Irrigated land in southern Alberta is intensively managed, producing high yields but also requiring higher inputs, notably of nitrogen (N), than adjacent rainfed lands. The higher N inputs, combined with enhanced soil moisture, might stimulate nitrous oxide (N 2 O) emissions, but the influence of management on these emissions has not been widely studied. Our objective was to assess soil N 2 O emissions, along with those of carbon dioxide (CO 2 ) and of methane (CH 4 ), from irrigated cropping systems as influenced by source of N. We used a chamber technique to measure year-round emissions for 3 yr in long-term irrigated crop rotations receiving N as legume crop residues, non-legume crop residues, livestock manure or ammonium nitrate fertilizer. Unlike CO 2 fluxes, which peaked during the growing season, those of N 2 O showed no consistent seasonal trends; emissions occurred sporadically in bursts throughout the year. Depending on management practices, 0.4 to 4.0 kg N 2 O-N ha -1 yr -1 was emitted to the atmosphere. The amount of N 2 O emitted from the alfalfa system, averaged over all manure and fertilizer N amendments, was more than twofold that emitted from the corn system. The proportions of fertilizer-N released as N 2 O were 0.95% for the alfalfa system and 1.30% for the corn system. After livestock manure or legume residues were incorporated, soil CO 2 and N 2 O emissions appeared to be intertwined, but during the early spring N 2 O emissions were decoupled from CO 2 . Furthermore, N 2 O emissions were highly variable in space; at three of 54 chambers, N 2 O fluxes were consistently 12 to 55 times greater than those for other chambers in the same treatment. Such complexity conceals the underlying processes of net N 2 O production and transport to the soil surface.
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Ellert et al. (2008) studied this question.
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