Emissions of nitric oxide (NO) were determined during late spring and summe
r 1995 and the spring of 1996 from four agricultural soils on which four di
fferent crops were grown. These agricultural soils were located at four dif
ferent sites throughout North Carolina. Emission rates were calculated usin
g a dynamic flow-through chamber system coupled to a mobile laboratory for
in-situ analysis. Average NO fluxes during late spring 1995 were: 50.9 +/-
47.7 ng N m(-2) s(-1) from soil planted with corn in the lower coastal plai
n. Average NO fluxes during summer 1995 were: 6.4 +/- 4.6 and 20.2 +/- 19.0
ng N m(-2) s(-1), respectively, from soils planted with corn and soybean i
n the coastal region; 4.2 +/- 1.7 nq N m(-2) S-1 from soils planted with to
bacco in the piedmont region; and 8.5 +/- 4.9 ng N m(-2) s(-1) from soils p
lanted with corn in the upper piedmont region. Average NO fluxes for spring
1996 were: 66.7 +/- 60.7 ng N m(-2) s(-1) from soils planted with wheat in
the lower coastal plain; 9.5 +/- 2.9 ng N m-(2) s(-1) from soils planted w
ith wheat in the coastal plain; 2.7 +/- 3.4 ng N m(-2) s(-1) from soils pla
nted with wheat in the piedmont region; and 56.1 +/- 53.7 ng N m(-2) s(-1)
from soils planted with corn in the upper piedmont region. An apparent incr
ease in NO flux with soil temperature was present at all of the locations.
The composite data from all the research sites revealed a general positive
trend of increasing NO flux with soil water content. In general, increases
in total extractable nitrogen (TEN) appeared to be related to increased NO
emissions within each site, however a consistent trend was not evident acro
ss all sites. (C) 2000 Elsevier Science Ltd. All rights reserved.