Biochar can reduce nitrate (NO 3 − ) leaching from soil, yet typically only at high, uneconomic application rates. Therefore, biochar should be produced and modified to achieve high sorption capacity. Increased NO 3 − sorption at acidic pH has been reported. However, the sorption mechanisms and potential of biochar acidification to reduce nitrate leaching remain unexplored. Here, NO 3 − sorption was quantified at soil-relevant pH of 5 and 7 on woody biochars produced at highest treatment temperatures (HTT) of 400–900 °C. Sorption capacities ranged between 700 and 6200 mg NO 3 − -N kg −1 at pH 5 and between 200 and 2500 mg NO 3 − -N kg −1 at pH 7. Thus, NO 3 − sorption to biochar might be higher in acidic compared to neutral soils and can be maximized by producing biochars at HTT ≥750 °C. Correlation of sorption data with content of surface functional groups and proxies for biochar aromaticity suggest that NO 3 − is sorbed to protonated aromatic structures in biochars produced at >500 °C, while NO 3 − might sorb to protonated functional groups in biochar produced at 400 °C. Further, biochar acidification under NO 3 − enrichment was tested to reduce NO 3 − leaching. Both in aqueous suspension and in soil columns, full NO 3 − release from KNO 3 -enriched industrial biochar was prevented by biochar acidification, i.e., combined HNO 3 +KNO 3 enrichment. In soil with pH 5.7 or pH 7.4, only acidified biochar reduced NO 3 − leaching by up to 23 % and 12 %, respectively, compared to the soil-only control. Thus, acidification could be an interesting approach to produce biochar-based fertilizers with controlled NO 3 − release.
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Grafmüller et al. (2025) studied this question.
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