Pb(II) adsorption by biochar from co-pyrolysis of corn stalks and alkali-fused fly ash
Xiaotong Yun , Yan Ma , Hao Zheng , Yaru Zhang , Biying Cui , Baoshan Xing
Biochar ›› 2022, Vol. 4 ›› Issue (1)
Numerous studies have reported the potential of silica as a biochar (BC) modifier. However, despite its high silica content, fly ash is rarely used for BC modification. Herein, modified BCs were produced by co-pyrolysis of corn stalks with alkali-fused fly ash (AFFA) at 200 and 600 °C (denoted as AFFA/BC). The Pb(II) adsorption mechanism and adsorption performance were investigated. The AFFA/BC had larger specific surface areas than the pure BC samples (2.54–137 vs. 0.50 m2 g−1) owing to their stable carbon structure. The Pb(II) adsorption capacity of AFFA/BC in water was approximately 6% higher than that of BC owing to the increased cation (Na+) exchange and new bonding sites, such as C–O and Si–O. AFFA/BC exhibited good Pb(II) adsorption performance in high-concentration simulated wastewater (pH 4–6), with a maximum adsorption capacity of 110.29 mg g−1. The Pb(II) adsorption mechanism was in accordance with the pseudo-second-order kinetic and Langmuir isotherm models. At 25 °C and pH 5, the theoretical Pb(II) adsorption capacities of AFFA200/BC and AFFA600/BC were 201.66 and 186.81 mg g−1, respectively, compared to 145.98 mg g−1 of BC. Physical adsorption, precipitation, cation exchange, and complexation were identified as the main Pb(II) adsorption mechanisms through X-ray photoelectron spectrometry.
| • | A new type of biochar was prepared by co-pyrolysis of corn stalks and alkali-fused fly ash for Pb(II) removal from wastewater. |
| • | The high surface area and Pb(II) adsorption capacity of adsorbents made them suitable for wastewater treatment. |
| • | The main Pb(II) adsorption mechanisms were physisorption, precipitation, cation exchange, and complexation. |
National Key Research and Development Program of China(2020YFC1806500)
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