Abstract <p>Effective simultaneous passivation of cationic (Cd) and anionic (As) heavy metal (metalloids) still is a critical environmental challenge. In this study, rice husk biochar was ball-milled with iron-based materials magnetite (Fe₃O₄) and pyrite (FeS₂), then re-pyrolyzed at 600^oC to produce modified biochars Fe₃O₄-BC and FeS₂-BC respectively. Short-term removal performance was evaluated after 24&#xa0;h adsorption in dual-element aqueous systems where Fe₃O₄-BC displayed Cd (99.62%) and As (62.39%) removal, and FeS₂-BC displayed Cd (81.73%) and As (55.54%) removal, and BC displayed Cd (99.04%) and As (54.31%) removal. Tessier and Wenzel sequential extraction of Cd and As sorbed biochar solids revealed both modifications led to enhanced immobilization mechanisms (precipitation and complexation) absent in unmodified BC. XRD and FTIR spectra identified heavy metal precipitates and surface complexation respectively. Sorbed Cd, As was visualized with SEM-EDS. Long-term passivation effects were studied in co-contaminated soil systems with 1% (w/w) treatment with biochars, quantifying&gt; soil-to-plant heavy metal translocation by bioconcentration factors in lettuce plant, shoot, and root. Differing passivation superiority was observed for each individual metal, where Fe_,3,,O,_,4,,-BC treatment led to lowest plant Cd BCF (70.77%) while FeS,_,2,,-BC treatment resulted in lowest plant As BCF (65.72%),. Interestingly, in comparison to the control, application of unmodified BC led to,increased plant As BCF (101.03%),, suggesting biochar modification with inorganic iron materials leads to increased long-term stability by decelerating DOC release. Overall, Fe₃O₄-BC treatment appeared most effective in countering simultaneous Cd and As accumulation in edible lettuce portions,displaying shoot Cd BCF (35.33%) and shoot As BCF (9.17%).</p> Graphical abstract <p></p>