Previous field research in Alberta has suggested that denitrification occurs mostly when soil thaws in the spring, with associated soil water saturation. Our objective was to determine if denitrification and N 2 O emission in fact take place in cold, thawing soil in the field. Denitrification and N 2 O flux were measured in two springs and the intervening summer. Cylinders were placed in soil in November, 1988, and 57 kg N ha −1 of 15 Nlabeled KNO 3 was added. Soil 15 N mass balance technique showed 23 kg N ha −1 of added-N was lost by 15 May 1989. Gas trappings were made (28 March to 29 April) and nearly all of the N 2 O emission (3.5 kg N 2 O-N ha −1 ) occurred during an 11-d period of thaw. The accumulated N 2 O flux from 20 June to 31 August was small (0.5 kg N 2 O-N ha −1 , or less); during that time there were no rainfall events intense enough to produce water saturated soil. In 1990, 15 N-labeled KNO 3 (100 kg N ha −1 ) was applied on 26 March (outset of the thaw) and mass balance showed 32.7 kg N ha −1 of added-N was lost by 7 May. A flux of 16.3 kg N 2 O-N ha −1 occurred largely in a 10-d period during and immediately after soil thaw. The N 2 O emitted from soil left a considerable fraction of the lost N unaccounted for. This unaccounted N was most likely lost as gaseous N other than N 2 O (e.g., N 2 ). We conclude that large amounts of soil nitrate may be denitrified, with smaller amounts emitted as N 2 O, as the soil thaws and soon thereafter.
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Nyborg et al. (1997) studied this question.
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