Abstract

A molecular theory has been applied to study the equilibrium conditions of glyphosate and aminomethylphosphonic acid (AMPA) adsorption from aqueous solutions to hydrogel films of cross-linked polyallylamine (PAH). This theoretical framework allows for describing the size, shape, state of charge/protonation, and configurational freedom of all chemical species in the system. Adsorption of glyphosate is a nonmonotonic function of the solution pH, which results from the protonation behavior of both the adsorbate and adsorbent material. Glyphosate and chloride ions compete for adsorption to neutralize the polymer charge; lowering the solution salt concentration enhances the partition of glyphosate inside the hydrogel film. AMPA adsorption is qualitatively similar to that of glyphosate but orders of magnitude smaller under the same conditions. AMPA is less charged than glyphosate, which unbalances the competition for adsorption with salt counter ions. In mixed solutions, glyphosate presence can significantly hinder AMPA adsorption. A higher pH establishes inside the film than in the bulk solution, which has important implications for the herbicide biodegradation because microbial activity is pH-dependent. Thus, PAH hydrogel films can be considered as functional materials that combine glyphosate sequestration and in situ degradation. In devising these materials, the polymer density is an important variable of design; polymer networks with high density of titratable units can enhance adsorption; this density can also be used to modify the pH inside the material.

Highlights

  • Glyphosate (GLP) is the world’s best-selling and most widely applied pesticide.[1,2] In Argentina, GLP use continues to increase with 0.2 megatons consumed in 2012, which represents 80% of total herbicide sales in the country.[3]

  • We investigate the adsorption of GLP, aminomethylphosphonic acid (AMPA), and their mixtures to grafted poly(allylamine hydrochloride) (PAH) cross-linked networks

  • Panel A shows that Γ is a decreasing function of the salt concentration, which is a clear signature that adsorption is driven by PAH−GLP electrostatic attractions

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Summary

Introduction

Glyphosate (GLP) is the world’s best-selling and most widely applied pesticide.[1,2] In Argentina, GLP use continues to increase with 0.2 megatons consumed in 2012, which represents 80% of total herbicide sales in the country.[3] This efficient broadspectrum herbicide, used nonselectively in agriculture, works by blocking a biochemical pathway leading to the production of essential amino acids, causing plant death by starvation.[4] Because humans do not produce essential amino acids, GLP use is presumed safe. GLP has been detected in different soils, groundwaters, surface waters, and its bottom sediments, in those used for agriculture;[5−7] it has been found in processed food, drinking water, and pharmaceutical products.[8,9] it is nowadays clear that development of means for GLP removal is of critical importance

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