Overlooked contributions of biochar-derived dissolved organic matter on the adsorption of Pb (Ⅱ): Impacts of fractionation and interfacial force.

Comprehensive understanding of how the release of biochar-derived dissolved organic matter (BDOM) affects the immobilization of heavy metals when biochar (BC) is applied for long-term soil remediation is extremely important. In this study, BCs prepared under different pyrolysis temperatures were fractionated into residual BC (RBC), nano-sized BC (NBC), and BDOM, in order to clarify the contribution of BDOM for lead (Pb(II)) adsorption on BC and to explore the interfacial mechanisms. Results demonstrated that the adsorption capacity (Q e) of Pb(II) on BC improved from 166.1 to 423.9 mg g−1 with the increase in the pyrolysis temperature from 350 to 800 °C. The sum of Q e of Pb(II) on NBC and RBC was lower than that on BC, due to the complexation between BDOM and Pb(II) rather than pH variance and cation exchange. Ultraviolet–visible and fluorescence spectroscopy revealed that fulvic-like substances as well as small molecules with low aromaticity in BDOM underwent favorable association with Pb(II) and got re-adsorbed on RBC. With the increase in the Pb(II) concentration, the contribution of van der Waals interaction for adsorption of BDOM350-Pb complexes was improved, whereas adsorption mechanism in BDOM800-Pb complexes was more dependent on ligand exchange. This study provides mechanistic insights into the impact of BDOM on Pb(II) immobilization, which can provide valuable information for the long-term remediation of Pb-contaminated soils using BC. [Display omitted] • The Q e of Pb(Ⅱ) on BC improved with the increase in pyrolysis temperature. • The inequality Q e of Pb(Ⅱ) between BC and the sum of NBC+RBC was observed. • Complexation between BDOM and Pb(II) was responsible for the difference. • Low aromatic fulvic-like substances in BDOM preferred to bind with Pb(II). • Specific interfacial forces induced re-adsorption of BDOM-Pb complexes. [ABSTRACT FROM AUTHOR]