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Ammonia and nitrous oxide emissions from a field Ultisol amended with tithonia green manure, urea, and biochar

Short-term mitigation of ammonia (NH 3 ) and nitrous oxide (N 2 O) emissions by biochar soil amendments has been reported, but limited knowledge of the mechanisms, particularly those associated with long term changes, remain relatively unknown. In order to investigate potential mechanisms and residu...

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Published in:Biology and fertility of soils 2019-02, Vol.55 (2), p.135-148
Main Authors: Fungo, Bernard, Lehmann, Johannes, Kalbitz, Karsten, Thionģo, Margaret, Tenywa, Moses, Okeyo, Irene, Neufeldt, Henry
Format: Article
Language:English
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Summary:Short-term mitigation of ammonia (NH 3 ) and nitrous oxide (N 2 O) emissions by biochar soil amendments has been reported, but limited knowledge of the mechanisms, particularly those associated with long term changes, remain relatively unknown. In order to investigate potential mechanisms and residual effect of biochar on NH 3 and N 2 O emission, a 3-year field trial was set up on an Ultisol in western Kenya with a three-replicate full factorial treatment structure. The factors investigated include the following: biochar (from eucalyptus wood, pyrolyzed at 550 °C, applied once before the start of the experiment at either 0 or 2.5 t ha −1 ); tithonia green manure applied at the start of each season at either 0, 2.5, or 5.0 t ha −1 ; mineral nitrogen (N) (as urea applied each season at either 0 or 120 kg N ha −1 ). NH 3 as well as N 2 O emission and water-filled pore space (WFPS) were monitored throughout the 3 years. In the third year, soil mineral nitrogen (exchangeable NH 4 + and NO 3 − ) contents were measured. Biochar reduced cumulative emissions of NH 3 and N 2 O by 47 ± 5 and 22% ± 3, respectively, over the 3 years. Over the 3 years, the effect size of biochar was reduced by 53 and 59% for NH 3 and N 2 O, respectively, indicating that the residual effect of biochar on NH 3 and N 2 O persists at least up to 3 years under field conditions. Tithonia and urea additions increased both gas emissions by 13–68% compared to the control. Combination of the three amendments reduced cumulative NH 3 emissions by 18 ± 3%, but had no effect on cumulative N 2 O. Our results show that biochar can influence emissions of NH 3 and N 2 O longer than most previous studies have reported but is not explained by N dynamics. Other mechanisms such as direct interactions with oxidized biochar surfaces could be more likely to account for the residual effect of biochar on NH 3 and N 2 O in agricultural soils.
ISSN:0178-2762
1432-0789
DOI:10.1007/s00374-018-01338-3