Abstract

The enhancement of surface functional groups on biochar is essential to improving its toxic metals adsorption capacity. In this study, we used two solutions: NaOH (aq) and NaOH dissolved in absolute ethanol (C 2 H 5 OH) to dope the surface of powdered oiltea camellia shell. Then, the shells were pyrolyzed at 500 °C for 120 min to obtain NaOH-modified biochar (SBC), NaOH–C 2 H 5 OH-modified biochar (EBC), and the undoped sample (BC). After modification, the special surface area, O-containing functional groups, especially C=C were improved. The specific surface area of EBC and SBC (91.76 and 56.83 m 2 g −1 , respectively) were superior to that of the BC (36.98 m 2 g −1 ). With NaOH–C 2 H 5 OH, more C=C groups were introduced via elimination reaction, enhancing its adsorption properties. EBC consistently showed higher adsorption efficiency than BC for Cd(II) and Pb(II). Moreover, the spectroscopic analysis revealed that Cd(II)- π , Pb(II)- π interactions were the predominant mechanisms for the toxic metals’ collection on the EBC, each contributing 75.45% and 58.60%, respectively. Besides, the O-functional groups onto EBC surface bonded easily to Pb(II) than Cd(II) in the mixture solution. Therefore, EBC produced in the NaOH–C 2 H 5 OH system, as efficient and cost-effective biochar, is promising for toxic metals adsorption. • NaOH–EtOH-modified improves special surface area and functional groups on biochar surface. • Cd(II) − π , Pb(II) − π interactions were the predominant mechanisms for toxic metals’ adsorption on the EBC. • The O − functional groups onto EBC surface bonded easily to Pb(II) than Cd(II) in the binary solution. • EBC exerts a relatively higher adsorption capacity for Cd(II) and Pb(II) than BC.

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