Fall application of anhydrous ammonia in Manitoba is common but its impact on nitrous oxide (N 2 O) emissions is not well known. A 2-yr study compared application before freeze-up in late fall to spring pre-plant application of anhydrous ammonia on nitrous oxide (N 2 O) emissions from a clay soil in the Red River Valley, Manitoba. Spring wheat (Triticum aestivum L.) and corn (Zea mays L.) were grown on two 4-ha fields in 2011 and 2012, respectively. Field-scale flux of N 2 O was measured using a fluxgradient micrometeorological approach. Late fall treatment did not induce N 2 O emissions soon after application or in winter likely because soil was frozen. Application time did alter the temporal pattern of emissions with late fall and spring pre-plant applications significantly increasing median daily N 2 O flux at spring thaw and early crop growing season, respectively. The majority of emissions occurred in early growing season resulting in cumulative emissions for the crop year being numerically 33% less for late fall than spring pre-plant application. Poor yield in the first year with late fall treatment occurred because of weed and volunteer growth with delayed planting. Results show late fall application of anhydrous ammonia before freeze-up increased N 2 O emissions at thaw and decreased emissions for the early growing season compared to spring pre-plant application. However, improved nitrogen availability of late fall application to crops the following year is required when planting is delayed because of excessive moisture in spring. (2012) concluded anhydrous ammonia induces the largest emissions of N 2 O from cropped soils of all fertilizer N products. In Manitoba, however, with a lower application rate than other studies included in metaanalyses, Burton et al. (2008) reported no greater emissions with 80 kg N ha -1 anhydrous ammonia than urea applied at planting to spring wheat (Triticum aestivum L.). These studies highlighted the importance of developing strategies to reduce N 2 O emissions from anhydrous ammonia.
Lower Nitrous Oxide Emissions from Anhydrous Ammonia ApplicationAnhydrous ammonia is commonly applied in the fall in the Northern Great Plains of Canada because of lower retail cost (MAFRD, 2007), greater availability over time, and generally drier soil conditions than at spring pre-plant or at spring planting. However, nitrification of early fall applied anhydrous ammonia can occur before winter freeze-up (Malhi and McGill, 1982;Tiessen et al., 2006). To minimize nitrification and thus nitrate accumulation before freeze-up, it is recommended in Manitoba that fall N fertilizer applications are banded and delayed until soil temperatures fall below 5°C (MAFRD, 2007).Applying N in late fall when soil is cool and close to the onset of freezing may not result in increased emissions compared to Abbreviations: TGA, trace gas analyzer; TGAS-Man, Trace Gas Manitoba research site; WFPS, water-filled pore space.
Journal of Environmental Quality
ATMOSPHERIC POLLUTANTS AND TRACE GASES TECHNICAL R...