2008 Joint Meeting of The Geological Society of America, Soil Science Society of America, American Society of Agronomy, Crop Science Society of America, Gulf Coast Association of Geological Societies with the Gulf Coast Section of SEPM

Paper No. 6
Presentation Time: 8:00 AM-6:00 PM

Nitrous Oxide Gas Fluxes in a Potato Field Following Application of Urea and Coated Urea Fertilizers


VENTEREA, Rodney T.1, ROSEN, Carl J.2, MCNEARNEY, Matt2, WILSON, Melissa2 and DOLAN, Michael1, (1)Soil and Water Mgmt Research Unit, USDA-ARS, 1991 Upper Buford Circle, 439 Borlaug Hall, St. Paul, MN 55108-6028, (2)Dept. of Soil, Water and Climate, University of Minnesota, 1991 Upper Buford Circle, 439 Borlaug Hall, St. Paul, MN 55108-6028, venterea@umn.edu

Application of urea and other forms of nitrogen (N) fertilizer can generate atmospheric emissions of nitrous oxide (N2O), which is a potent greenhouse gas. Field experiments were conducted on a loamy sand soil in Becker, Minnesota to evaluate the effects of soluble and coated forms of urea on N2O fluxes in a potato field. The following treatments, all receiving a total of 270 kg/ha N were tested: 1) Conventional urea with split applications at emergence and 5 additional applications; 2) Polymer coated urea (ESN, 44-0-0, Agrium, Inc.); 3) Polymer coated urea (PCU, 42-0-0, Kingenta Co.); and 4) Sulfur coated urea (SCU, 35-0-0, Kingenta Co.). The coated urea treatments were applied 6 days prior to planting and then immediately incorporated. All treatments included 45 kg/ha N as diammonium phosphate at planting as part of the total N applied. Closed chambers were used to measure soil-to-atmosphere fluxes of N2O on 25 dates from 27 April (one day after planting) through 14 September 2007. On each sampling date, measurements were made for one hour in 3-plot replicates of each treatment; each using paired gas-flux chambers with one chamber placed on the hill and the other in the inter-row. Flux of N2O was estimated from the rate of increase in N2O concentration within the chamber. The soluble urea treatment displayed a gradual increase in flux starting at 24 days after planting (DAP) and continued until reaching a maximum at 47 DAP. This increase appears to have been the result of a 110 kg/ha N application as soluble urea at 19 DAP. None of the other treatments displayed such an increase. Integration of the flux data across the entire sampling period resulted in estimates of 6.9, 5.2, 4.7, and 4.2 kg N2O-N ha-1 emitted from soluble urea, Agrium ESN, Kingenta PCU, and Kingenta SCU, respectively.