Mechanism of Cd Immobilization by Modified Corn Straw Biochar in Post-Mining Land on the Loess Plateau, China
摘要
Background: Heavy metal pollution particularly Cd, is a great threat to the environment and human health. Modified biochar is a promising material for mitigating soil Cd contamination. However, Cd immobilization performance and mechanism of modified biochar in alkaline soil of coal mine wasteland receive little attention. Purpose: This study examines the remediation efficiency of modified biochars for Cd contaminated soil in coal mine sites. Methods: Modified biochars (H2O2-BC, HNO3-BC, KMnO4-BC and CaCl2-BC) were prepared and applied to Cd-contaminated soil at three ratios (1%, 2% and 3% w/w) to investigate changes in Cd fractions and the bioavailability of Cd. Results: HNO3-BC exhibited abundant acidic functional groups. The application of biochar and modified biochars decreased the exchangeable and Fe-Mn oxides bound fractions of Cd, and increased the organic and residual fractions of Cd in soil. The exchangeable Cd with high activity decreased and residual Cd fraction increased under HNO3-BC addition at a 2% ratio. The content of soil available Cd decreased under modified biochar treatments, and the largest reduction occurred with HNO3-BC addition at a 2% ratio, followed by KMnO4-BC treatment. Conclusions: Modified biochar enhanced the transformation of Cd from labile fractions to more stable forms, and HNO3-BC application achieved the optimal remediation efficacy. Functional groups on biochar surface played a vital role in immobilizing Cd through complexation. HNO3-BC could serve as an effective measure for Cd pollution remediation in degraded ecosystems, especially in alkaline soils of northern China.