Efficacy of in situ active capping Cd highly contaminated sediments with nano-Fe2O3 modified biochar

Effective remediation of Cd polluted sediment is imperative for its potential damages to aquatic ecosystem. Biochar (BC) and nano-Fe₂O₃ modified BC (nFe₂O₃@BC) were conducted to remedy Cd highly contaminated sediments, and their performances, applicable conditions, and mechanisms were investigated. After 60 d capping, both BC and nFe₂O₃@BC capping inhibited Cd release from sediment to overlying water and porewater (reduction rates >99%). The released Cd concentrations in overlying water with nFe₂O₃@BC capping decreased by 1.6–11.0 times compared to those of BC capping, indicating nFe₂O₃@BC presented a higher capping efficiency. Notably, the increases of acidity and disturbance intensity of overlying water weakened the capping efficiencies of nFe₂O₃@BC and BC. BC capping was inappropriate in acidic and neutral waters (pH 3, 5, and 7) because Cd maintained a continuous release after 15 d, while nFe₂O₃@BC capping was valid in all pH treatments. Under 150 rpm stirring treatment, Cd release rates with BC and nFe₂O₃@BC capping decreased after 15 d and 30 d, respectively. At 0 and 100 rpm treatments, Cd releases treated by nFe₂O₃@BC capping finally kept a balance, indicating nFe₂O₃@BC was valid at low disturbance intensity. BC and nFe₂O₃@BC capping inhibited Cd release via weakening the influences of pH and disturbance on sediment. However, capping layers should be further processed because most adsorbed Cd in capping layers (>98%) would be re-released into overlying water. Meanwhile, excessive application of nFe₂O₃@BC could increase the risk of Fe release. The results provide novel insights into the potential applications of nFe₂O₃@BC and BC in situ capping of Cd polluted sediments in field remediation.