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Removal of Antibiotic Drugs from Aqueous Solution by Modified Coconut Shell

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In this study, coconut shell (CS), coconut shell carbonized (CSC), acid coconut shell carbonized (ACSC), base coconut shell carbonized (BCSC) finally coconut shell carbonized impregnation by nickel (II) oxide (CSC/NiO) nanocomposite, investigated to remove ciprofloxacin (CIP) from an aqueous solution. Optimization of adsorption conditions: initial CIP concentration, pH, adsorbent dose and contact time were studied and found to have a significant effect on CIP removal. The morphological and chemical characteristics of the adsorbents were established by Fourier Transform Infrared (FTIR), X-Ray diffraction (XRD), The Scanning Electron Microscopy (SEM) and Energy Dispersive X-Ray (EDX). The adsorption kinetic study shows the CIP adsorption onto adsorbents follow the pseudo-second order, the values of K2, qe and R2 in the range (0.254-9.529) gµg-1min-1, (0.016-0.300) mgg-1 and (0.706-0.980) respectively at three different temperature 298 K, 308 K and 318 K. The Freundlich isotherm model adsorption data were applied and the value of KF, nF and R2 in the range (3.056-3.694) mg g-1, (1.379-1.720) and (0.886-0.999) respectively. The experimental data found to be suitable linearity with Langmuir isotherm the value of KL, Cm and R2 in the range (0.011-0.180) L mg−1, (10000-166667) μg g−1 and (0.760-0.980) respectively. The negative values of ΔGo (−18.47 to −23.74) kJ mol−l and positive value of each of ΔHo and ΔSo in the range (0.131 to 0.228) kJ mol−l and (0.992 to 1) kJ mol−lK-1 were indicating the adsorption of CIP on to adsorbents was a spontaneous and endothermic process.
Title: Removal of Antibiotic Drugs from Aqueous Solution by Modified Coconut Shell
Description:
In this study, coconut shell (CS), coconut shell carbonized (CSC), acid coconut shell carbonized (ACSC), base coconut shell carbonized (BCSC) finally coconut shell carbonized impregnation by nickel (II) oxide (CSC/NiO) nanocomposite, investigated to remove ciprofloxacin (CIP) from an aqueous solution.
Optimization of adsorption conditions: initial CIP concentration, pH, adsorbent dose and contact time were studied and found to have a significant effect on CIP removal.
The morphological and chemical characteristics of the adsorbents were established by Fourier Transform Infrared (FTIR), X-Ray diffraction (XRD), The Scanning Electron Microscopy (SEM) and Energy Dispersive X-Ray (EDX).
The adsorption kinetic study shows the CIP adsorption onto adsorbents follow the pseudo-second order, the values of K2, qe and R2 in the range (0.
254-9.
529) gµg-1min-1, (0.
016-0.
300) mgg-1 and (0.
706-0.
980) respectively at three different temperature 298 K, 308 K and 318 K.
The Freundlich isotherm model adsorption data were applied and the value of KF, nF and R2 in the range (3.
056-3.
694) mg g-1, (1.
379-1.
720) and (0.
886-0.
999) respectively.
The experimental data found to be suitable linearity with Langmuir isotherm the value of KL, Cm and R2 in the range (0.
011-0.
180) L mg−1, (10000-166667) μg g−1 and (0.
760-0.
980) respectively.
The negative values of ΔGo (−18.
47 to −23.
74) kJ mol−l and positive value of each of ΔHo and ΔSo in the range (0.
131 to 0.
228) kJ mol−l and (0.
992 to 1) kJ mol−lK-1 were indicating the adsorption of CIP on to adsorbents was a spontaneous and endothermic process.

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