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a Soil and Water Science Dep., Tropical Research and Education Center, Univ. of Florida, 18905 SW 280th St., Homestead, FL 33031
b USDA-ARS, 24106 N. Bunn Rd., Prosser, WA 99350
* Corresponding author (yunli@mail.ifas.ufl.edu).
Emission of N as NH3 is the primary gaseous loss of N from N sources applied to soils. Knowledge of NH3 volatilization, however, in relation to temperature is incomplete. Soils used in this study were a Biscayne marl soil (BMS) and Krome gravelly loam (KGL) from Florida, and Quincy fine sand (QFS) and Warden silt loam (WSL) soils from Washington. These soils were amended with either KNO3, NH4NO3, (NH4)2SO4, or urea, and incubated at 11, 20, or 29°C under 20 or 80% field capacity (FC) soil water regimes. A change in the rate of NH3 emission corresponding to a 9°C change in temperature is expressed as the temperature quotient (Q9), which describes the temperature effect on rates of NH3 volatilization. At 20°C, the cumulative NH3 emission at 20% FC was up to 8.1-fold greater than that at 80% FC. The Q9 values of NH3 emission from the WSL soil were up to 10-fold greater than those from the other three soils amended with either (NH4)2SO4 or NH4NO3. The Arrhenius activation energy (Ea) was about 188 J mol–1 for the WSL soil but
42 J mol–1 for the other soils. Volatilization from the WSL soil was highly temperature dependent. These results indicate that Q9 and Ea could be used as indices for N management for crop production to minimize NH3 emissions. Further research is needed, however, to verify the above relationships across a wide range of soils and agroclimatic regions.
Abbreviations: BMS, Biscayne marl soil CAE, cumulative ammonia emission FC, field capacity IPAV, isothermal point of ammonia volatilization KGL, Krome gravelly loam QFS, Quincy fine sand WSL, Warden silt loam
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