Background/Question/Methods We report on a novel pathway in the terrestrial nitrogen (N) cycle that couples anaerobic ammonium oxidation with iron(III) reduction. The pathway, called Feammox, results in the production of dinitrogen (N
2) gas or nitrite (NO
2-). Nitrite produced via Feammox can be subsequently reduced to nitrous oxide (N
2O) gas, N
2, or ammonium (NH
4+) via dissimilatory NO
2- reduction or abiotic oxidation of iron(II). We conducted three experiments. As a general test of anaerobic NH
4+ oxidation we added equimolar
15NH
4+ and natural abundance NO
2- (
14NO
2-) to iron (Fe)-rich tropical forest soils. Acetylene (C
2H
2) was added as an inhibitor of N
2O reduction to N
2 and of anammox to a second set of isotopically labeled samples. This method can distinguish direct N
2 production via Feammox or anammox from N
2 produced from denitrification of Feammox-generated NO
2-. Changes in the
15-14N
2 mole fraction could result from anammox or Feammox, whereas changes in the
15-15N
2 mole fraction indicated Feammox. In the presence of C
2H
2, increases in the
15N enrichment of N
2 suggest direct N
2 production via Feammox. In the second experiment we added NH
4+ only or NH
4+ with Fe(III) to pre-incubated anaerobic slurries to test for NO
2- production. We explored the potential for Feammox to produce N
2 in a third experiment. Pre-incubated soil slurries were amended with
15NH
4+ (24 h only) or
15NH
4+ with Fe(III) (6 and 24 h) in stoichiometric equivalency. Dinitrogen was measured immediately after collection on an isotope ratio mass spectrometer.
Results/Conclusions
There was no 15-14N2 produced during the 96 h incubation with or without C2H2 added. However, we measured considerable 15-15N2 production. Acetylene addition (24 h only) increased the 15-15N2 mole fraction suggesting that some N2 was produced directly via Feammox and did not result from anammox or biological denitrification of NO2-. In the second experiment, aqueous NO2- concentrations were significantly higher in samples that had received NH4+ and Fe(III) than soils that had received only NH4+ after 22 hours. A similar trend occurred at 3 h, but the differences were not statistically significant. In the third experiment, we measured significantly higher 15-15N2 mole fraction in the 15NH4+ and Fe(III) treatment than in the 15NH4+ only or blank (soil free) treatments. Using mass balance calculations we determined that over 20% of the added NH4+ was lost as N2 via Feammox. Our results suggest that Feammox occurs in these upland soils, and has the potential to produce significant N2 and NO2-.