Managing Global Resources for a Secure Future

2017 Annual Meeting | Oct. 22-25 | Tampa, FL

198-2 Effect of Soil Freeze-Thaw Cycles on Nitrous Oxide Emissions.

See more from this Division: ASA Section: Environmental Quality
See more from this Session: Soil Carbon and Greenhouse Gas Emissions General Oral I (Student's Oral Competition)

Tuesday, October 24, 2017: 9:20 AM
Tampa Convention Center, Room 33

Mark Libby, University of Guelph, Ottawa, ON, CANADA, Andrew VanderZaag, Agriculture and Agri-Food Canada, Ottawa, ON, Canada, Edward G Gregorich, Neatby Bldg., Agriculture & Agri-Food Canada, Ottawa, ON, CANADA and Claudia Wagner-Riddle, School of Environmental Sciences, University of Guelph, Guelph, ON, CANADA
Abstract:
Freezing and thawing of soils leads to increased emissions of N2O; however, the link between soil freeze-thaw (FT) cycles and N2O emissions remains poorly understood. Production of N2O during FT is linked to anaerobic denitrification which, in turn, is strongly influenced by soil temperature, and availability of C and N. Our objective in this laboratory study was to characterize the relationship between N2O emissions and soil C and N dynamics during FT cycles. Significant fluctuations of soluble C and N concentrations were observed in soils treated with manure over the duration of the experiment relative to unamended controls in the 0-5 cm layer. For example, from the start of the 1000 hour freeze experiment, extractable C in the top 0-5 cm of the forage manure cores increased by 15 µg/g immediately before thaw, then increased by another 51 µg/g immediately after thaw; it then decreased by about 59 µg/g over the remaining thaw period. In contrast the C concentration in the control increased by 13 µg/g immediately after thaw but remained constant thereafter. Total N in the top 0-5 cm of the forage manure treatment was relatively constant until the later stages of thaw when concentrations decreased by about 29 µg/g. However, the proportion of NO3 and NH4 during these periods fluctuated greatly. In contrast, these proportions were relatively constant over the entire sampling period in the control treatment. When comparing the depth effect of C and N changes for each treatment over time, the 5-15 cm layers of soil remained relatively unchanged. These results suggest that most of the FT-induced N2O emissions from agricultural soils may originate in the upper 5 cm of soil. Differences observed between freezing durations, manure amendments, and preceding crop types will be discussed.

See more from this Division: ASA Section: Environmental Quality
See more from this Session: Soil Carbon and Greenhouse Gas Emissions General Oral I (Student's Oral Competition)