N/N and O/O stable isotope ratios of nitrous oxide produced during denitrification in temperate forest soils

Anaerobic incubations of upland and wetland temperate forest soils from the same watershed were conducted under different moisture and temperature conditions. Rates of nitrous oxide (N₂O) production by denitrification of nitrate () and the stable isotopic composition of the N₂O (δ¹⁵N, δ¹⁸O) were measured. In all soils, N₂O production increased with elevated temperature and soil moisture. At each temperature and moisture level, the rate of N₂O production in the wetland soil was greater than in the upland soil. The ¹⁵N isotope effect (ε) _{(product − substrate)} ranged from −20‰ to −29‰. These results are consistent with other published estimates of ¹⁵N fractionation from both single species culture experiments and soil incubation studies from different ecosystems.A series of incubations were conducted with ¹⁸O-enriched water (H₂O) to determine if significant oxygen exchange (O-exchange) occurred between H₂O and N₂O precursors during denitrification. The exchange of H₂O-O with nitrite () and/or nitric oxide (NO) oxygen has been documented in single organism culture studies but has not been demonstrated in soils prior to this study. The fraction of N₂O-O derived from H₂O-O was confined to a strikingly narrow range that differed between soil types. H₂O-O incorporation into N₂O produced from upland and wetland soils was 86% to 94% and 64% to 70%, respectively. Neither the temperature, soil moisture, nor the rate of N₂O production influenced the magnitude of O-exchange. With the exception of one treatment, the net ¹⁸O isotope effect (ε_net) _{(product-substrate)} ranged from +37‰ to +43‰.Most previous studies that have reported ¹⁸O isotope effects for denitrification of to N₂O have failed to account for the effect of oxygen exchange with H₂O. When high amounts of O-exchange occur after fractionation during reductive O-loss, the ¹⁸O-enrichment is effectively lost or diminished and δ¹⁸O-N₂O values will be largely dictated by δ¹⁸O-H₂O values and subsequent fractionation. The process and extent of O-exchange, combined with the magnitude of oxygen isotope fractionation at each reduction step, appear to be the dominant controls on the observed oxygen isotope effect. In these experiments, significant oxygen isotope fractionation was observed to occur after the majority of water O-exchange. Due to the importance of O-exchange, the net oxygen isotope effect for N₂O production in soils can only be determined using δ¹⁸O-H₂O addition experiments with δ¹⁸O-H₂O close to natural abundance.The results of this study support the continued use of δ¹⁵N-N₂O analysis to fingerprint N₂O produced from the denitrification of . The utilization of ¹⁸O/¹⁶O ratios of N₂O to study N₂O production pathways in soil environments is complicated by oxygen exchange with water, which is not usually quantified in field studies. The oxygen isotope fractionation observed in this study was confined to a narrow range, and there was a clear difference in water O-exchange between soil types regardless of temperature, soil moisture, and N₂O production rate. This suggests that ¹⁸O/¹⁶O ratios of N₂O may be useful in characterizing the actively denitrifying microbial community.