Author
Listed:
- Chengcheng Liu
(School of Environmental and Safety Engineering, Changzhou University, Changzhou 213164, China
These authors contributed equally to this work.)
- Jiaxin Lin
(School of Environmental Science and Engineering, Institute of Environmental Health and Pollution Control, Guangdong University of Technology, Guangzhou 510006, China
Synergy Innovation Institute of GDUT, Shantou 515041, China
These authors contributed equally to this work.)
- Haojia Chen
(School of Environmental Science and Engineering, Institute of Environmental Health and Pollution Control, Guangdong University of Technology, Guangzhou 510006, China
Synergy Innovation Institute of GDUT, Shantou 515041, China
Chemistry and Chemical Engineering Guangdong Laboratory, Shantou 515041, China)
- Wanjun Wang
(School of Environmental Science and Engineering, Institute of Environmental Health and Pollution Control, Guangdong University of Technology, Guangzhou 510006, China
Synergy Innovation Institute of GDUT, Shantou 515041, China)
- Yan Yang
(School of Environmental and Safety Engineering, Changzhou University, Changzhou 213164, China
School of Environmental Science and Engineering, Institute of Environmental Health and Pollution Control, Guangdong University of Technology, Guangzhou 510006, China
Synergy Innovation Institute of GDUT, Shantou 515041, China
Chemistry and Chemical Engineering Guangdong Laboratory, Shantou 515041, China)
Abstract
The potential application of biochar in water treatment is attracting interest due to its sustainability and low production cost. In the present study, H 3 PO 4 -modified porous biochar (H-PBC), ethylenediaminetetraacetic acid-modified porous biochar (E-PBC), and NaOH-modified porous biochar (O-PBC) were prepared for Ni(II) and Pb(II) adsorption in an aqueous solution. Scanning electron microscopy (SEM), X-ray diffraction analysis (XRD), Brunauer–Emmett–Teller analysis (BET), and Fourier-transform infrared (FT-IR) spectroscopy were employed to characterize the as-obtained samples, and their capacities for Ni(II) and Pb(II) adsorption were determined. SEM showed that H-PBC retained the hierarchical porous structure of pristine biochar. FT-IR showed that H-PBC possessed abundant oxygen-containing and phosphorus-containing functional groups on the surface. BET analysis demonstrated that the surface areas of H-PBC (344.17 m 2 /g) was higher than O-PBC (3.66 m 2 /g), and E-PBC (1.64 m 2 /g), respectively. H-PBC, E-PBC, and O-PBC all exhibited excellent performance at Ni(II) and Pb(II) adsorption with maximum adsorption capacity of 64.94 mg/g, 47.17 mg/g, and 60.24 mg/g, and 243.90 mg/g, 156.25 mg/g, and 192.31 mg/g, respectively, which were significantly higher than the adsorption capacity (19.80 mg/g and 38.31 mg/g) of porous biochar (PBC). Pseudo-second order models suggested that the adsorption process was controlled by chemical adsorption. After three regeneration cycles, the Ni(II) and Pb(II) removal efficiency with H-PBC were still 49.8% and 56.3%. The results obtained in this study suggest that H-PBC is a promising adsorbent for the removal of heavy metals from aqueous solutions.
Suggested Citation
Chengcheng Liu & Jiaxin Lin & Haojia Chen & Wanjun Wang & Yan Yang, 2022.
"Comparative Study of Biochar Modified with Different Functional Groups for Efficient Removal of Pb(II) and Ni(II),"
IJERPH, MDPI, vol. 19(18), pages 1-14, September.
Handle:
RePEc:gam:jijerp:v:19:y:2022:i:18:p:11163-:d:907762
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