Li, et al (2024) Sb/As immobilization and soil function improvement under the combined remediation strategy of modified biochar and Sb-oxidizing bacteria at a smelting site. Journal of Hazardous Materials. https://doi.org/10.1016/j.jhazmat.2024.134302

Soil pollution from antimony (Sb) and arsenic (As) at Sb smelting sites presents a significant environmental challenge. Traditional methods often focus solely on immobilizing these contaminants, overlooking the crucial aspect of restoring soil functionality. A recent study explores a dual approach using Fe/H2O2-modified biochar (Fe@H2O2-BC) and Sb-oxidizing bacteria (Bacillus sp. S3) to tackle both these issues effectively.

Fe@H2O2-BC has proven to significantly immobilize Sb and As, reducing their leaching toxicity to extremely low levels over a year-long period. This modified biochar not only curtails the availability of these toxic metalloids by up to 98% but also enhances the soil’s aggregate structure, pore characteristics, and water-holding capacity. Acting as a pH buffer and a reservoir for organic carbon, Fe@H2O2-BC improves the soil’s carbon substrate availability which is crucial for bacterial activity.

In parallel, the introduction of Bacillus sp. S3, a bacterium capable of oxidizing Sb(III) to Sb(V) and As(III) to As(V), initiates a beneficial transformation in the soil. This bacterial action not only aids in further reducing the bioavailability of these toxicants but also reshapes the microbial community within the soil. It particularly increases the relative abundance of nitrogen and sulfur-cycling bacteria, thereby enhancing the overall soil functionality.

The combined application of Fe@H2O2-BC and Bacillus sp. S3 not only addresses the immediate concern of contaminant immobilization but also promotes a longer-term ecological restoration of the soil at Sb smelting sites. This innovative approach offers a promising solution for environmental remediation projects, balancing immediate detoxification needs with the restoration of healthy soil ecosystems.



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