Predicting the behavior, fate, and transport potential of a herbicide in any soil involves understanding the sorption characteristics. The sorption characteristics of glyphosate (GPS) on soil and their main components were investigated, indicating that the mineral phase is more important than the organic carbon in adsorption of GPS. Sorption isotherms were determined from each component using the batch equilibrium method at various concentrations (5, 10, 15, 20, 25, and 30 mg L−1) and sorption affinity of GPS was approximated by the Freundlich equation. The sorption strength K f [mg kg−1 (L mg−1)−n] across the various components ranged from 2.1–134.9 while the organic carbon-normalized Freundlich sorption capacity values, K foc, ranged from 1.28–3.53 mg kg−1-OC/(mg L−1)n. Infrared Fourier transform spectroscopy (FTIR) of the components showed significant structural differences. The results suggest that the presence of the oxides and hydroxides iron, in particular in soil solutions, enhanced GPS adsorption. They also suggest that reduction in OC% due to various treatments may enhance the remobilization of GPS into the aqueous phase (i.e., groundwater), though at different rates. Comparatively, contribution of surface area to the adsorption of GPS on the various components proved more significant than contents of organic carbon.
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Ololade et al. (2013) studied this question.
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