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Updated: May 5, 2026

Physical, Chemical and Biological Characterization of Six Biochars Produced for the Remediation of Contaminated Sites
Published on: November 28, 2014
Biochar aging-driven cadmium release in paddy soils: Mechanistic insights into adsorption capacity loss and biochar
Ze-Ning Yu1, Xiao-Qing Zhang1, Fei-Mei Chen1
1Key Laboratory of Soil Environment and Waste Reuse in Agriculture of Guangdong Higher Education Institutes, College of Natural Resources and Environment, South China Agricultural University, Guangzhou 510642, China.
Abstract:
Biochar application in Cd-contaminated paddy soils relies heavily on its inherent capacity for direct Cd adsorption. However, the long-term stability is critically challenged by Cd re-mobilization during biochar aging. Thus, we conducted a six-season pot experiment to investigate the temporal Cd release patterns under rice cultivation conditions from four types of Cd-loaded biochar: sewage sludge biochar (Cd-SSBC), palm fiber biochar (Cd-PFBC), pig manure biochar (Cd-PMBC), and rice straw biochar (Cd-RSBC). Our findings revealed three key phases of Cd release dynamics: (1) initial rapid Cd release (first growing season) exhibited strong material specificity, following the order: Cd-SSBC (61.59 %) > Cd-PFBC (48.10 %) > Cd-PMBC (27.82 %) > Cd-RSBC (28.90 %), (2) mid-term (second to the fourth growing season) slow release phase where pH decline (ΔpH = -0.55 to 0.81) showed significant positive correlation with Cd release (r = 0.75, p < 0.001), and (3) long-term equilibration phase after six seasons rice with cumulative Cd release reaching 85.56 %-93.92 %. Results also demonstrated distinct stability profiles among Cd-binding forms at initial aging phase: hydrogen bonding (Qhyd-Cd) and complexed (Qcom-Cd) species exhibited greater persistence compared to physically adsorbed (Qphy-Cd) and exchangeable (Qexc-Cd) fractions at initial aging phases. Notably, inter-biochar variability in total Cd release rates decreased from 33.8 % (S1) to 8.4 % (S6), while Cd form consistency increased across all biochar types. This study provides critical evidence for biochar aging-induced pH decline as the primary driver of Cd re-mobilization, and material-specific Cd release patterns. It also suggests that RSBC/PMBC may exhibit superior stability for extended applications in Cd-contaminated agroecosystems.
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