Huang, Q., Chen, W., Gao, J. et al. Impact of low molecular weight organic acids on heavy metal(loid) desorption in biochar-amended paddy soil. Environ Geochem Health46, 289 (2024). https://doi.org/10.1007/s10653-024-02064-6
Low molecular weight organic acids (LMWOAs) are key components in soil that influence the behavior of heavy metals. This study examines how biocharBiochar is a carbon-rich material created from biomass decomposition in low-oxygen conditions. It has important applications in environmental remediation, soil improvement, agriculture, carbon sequestration, energy storage, and sustainable materials, promoting efficiency and reducing waste in various contexts while addressing climate change challenges. More, a soil amendmentA soil amendment is any material added to the soil to enhance its physical or chemical properties, improving its suitability for plant growth. Biochar is considered a soil amendment as it can improve soil structure, water retention, nutrient availability, and microbial activity. More made from Paulownia biowaste, affects the interaction between LMWOAs and heavy metals, specifically cadmium (Cd) and antimony (Sb).
Four specific acids were studied: oxalic acid (OA), tartaric acid (TA), malic acid (MA), and citric acid (CA). These acids were found to lower soil pHpH is a measure of how acidic or alkaline a substance is. A pH of 7 is neutral, while lower pH values indicate acidity and higher values indicate alkalinity. Biochars are normally alkaline and can influence soil pH, often increasing it, which can be beneficial More as their concentrations increased. However, when biochar was added to the soil, it partially counteracted this pH reduction.
At low concentrations, these acids reduced the desorption of Cd from the soil, meaning less Cd was released. Conversely, at high concentrations, Cd desorption increased, with citric acid having the most significant effect. A similar pattern was observed for Sb, with citric acid again being the most effective.
Adding biochar to the soil influenced Cd and Sb differently. Biochar reduced Cd desorption but increased Sb desorption. It also increased the distribution coefficient (Kd) values for Cd, indicating a higher retention of Cd in the soil, while decreasing the Kd values for Sb, leading to greater Sb mobility.
This research highlights the complex interactions between LMWOAs, biochar, and heavy metals in soil. It underscores the potential benefits of biochar in managing Cd contamination but also warns of increased risks related to Sb desorption, which could have environmental implications.






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