y Técnicas; Argentina
Fil: Dávila Costa, José Sebastián. Consejo Nacional de Investigaciones Científicas y Técnicas. Centro Científico Tecnológico Conicet - Tucumán. Planta Piloto de Procesos Industriales Microbiológicos; Argentina
Fil: Alvarez, Analia. Consejo Nacional de Investigaciones Científicas y Técnicas. Centro Científico Tecnológico Conicet - Tucumán. Planta Piloto de Procesos Industriales Microbiológicos; Argentina
The LV Annual SAIB Meeting and XIV PABMB Congress
Salta
Argentina
Sociedad Argentina de Investigación en Bioquímica y Biología Molecular
description Glyphosate (Gly) is the most used herbicide in Argentina. Consequently, a higher occurrence of Gly and its major metabolite (AMPA) in differentenvironmental compartments are currently found. Plants growing in such environments can reduce pollutant loads. Contaminated soils andvegetation represent a source of potentially beneficial plant associated-bacteria that could be used within microbial-assisted remediation strategies.The objectives of this study were (1) to isolate bacterial strains from Gly contaminated soil and rhizosphere of Salix fragilis (Sf) and Festucaarundinacea (Fa) spontaneously grown on soils contaminated, and (2) to evaluate Gly and AMPA content in soil and plant tissue of Sf and Fagrown in a greenhouse experiment. Samples of top soils contaminated with Gly and samples of Sf and Fa growing in the surroundings of theClaromecó stream (Tres Arroyos) were collected. For the bacterial isolation, one g of bulk soil (S) and rhizosphere soil (R) was suspended in asterile solution. Soil suspensions were diluted and plated. After 7 days of incubation, distinct colony morphotypes isolated were screened accordingto use Gly (0.5 g L-1) as only carbon source (minimal medium+Gly) and to use Gly as only P source (mineral salt medium+sodium glutamate+Gly). For the greenhouse experiment, pots were filled with 2 kg of contaminated soil and one Sf cutting and 6 Fa seedlings were planted per pot, for 3months. Four pot replicates were prepared for each treatment, including control pots. At the end of the experiment, plants were harvested, and soilsamples were taken for Gly and AMPA analysis by UPLC-MS/MS. Sixty-nine different colonies morphotypes, 23 from S and 46 from R (26 fromFa and 20 from Sf) were isolated. Seventeen of the isolates were able to grow on Gly as source of P and 14 were able to grow using Gly as sourceof C. Five of different bacterial morphotypes were able to grow using Gly as source of P and C. In the greenhouse experiment, Gly and AMPAinitial content in soils were 5512 ± 1369 μg kg-1 and 2353 ± 181 μg kg-1, (respectively). At the end of the assay, Gly final content was 325 ± 23μg kg-1 (Sf) and 25 ± 2 μg kg-1 (Fa) showing both a noticeable decrease in planted soils. AMPA final content was also decreased in Fa (822 ± 104μg kg-1) while for Sf AMPA was enhanced (3853 ± 207 μg kg-1). Gly detected in plant biomass was 513 ± 97 μg kg-1 (Sf) and 164 ± 50 μg kg-1(Fa). AMPA content in plants was 2385 ± 726 μg kg-1 (Sf) and 575 ± 87 μg kg-1 (Fa). In control pots, differences in contaminant content were notsignificant during the assay. Since Fa treatment showed decreased values of Gly and AMPA both in plant and soil, and five of different bacterialmorphotypes were able to grow using Gly as a source of P and C, bioassays combining both bacterial inoculant and Fa are currently in course.The microbial-plant system could be considered a promising tool for the phytoremediation of Gly and AMPA.
publishDate 2019
dc.date.none.fl_str_mv 2019
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Glyphosate removal by riparian vegetable species and isolation of associated bacteria; The LV Annual SAIB Meeting and XIV PABMB Congress; Salta; Argentina; 2019; 147
0327-9545
CONICET Digital
CONICET
url http://hdl.handle.net/11336/181022
identifier_str_mv Glyphosate removal by riparian vegetable species and isolation of associated bacteria; The LV Annual SAIB Meeting and XIV PABMB Congress; Salta; Argentina; 2019; 147
0327-9545
CONICET Digital
CONICET
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