ABSTRACT This study compared the sorption-desorption behavior of glufosinate-ammonium herbicide in three soils (S1, S2, S3) and these soils amended with farmyard manure (S1 M, S2 M, S3 M) and bentonite clay (S1C, S2C, S3C) at 288 K, 298K and 308 K. Sorption-desorption kinetics was studied by pseudo first, pseudo second, elovich and intraparticle diffusion models and isotherms by Freundlich, Langmuir, Temkin, SIPS and Dubinin-Radushkevich (D-R) equations. The kinetic data were best explained by Pseudo-second order and isothermal data with Freundlich model with higher correlation regression coefficients, R2 values. The results indicated that the addition of farmyard manure and clay enhanced the adsorption capacity of soils, with higher adsorption by farmyard manure as confirmed from higher Kd (9.1–16. 2 in Soil III > 7.4–12.1 in Soil II > 4.8–10.3 in Soil I) and Kf values (Soil III (9.48–13.12) > Soil II (8.17–11.50) > Soil I (5.42–10.36) in following order Soil III > Soil II > I. With increase in temperature adsorption decreased, due to weak interactions as indicated by decrease in Kd and Kf values. Desorption results indicated more retention of glufosinate-ammonium at low temperature. The sorption desorption coefficients values (Kfads< Kfdes) and strengths of adsorption/desorption (1/nads <1/ndes) indicated positive hysteresis. The negative ΔGo in the range −3.99 to −5.58 KJ/mol in Soil I, −4.99 to −5.98 in Soil II and −5.66 to − 6.66 in Soil III and ΔH° values in the range −6.96 to −10.26 indicated spontaneous and exothermic nature of sorption process. The risks of water bodies contamination in terms of groundwater ubiquity score, in the range 0.79–1.20, classify it as a non-leacher pesticide; therefore, do not cause potential harm to ground-water. The results indicated that the sorption-desorption was significantly affected by organic carbon, clay and temperature, therefore their addition can be utilized as suitable alternative to reduce environmental contamination by pesticides.
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