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. 2019 May 7;9(25):14143-14153.
doi: 10.1039/c9ra01271k.

Antibiotic removal by agricultural waste biochars with different forms of iron oxide

Affiliations

Antibiotic removal by agricultural waste biochars with different forms of iron oxide

Yue Chen et al. RSC Adv. .

Abstract

Pollution by antibiotics has become a serious threat to public health. In this study, agricultural waste, corn husk, in the form of biochar, was utilized for antibiotic removal from wastewater. Two kinds of iron-loaded biochars, impregnation-pyrolysis biochar (IP) and pyrolysis-impregnation biochar (PI), were synthesized to adsorb the typical antibiotics tetracycline (TC) and levofloxacin (LEV). PI contained amorphous hydrated iron oxide, whereas the major component of IP was γ-Fe2O3. Compared with IP, PI had a much higher adsorption capacity for both TC and LEV. This was because PI could provide more -OH, especially -OHads, to serve as the adsorption sites. In comparison with TC, -OH was prone to combine with LEV. FT-IR and XPS results indicated that the mechanisms of LEV adsorption included hydrogen bonding, F-replacement, electrostatic attraction and bridging bidentate complexation. TC adsorption may involve complexation, hydrogen bonding and electrostatic attraction.

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Conflict of interest statement

There are no conflicts to declare.

Figures

Fig. 1
Fig. 1. The structures of LEV (a) and TC (b).
Fig. 2
Fig. 2. Procedure for the preparation of PI and IP.
Fig. 3
Fig. 3. XRD of IP (a) and PI (b).
Fig. 4
Fig. 4. Adsorption amounts at different pH values.
Fig. 5
Fig. 5. FT-IR spectra of IP (a), PI (b) before and after adsorption, FT-IR spectra of LEV and TC (c).
Fig. 6
Fig. 6. The adsorption amount in the single and competitive systems: (a) LEV adsorption amount by PI; (b) TC adsorption amount by PI; (c) LEV adsorption amount by IP; (d) TC adsorption amount by IP.
Fig. 7
Fig. 7. Possible adsorption mechanisms for LEV (a) and TC (b).
Fig. 8
Fig. 8. Reuse experiment results.

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