“…Sorption is a major process which controls the mobility and bioavailability of sulfonamide antibiotics in the environment. Previous research has revealed that minerals, especially iron oxides, might have a key role in the sorption of antibiotics in soil [4][5][6].…”
Sulfamethazine (SMT) as an ionic compound can enter the soil environment via the application of livestock wastes in agricultural fields and via the abuse of pharmaceuticals. Goethite as one of the most important iron oxides in soil might interact with SMT and influence its environmental behavior and bioavailability in soil. In this study, the sorption properties of SMT on goethite under different solution conditions were investigated. The sorption isotherm exhibited a significant nonlinear shape and desorption hysteresis, while the data could be fitted well by the Freundlich model with the correlation coefficient R 2 = 0.991. Sorption capacity initially increased and then decreased as pH values increased from 3 to 13, while the strongest uptake occurred in neutral conditions. The sorption increased slightly and then kept relatively constant as the ionic strength of the solution increased. The results indicated that the sorption mechanism would be altered in different solution conditions. In acidic and neutral conditions, the p-p electron donor-acceptor interactions and outer-and inner-sphere complexions might be the dominating sorption mechanisms. The sorption in alkali conditions might be dominated by electrostatic interactions between SMT and goethite. It should be noted that the heterogeneous sorption affinity of SMT on goethite under various solution conditions will influence its environmental fate.
“…Sorption is a major process which controls the mobility and bioavailability of sulfonamide antibiotics in the environment. Previous research has revealed that minerals, especially iron oxides, might have a key role in the sorption of antibiotics in soil [4][5][6].…”
Sulfamethazine (SMT) as an ionic compound can enter the soil environment via the application of livestock wastes in agricultural fields and via the abuse of pharmaceuticals. Goethite as one of the most important iron oxides in soil might interact with SMT and influence its environmental behavior and bioavailability in soil. In this study, the sorption properties of SMT on goethite under different solution conditions were investigated. The sorption isotherm exhibited a significant nonlinear shape and desorption hysteresis, while the data could be fitted well by the Freundlich model with the correlation coefficient R 2 = 0.991. Sorption capacity initially increased and then decreased as pH values increased from 3 to 13, while the strongest uptake occurred in neutral conditions. The sorption increased slightly and then kept relatively constant as the ionic strength of the solution increased. The results indicated that the sorption mechanism would be altered in different solution conditions. In acidic and neutral conditions, the p-p electron donor-acceptor interactions and outer-and inner-sphere complexions might be the dominating sorption mechanisms. The sorption in alkali conditions might be dominated by electrostatic interactions between SMT and goethite. It should be noted that the heterogeneous sorption affinity of SMT on goethite under various solution conditions will influence its environmental fate.
“…It is a very versatile process that can be used for organic compounds and heavy metal capture thanks to a wide spectrum of adsorption targets [21,22,23] as well as for single or multiple contaminations [20,24]. The wide application of the adsorption process is also due to the possibility of using different kinds of adsorbents, including natural and waste materials either raw or activated [15,16,21,23].…”
“…K F and n are constants (Table 1). It is worth nothing that the K F values reported in literature for the sorption onto activated carbon, currently the most popular sorbent for organic compounds, and for other recently introduced sorbent materials [14,15,16,17] are markedly higher than those reported in Table 1 for PCT. For example, K F values reported for the sorption of toluene and o-xylene onto activated carbon were respectively 35.8 and 54.8 L 1/n mg 1-1/n g -1 [18]; for phenol a K F value of 54.0 L 1/n mg 1-1/n g -1 has been reported [19].…”
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