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Dep. of Biology and the Ecology Center, Utah State Univ., Logan, UT 84322-5500
Dep. of Soil Science, Univ. of California, Berkeley, CA 94720
*Corresponding author (jstark{at}cc.usu.edu).
ABSTRACT
In N cycling studies, soil NO–3 pools are typically labeled by adding solutions containing 15NO–3. The associated increase in moisture may perturb the system and preclude measurement of N-cycle processes in relatively dry soils. This study examined the feasibility of using 15N-NO gas to label soil NO–3 pools without addition of water. Soil samples (ashed, oven dry, or with soil water potentials ranging from –3.7 to –0.2 kJ kg–1 [1 MPa = 1 kJ kg–1]) were exposed to various quantities of NO gas (0–600 mg NO-N kg–1 soil). Maximum recovery of NO-N in soil NO–2 and NO–3 pools occurred after <2 h of exposure to the gas and ranged from
40% for moist soil samples to >90% in ashed soil. Relative increases in either NO–2 or NO–3 depended on the initial NO concentration and the soil treatment. In general, higher soil moisture resulted in higher NO–2/NO–3 ratios. Within 20 h of addition of 15NO, almost all of the NO–2 was converted to NO–3; however, a small amount was also converted to NH+4 and organic N. These results demonstrate that 15NO can be used to label soil NO–3 pools without addition of water. Depending on the objectives of the study, however, it may be necessary to monitor the enrichment of a variety of other soil N pools as well.
Received for publication February 22, 1995.
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