77-2Temporal Variation of Methane and Nitrous Oxide Emissions From Dairy Slurries and Implications On Discrete Sampling.

See more from this Division: ASA Section: Environmental Quality
See more from this Session: Methane and Nitrous Oxide Emissions From Agricultural Systems.
Monday, October 22, 2012: 1:15 PM
Duke Energy Convention Center, Room 237-238, Level 2

Jeffrey D. Wood, School of Environmental Sciences, University of Guelph, Guelph, ON, Canada, Robert Gordon, Ontario Agricultural College, University of Guelph, Guelph, ON, Canada and Claudia Wagner-Riddle, 50 Stone Road E, University of Guelph, Guelph, ON, CANADA
Slurry storages are sources of methane (CH4) and nitrous oxide (N2O) emissions. Due to temporal flux variations, chamber measurements with discrete sampling may yield biased emission estimates, particularly when integrating over extended periods. This research quantified temporal variations in CH4 and N2O emissions from dairy slurries, and examined the potential implications on discrete sampling protocols. Six pilot-scale storages in Truro Nova Scotia, Canada, were filled with dairy slurries of different total solids content in May, 2010. Each storage was permanently fitted with a dynamic chamber and gas fluxes were measured continuously for 6 mo. Discrete sampling was simulated by extracting data from continuous hourly flux datasets at sampling intervals ranging from 1 through 21 d, and for each time-of-day. Long-term flux variation was observed for both gases with lags prior to the onset of increased emissions. When CH4 production was high, daily flux variations for incompletely encrusted slurries were linked with the dissipation of bubble-scums in the morning as the surface heated. In contrast, CH4 emissions from completely encrusted slurries were more episodic. Daily variations in N2O emissions were in phase with the surface temperature cycle when there was a crust >2 mo in age. This flux variation may have been due to decreased N2O solubility and increased rates of production at elevated temperatures. For discrete sampling intervals of 1-7 d, to achieve ±10% deviation (in total fluxes) from continuous measurements, samples should be taken between 1800-0800 h, and 1900-2000 h for CH4 (96% probability) and N2O (50% probability), respectively. Results demonstrated that temporal CH4 and N2O flux variations for manure storage systems are affected by surface conditions. When using discrete sampling to quantify emissions, sampling intervals should be ≤7 d. Biases in N2O emission estimates appear to be more sensitive to the time-of-day of sampling compared to CH4.
See more from this Division: ASA Section: Environmental Quality
See more from this Session: Methane and Nitrous Oxide Emissions From Agricultural Systems.