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 degrees 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.

Automated summary

This study investigated the impact of biochar-derived dissolved organic matter (BDOM) on the immobilization of lead (Pb(II)) on biochar (BC). Results showed that fulvic-like substances and small molecules with low aromaticity in BDOM favored association with Pb(II) and re-adsorption on residual BC, with the adsorption mechanism dependent on the Pb(II) concentration. This research provides insights into the interfacial mechanisms between BDOM and Pb(II) and their contribution to long-term remediation of Pb-contaminated soils using BC.