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Aqueous norfloxacin removal by novel biochar adsorbent prepared through ethanol-combined ball milling

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Article: 2311675 | Received 11 Dec 2023, Accepted 24 Jan 2024, Published online: 06 Feb 2024

Figures & data

Table 1. Elemental contents of p-BC, C2H6O-BC and C2H6O-BC after nor adsorption.

Figure 1. SEM images of p-BC (a) and C2H6O-BC (b), N2 adsorption and desorption isotherms (c) and FT-IR spectra of unloaded and NOR/Cu-loaded biochars (d).

Figure 1. SEM images of p-BC (a) and C2H6O-BC (b), N2 adsorption and desorption isotherms (c) and FT-IR spectra of unloaded and NOR/Cu-loaded biochars (d).

Figure 2. Adsorption isotherms, kinetics and the related comparisons and fitting [(a) adsorption isotherms; (b) comparison of NOR adsorption capacity by C2H6O-BC with that by unmodified/modified hydrothermal/slow pyrolyzed biochars reported in literature [Citation34–38]; (c) adsorption kinetics ; and (d) mass transfer process simulated by weber-morris model].

Figure 2. Adsorption isotherms, kinetics and the related comparisons and fitting [(a) adsorption isotherms; (b) comparison of NOR adsorption capacity by C2H6O-BC with that by unmodified/modified hydrothermal/slow pyrolyzed biochars reported in literature [Citation34–38]; (c) adsorption kinetics ; and (d) mass transfer process simulated by weber-morris model].

Table 2. Adsorption fitting parameters of C2H6O-BC and p-BC.

Figure 3. Effect of solution initial pH on NOR adsorption onto C2H6O-BC (bichar 2 g L−1, 24 h)(a), co-existing Cu(II) (bichar 1 g L−1, 24 h) (b) and solid-liquid ration (1: 0.5 g L−1; 2: 1 g L−1; 3: 2 g L−1; 4: 4 g L−1, 24 h) (c).

Figure 3. Effect of solution initial pH on NOR adsorption onto C2H6O-BC (bichar 2 g L−1, 24 h)(a), co-existing Cu(II) (bichar 1 g L−1, 24 h) (b) and solid-liquid ration (1: 0.5 g L−1; 2: 1 g L−1; 3: 2 g L−1; 4: 4 g L−1, 24 h) (c).

Figure 4. Fixed bed adsorption of NOR adsorption by C2H6O-BC [(a) sorption of NOR with influent concentration of 15 mg L−1 (NOR1), 100 mg L−1 (NOR2) and 200 mg L−1 (NOR3); (b) Thomas model fitting; (c) Yoon-nelson Model fitting; (d) effects of high concentration of Cu(II) (15 mg L−1 NOR +100 mg L−1 Cu); (e) effects of Cu(II) preloading (200 mg L−1 NOR after preloading of 120 mg L−1 Cu); and (f) co-transport of 200 mg L−1 NOR +120 mg L−1 Cu as a comparison for preloading experiment].

Figure 4. Fixed bed adsorption of NOR adsorption by C2H6O-BC [(a) sorption of NOR with influent concentration of 15 mg L−1 (NOR1), 100 mg L−1 (NOR2) and 200 mg L−1 (NOR3); (b) Thomas model fitting; (c) Yoon-nelson Model fitting; (d) effects of high concentration of Cu(II) (15 mg L−1 NOR +100 mg L−1 Cu); (e) effects of Cu(II) preloading (200 mg L−1 NOR after preloading of 120 mg L−1 Cu); and (f) co-transport of 200 mg L−1 NOR +120 mg L−1 Cu as a comparison for preloading experiment].

Table 3. Removal ratios of nor by C2H6O-BC via STBR.

Figure 5. The XPS spectrum of C2H6O before and after adsorption [(a) the full XPS spectrum and (b) the high-resolution XPS spectrum of C1s, O1s and Cu2p].

Figure 5. The XPS spectrum of C2H6O before and after adsorption [(a) the full XPS spectrum and (b) the high-resolution XPS spectrum of C1s, O1s and Cu2p].
Supplemental material

Supplemental Material

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Data availability statement

Data will be made available on request.