4.7 Article

Activating soil nitrification by co-application of peanut straw biochar and organic fertilizer in a rare earth mining soil

Journal

SCIENCE OF THE TOTAL ENVIRONMENT
Volume 866, Issue -, Pages -

Publisher

ELSEVIER
DOI: 10.1016/j.scitotenv.2023.161506

Keywords

Rare earth mining; Ammonium; Biochar; Nitrification; Acid neutralization capacity; Nitrosomonas europaea

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Intensive mining activities in southern China have led to significant ammonium contamination in tailing soils. This study explored the feasibility of using different additives to remove ammonium from rare earth mining soil. The application of peanut straw biochar, CaCO3, and organic fertilizer activated both ammonia volatilization and soil nitrification processes.
The intensive mining activities to extract rare earth elements from ion-adsorption rare earth deposits have introduced massive amounts of ammonium into the tailing soils in southern China. Compared to the ubiquitous soil nitrification in cropland, forest, and grassland soils, however, there is no feasible strategy to alleviate the ammonium contamination in tailing soil. Herein, the feasibility to remove ammonium by adding ammonium adsorbents (e.g., biochar, activated carbon, and zeolite), alkaline materials, and organic fertilizer to the rare earth mining soil was explored. The amend-ment of rice straw biochar, activated carbon, or zeolite in combination with CaCO3 and organic fertilizer showed no significant effect on ammonium removal due to their limited capacity to elevate soil pH. However, the co -application of peanut straw biochar (PSBC), CaCO3, and organic fertilizer activated both the ammonia volatilization and soil nitrification processes. Specifically, the three components functioned as follows: organic fertilizer supplied ac-tive ammonia-oxidizing bacteria (AOB); PSBC stimulated AOB proliferation by elevating soil pH above 7.75; CaCO3 ameliorated soil acidity and reduced the lag time for activating soil nitrification. The soil ammonium removal and nitrate accumulation rates were positively correlated to the acid neutralization capacity of PSBC prepared at 400 degrees C-800 degrees C. The qPCR and microbial community analysis results indicated that Nitrosomonas europaea was the dom-inant AOB that was responsible for enhanced soil nitrification. Our findings pave the way for developing cost-effective strategies to remediate ammonium contamination in rare earth mining soils.

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