Abstract

The transport of carbamazepine, ciprofloxacin and sulfamethoxazole in the different pores of activated carbon in an aqueous solution is a dynamic process that is entirely dependent on the intrinsic parameters of these molecules and of the adsorbent. The macroscopic processes that take place are analyzed by interfacial diffusion and reaction models. Modeling of the experimental kinetic curves obtained following batch treatment of each solute at 2 µg/L in tap water showed (i) that the transport and sorption rates were controlled by external diffusion and intraparticle diffusion and (ii) that the effective diffusion coefficient for each solute, with the surface and pore diffusion coefficients, were linked by a linear relationship. A statistical analysis of the experimental data established correlations between the diffusional parameters and some geometrical parameters of these three molecules. Given the major discontinuities observed in the adsorption kinetics, the modeling of the experimental data required the use of traditional kinetic models, as well as a new kinetic model composed of the pseudo first or second order model and a sigmoidal expression. The predictions of this model were excellent. The solubility of each molecule below 60 °C was formulated by an empirical expression.

Highlights

  • Carbamazepine (CBZ), Ciprofloxacin (CIP) and Sulfamethoxazole (SMX) are among the residues of pharmaceutically active compounds (PhACs) frequently found in various aquatic compartments

  • Various advanced water treatment technologies exist, due to certain economic and technical constraints, the treatment of pharmaceutical compounds by adsorption is the preferred option in drinking water production and tertiary wastewater treatment

  • Its acidic nature should promote cation adsorption. These different chemical characteristics were corroborated by the point of zero charge (PZC) and isoelectric point (IEP) values, respectively 6 and 3.6 ± 0.1

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Summary

Introduction

Carbamazepine (CBZ), Ciprofloxacin (CIP) and Sulfamethoxazole (SMX) are among the residues of pharmaceutically active compounds (PhACs) frequently found in various aquatic compartments. The fate of pharmaceutical residues in the environment is determined in part by the physical and physicochemical characteristics of each molecule (such as their size, volume, molecular mass, solubility in water, dissociation constants, octanol-water distribution coefficient (Dow )) Their fate is partly determined by environmental conditions: temperature, pH, ionic strength, presence of other chemical species, organic matter, matter in suspension, hydrodynamic conditions, hydraulic residence time, erosion, etc. Its concentration can reach up to 6 μg/L in WWTP effluents [10], 8 μg/L in surface waters [3] and a few nanograms in drinking water [11] It is considered a marker of the presence of wastewater in the aquatic environment and presents a potential risk factor for drinking water supplies. Certain characteristics of these molecules were more accurately defined in this study

C10 H11 N3 O3 S
Speciation
Activated Carbon
IEP: isoelectric
Applied Sorption Models
Impact of the Dosage of ACP on the Elimination Rate of Each Pollutant
Degradation
Dimensionless
External Diffusion
Diffusion Prediction with HSDM Model
Effective Diffusivity Prediction
Modeling
Possible Adsorption Mechanisms
Materials
Methods
Conclusions
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