Subcellular energy balance of Odontesthes bonariensis exposed to a glyphosate-based herbicide

Water pollution by agrochemicals is currently one of the most critical problems for the conservation of aquatic ecosystems. Glyphosate [N-(phosphonomethyl) glycine); PMG] is the main broad-spectrum post emergence herbicide used for the control of a wide range of pests in soybean crops. Adenylate ene...

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Autor principal: Menéndez-Helman, R.J
Otros Autores: Miranda, L.A, dos Santos Afonso, M., Salibián, A.
Formato: Capítulo de libro
Lenguaje:Inglés
Publicado: Academic Press 2015
Acceso en línea:Registro en Scopus
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024 7 |2 cas  |a adenosine diphosphate, 20398-34-9, 58-64-0; adenosine phosphate, 61-19-8, 8063-98-7; adenosine triphosphate, 15237-44-2, 56-65-5, 987-65-5; creatine phosphate, 67-07-2; glyphosate, 1071-83-6; glycine, 56-40-6, 6000-43-7, 6000-44-8; Adenine Nucleotides; Biological Markers; Glycine; glyphosate; Herbicides; Phosphocreatine; Water Pollutants, Chemical 
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100 1 |a Menéndez-Helman, R.J. 
245 1 0 |a Subcellular energy balance of Odontesthes bonariensis exposed to a glyphosate-based herbicide 
260 |b Academic Press  |c 2015 
270 1 0 |m dos Santos Afonso, M.; INQUIMAE, Facultad de Ciencias Exactas y Naturales, CONICET-Universidad de Buenos Aires, Pabellón 2, Ciudad UniversitariaArgentina 
506 |2 openaire  |e Política editorial 
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520 3 |a Water pollution by agrochemicals is currently one of the most critical problems for the conservation of aquatic ecosystems. Glyphosate [N-(phosphonomethyl) glycine); PMG] is the main broad-spectrum post emergence herbicide used for the control of a wide range of pests in soybean crops. Adenylate energy charge (AEC) reflects the energy balance of the cells, a measure of the energy available from the adenylate pool: adenosine triphosphate (ATP), adenosine diphosphate (ADP) and adenosine monophosphate (AMP). Background adenylates, phosphagens and the AEC index of two year old Odontesthes bonariensis were determined in some tissues by HPLC, and the impact on subcellular energy balance of sublethal glyphosate-based herbicide exposure was analyzed. The doses used were 0 (control tank), 1 or 10mg PMGL-1, trials were carried out during 15 days. AEC values in brain, liver and muscle from control fish were 0.37±0.02, 0.49±0.05 and 0.56±0.03, respectively (means±SEM). While brain ATP concentrations were undetectable (hence low values of AEC), the muscle tissue showed the highest concentrations of the more energetic molecules: 0.18μmole ATPg-1 and 8μmole phosphocreatineg-1 (PCrg-1). In the brain, no significant changes were detected in exposed fish compared to controls. Instead, in both the liver and muscle of animals exposed to the highest concentration of the herbicide, significant changes in the AEC (reduction of 26% and 15%, p<0.05) with respect to the control group were determined. Chronic exposure (15 days) of Odontesthes bonariensis to 1 and 10mgL-1 of formulated glyphosate did not affect brain AEC. However, the highest concentration of the herbicide produced a significant decrease in liver and muscle AEC manifesting adverse sublethal effects on the energy metabolism. These results suggest the usefulness of AEC as a biomarker of fish glyphosate exposure. © 2015 Elsevier Inc.  |l eng 
536 |a Detalles de la financiación: Agencia Nacional de Promoción Científica y Tecnológica 
536 |a Detalles de la financiación: Consejo Nacional de Investigaciones Científicas y Técnicas, PIP 1673/12 grant 
536 |a Detalles de la financiación: Universidad de Buenos Aires 
536 |a Detalles de la financiación: Ministerio de la Producción, Ciencia y Tecnología 
536 |a Detalles de la financiación: Fondo para la Investigación Científica y Tecnológica, PICT2012-1537, PICT2007-00371 
536 |a Detalles de la financiación: Secretaría de Ciencia y Técnica, Universidad de Buenos Aires, 20020100100750 
536 |a Detalles de la financiación: The authors acknowledge the Universidad de Buenos Aires (UBA) and the IIB-INTECH (CONICET – UNSAM), where this project was carried out. Authors also gratefully acknowledge the Consejo Nacional de Investigaciones Científicas y Técnicas de la República Argentina (CONICET, PIP 1673/12 grant), Ministerio de Ciencia y Tecnología , Agencia Nacional de Promoción Científica y Tecnológica , Fondo para la Investigación Científica y Tecnológica (MINCyT-ANPCyT-FONCyT, PICT2007-00371 and PICT2012-1537 grants) and Universidad de Buenos Aires (UBACyT 20020100100750 grant) for financial support. 
