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Comparative adsorption capacities of CAP antibiotic onto materials Fe3O(BDC)3 and MPCs-x, where x presents pyrolysis temperature at 600, 700, 800, and 900 °C.

Comparative adsorption capacities of CAP antibiotic onto materials Fe3O(BDC)3 and MPCs-x, where x presents pyrolysis temperature at 600, 700, 800, and 900 °C.

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Chloramphenicol (CAP) is commonly employed in veterinary clinics, but illegal and uncontrollable consumption can result in its potential contamination in environmental soil, and aquatic matrix, and thereby, regenerating microbial resistance, and antibiotic-resistant genes. Adsorption by efficient, and recyclable adsorbents such as mesoporous carbon...

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... In this investigation, the linear form of the Langmuir and Freundlich isotherms with two parameters was used to describe the adsorption data. [46,47] Several adsorption methods may use the Langmuir adsorption isotherm. The fundamental premise is that an adsorbate monolayer will develop on the adsorbent's outer surface and that there will be no more adsorption after that. ...
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... H°was found to be negative in value (− 36.41 kJ/mol) which demonstrates an exothermic adsorption system and agrees with previous reports [58,78,81,82]. Additionally, ...
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... The optimum synthesis parameters showed that N-HPC-850-2, which was prepared at 850 0 C calcination temperature and 2:1 mass ratio, exhibited the best porous carbon to eliminate CAP from water with a q max of 742.4 mg g À1 . Zhang et al. [79] found that the adsorption of CAP by CMCHPCs was endothermic as the adsorption capacity increased from 769. 95 [104] atmosphere at 700 ℃ for 4 h [82]. The adsorption capacity of CAP by MPC700 (40.6 mg g À1 ) was approximately 4 times higher than the adsorption capacity of Fe 3 O (BDC) 3 (9.6 mg g À1 ). ...
... For CAP, the magnetic resin MA-50 had the q max (193.88 mg g À1 ) among the produced resins. Tran et al. indicated that the treatment of raw (M 3 ) steel shavings by plasma in nitrogen (N 2 ) environment (M 3 -plN 2 ) slightly improved the adsorption capacity of CAP from 2.77 to 2.92 mg g À1 [82]. Xing et al. used cornstalk biomass fiber (CF) and Fe 3 O 4 embedded chitosan (CS) to synthesis a bio-composite (CFS) for effective elimination of CAP from water [104]. ...
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... Meanwhile, metal-organic frameworks (MOFs), constructed by Fe metal clusters and organic linkers (Tran et al. 2017), can become interesting templates for synthesizing nanocomposite. In a previous study, magnetically mesoporous carbon nanocomposite (Fe@C) stemmed from Fe-based MOF [Fe 3 O(BDC) 3 or Fe-MIL-88B] has been produced and this kind of material was adopted to remove an emergent chloramphenicol (CAP) antibiotic with high maximum adsorption capacity (96.3 mg/g) (Tran et al. 2019b). Hence, the potential for Fe@C nanocomposite is of great interest in adsorption applications. ...
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... Fourier transform infrared (FT-IR) spectra analysis was carried out on a Nicolet 6700 instrument. The pH drift method was used to evaluate the point of zero charge (pHpzc) for Cu-BDC [24] . 10 mg of Cu-BDC is added to 50 mL of 0.01 mol/L NaCl solution with different initial pH (pH Initial = 2-12 range) using 0.1 mol/L NaOH and HCl. ...
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... 949.3, and 956.4 eV. Herein, the existence of zero-valent Cu was not detected on XPS profile, but observed on XRD diffraction spectrum of Cu/Cu 2 O/CuO@C partly because hollow carbon matrix may decorate Cu/Cu 2 O/CuO particles, and Cu (I, II) layers may encapsulate zero-valent Cu, hampering the XPS signals to metal atoms [30]. In another interpretation, Zhao et al. claimed that binding energies between Cu (I) and Cu (0) may be overlapped, making Cu signals difficult to distinguish Cu 2 O signals [22]. ...
... The herein outcomes asserted the dominance of pseudo second-order in adsorption kinetic and seemed strongly suitable with other works [38,39]. In our previous publications, above results were very expectable for adsorption models for CIP and TTC [30,40]. ...
... J/mol.K) imply high affinity of Cu/Cu 2 O/CuO@C towards these compounds because of the migration between solvent and adsorbate molecules in heterogeneous phases [53]. Finally, the negative values of Gibbs free energy confirm the spontaneous nature of CIP and TTC adsorption over Cu/ Cu 2 O/CuO@C [30]. ...
... 10) [20], pseudo second-order (Eq. 11) [41], Elovich (Eq. 12) [42], and Bangham (Eq. ...
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Herein, an efficient and rapid fabrication procedure for ZIF-8 crystals through microwave-assisted strategy (450 W, 140 °C, and 15 min) was reported. Additionally, the crystallinity, morphology, chemical bonding, and porosity of ZIF-8 was fully characterized by X–ray powder diffraction (XRD), scanning electron microscopes (SEM), X-ray photoelectron spectroscopy (XPS), Fourier-transform infrared spectroscopy (FT-IR), and N2 adsorption/desorption isotherm measurement. Response surface methodology approach was established to optimize a series of adsorption conditions: initial concentration (8–92 mg/L), dose (0.6–1.4 g/L), and time (20–220 min) for CR and RhB removals. Many statistical error functions (R², MRE, χ², HYBRID, and MPSD) were analyzed to compare the compatibility of nonlinearised kinetic and isotherm models. Particularly, plausible adsorption mechanisms (electrostatic interactions and π–π stacking) were elucidated and isotherm models were rigorously studied by two-parameter equations (Langmuir, Freundlich, Temkin) and three-parameter equations (Redlich-Peterson, Sips, Khan). Through advantageous effectiveness involving good reusability (4 recycles), high removal efficiency (87–99%), maximum adsorption capacities (95.5–167.0 mg/g), it is recommendable to utilize ZIF-8 as an adequate adsorbent for the dyes remediation.