GLYPHOSATE TRANSPORT IN TWO AGRICULTURAL SOILS FROM EASTERN SANTIAGO DEL ESTERO, ARGENTINA
DOI:
https://doi.org/10.64132/cds.v43i1.873Keywords:
preferential flow, no tillage, soil profile, dissipationAbstract
Glyphosate can leach into deeper soil layers with drainage water. The objective of this research was to evaluate the risk of underground water contamination with glyphosate in two soils from the east of Santiago del Estero, Argentina. Experiments were conducted with undisturbed soil columns from the A, Bt1, Bt2, and Ck horizons of an Aquic Argiustoll and the A, AC, and C horizons of an Entic Haplustoll. Glyphosate breakthrough curves were fitted with the CXTFIT package, using the parameters velocity (v) and dispersion coefficient (D) obtained from the transport experiment of an inert molecule. Retardation coefficient (R), fraction of instantaneous solute retardation (β) and mass transfer coefficient (ω) were determined. After the study, the amount of glyphosate and aminomethylphosphonic acid adsorbed to the soil columns was quantified, and a mass balance was performed to determine leaching, retention, and dissipation percentages. Leaching was very limited and variable between the columns of each horizon. The early appearance of glyphosate in effluents was an indicator of preferential flow, while asymmetric curves, concentration peaks greater than one pore volume and a retardation factor greater than 1 indicated unbalanced chemical conditions. Adsorption was more important than leaching and greater retention of total glyphosate was found in the Aquic Argiustoll soil. Finally, most of the applied glyphosate was not found in the leachate or the columns, but rather dissipated during the experiment. This could be due to the formation of non-extractable residues or complete mineralization of the herbicide. The Entic Haplustoll soil, however, is located in a water flow recharge zone and would thus present a greater risk of regional groundwater contamination with glyphosate.
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