593 |a INQUIMAE, Facultad de Ciencias Exactas y Naturales, CONICET-Universidad de Buenos Aires, Pabellón 2, Ciudad Universitaria, Ciudad Autónoma de Buenos Aires, C1428EHA, Argentina 
593 |a Laboratorio de Ictiofisiología y Acuicultura, Instituto de Investigaciones Biotecnológicas, Instituto Tecnologico de Chascomus (IIB-INTECH) CONICET - UNSAM. B7130IWA Chascomus, Buenos Aires, Argentina 
593 |a Programa de Ecofisiología Aplicada (PRODEA), Instituto de Ecología y Desarrollo Sustentable (INEDES), Universidad Nacional de Luján, Luján, B6700ZBA, Argentina 
690 1 0 |a ADENYLATE ENERGY CHARGE (AEC) 
690 1 0 |a BASED HERBICIDE 
690 1 0 |a BIOMARKERS 
690 1 0 |a GLYPHOSATE 
690 1 0 |a ODONTESTHES BONARIENSIS 
690 1 0 |a PHOSPHAGENS 
690 1 0 |a ADENOSINE DIPHOSPHATE 
690 1 0 |a ADENOSINE PHOSPHATE 
690 1 0 |a ADENOSINE TRIPHOSPHATE 
690 1 0 |a CREATINE PHOSPHATE 
690 1 0 |a GLYPHOSATE 
690 1 0 |a ADENINE NUCLEOTIDE 
690 1 0 |a BIOLOGICAL MARKER 
690 1 0 |a GLYCINE 
690 1 0 |a GLYPHOSATE 
690 1 0 |a HERBICIDE 
690 1 0 |a WATER POLLUTANT 
690 1 0 |a AGROCHEMICAL 
690 1 0 |a BIOMARKER 
690 1 0 |a FISH 
690 1 0 |a GLYPHOSATE 
690 1 0 |a POLLUTION EXPOSURE 
690 1 0 |a SUBLETHAL EFFECT 
690 1 0 |a ADSORPTION KINETICS 
690 1 0 |a ANIMAL EXPERIMENT 
690 1 0 |a ANIMAL TISSUE 
690 1 0 |a ARTICLE 
690 1 0 |a BRAIN LEVEL 
690 1 0 |a CELL ENERGY 
690 1 0 |a CONCENTRATION (PARAMETERS) 
690 1 0 |a CONTROLLED STUDY 
690 1 0 |a DEGRADATION KINETICS 
690 1 0 |a ENERGY BALANCE 
690 1 0 |a ENVIRONMENTAL EXPOSURE 
690 1 0 |a FEMALE 
690 1 0 |a FISH 
690 1 0 |a HIGH PERFORMANCE LIQUID CHROMATOGRAPHY 
690 1 0 |a LIVER LEVEL 
690 1 0 |a LONG TERM EXPOSURE 
690 1 0 |a MALE 
690 1 0 |a MUSCLE LEVEL 
690 1 0 |a MUSCLE TISSUE 
690 1 0 |a NONHUMAN 
690 1 0 |a ODONTESTHES BONARIENSIS 
690 1 0 |a WATER POLLUTION 
690 1 0 |a ANALOGS AND DERIVATIVES 
690 1 0 |a ANIMAL 
690 1 0 |a BRAIN 
690 1 0 |a DOSE RESPONSE 
690 1 0 |a DRUG EFFECTS 
690 1 0 |a ENERGY METABOLISM 
690 1 0 |a LIVER 
690 1 0 |a METABOLISM 
690 1 0 |a MUSCLE 
690 1 0 |a SMEGMAMORPHA 
690 1 0 |a TOXICITY 
690 1 0 |a WATER POLLUTANT 
690 1 0 |a ANIMALIA 
690 1 0 |a GLYCINE MAX 
690 1 0 |a ODONTESTHES BONARIENSIS 
690 1 0 |a ADENINE NUCLEOTIDES 
690 1 0 |a ANIMALS 
690 1 0 |a BIOLOGICAL MARKERS 
690 1 0 |a BRAIN 
690 1 0 |a DOSE-RESPONSE RELATIONSHIP, DRUG 
690 1 0 |a ENERGY METABOLISM 
690 1 0 |a GLYCINE 
690 1 0 |a HERBICIDES 
690 1 0 |a LIVER 
690 1 0 |a MUSCLES 
690 1 0 |a PHOSPHOCREATINE 
690 1 0 |a SMEGMAMORPHA 
690 1 0 |a WATER POLLUTANTS, CHEMICAL 
700 1 |a Miranda, L.A. 
700 1 |a dos Santos Afonso, M. 
700 1 |a Salibián, A. 
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