Abstract
Magnetite-loaded biochar has recently received attention owing to its ability to remove arsenic from contaminated soil. In this study, mulberry stem biochar (MBC) and Fe(3)O(4)-loaded mulberry stem biochar (Fe(3)O(4)@MBC) were produced and used in a 100-day incubation experiment to investigate their performance in the stabilization of arsenic in paddy soil severely polluted by the As (237.68 mg·kg(-1)) mechanism. Incubation experiments showed that Fe(3)O(4)@MBC was more effective in immobilizing As after incubation for 100 days. Moreover, adding Fe(3)O(4)@MBC facilitated the transformation of exchangeable heavy metals into organic-bound and residual forms, thereby reducing As available concentrations, mobility, and bioavailability in the soil, and elevating slightly the soil pH and dissolved organic carbon (DOC). The concentration of TCLP-extractable As (As(TCLP)) in contaminated soil was reduced from 93.85 to 7.64 μg·L(-1) within 10 d, below the safety limit for drinking water set by the World Health Organization (WHO). The characterization results of Fe(3)O(4)@MBC after incubation indicated that the mechanisms for As passivation are linked to redox reactions, complexation, electrostatic attraction, surface adsorption, and coprecipitation. Conclusively, Fe(3)O(4)@MBC is a promising amendment in highly As-contaminated soil and provides a theoretical reference in such polluted paddy soil remediation.