Upper tropospheric NOx controls, in part, the distribution of ozone in
this greenhouse-sensitive region of the atmosphere. Many factors cont
rol NOx in this region. As a result it is difficult to assess uncertai
nties in anthropogenic perturbations to NO from aircraft, for example,
without understanding the role of the ether major NOx sources in the
upper troposphere. These include in situ sources (lightning, aircraft)
, convection from the surface (biomass burning, fossil fuels, soils),
stratospheric intrusions, and photochemical recycling from HNO3. This
work examines the separate contribution to upper tropospheric ''primar
y'' NOx from each source category and uses two different chemical tran
sport models (CTMs) to represent a range of possible atmospheric trans
port. Because aircraft emissions are tied to particular pressure altit
udes, it is important to understand whether those emissions are placed
in the model stratosphere or troposphere and to assess whether the mo
dels can adequately differentiate stratospheric air from tropospheric
air. We examine these issues by defining a point-by-point ''tracer tro
popause'' in order to differentiate stratosphere from troposphere in t
erms of NOx perturbations. Both models predict similar zonal average p
eak enhancements of primary NOx due to aircraft (approximate to 10-20
parts per trillion by volume (pptv) in both January and July); however
, the placement of this peak is primarily in a region of large stratos
pheric influence in one model and centered near the level evaluated as
the tracer tropopause in the second. Below the tracer tropopause, bot
h models show negligible NOx derived directly from the stratospheric s
ource. Also, they predict a typically low background of 120 pptv NOx w
hen tropospheric HNO3 is constrained to be 100 pptv of HNO3. The two m
odels calculate large differences in the total background NOx (defined
as the source of NOx from lightning + stratosphere + surface + HNO3)
when using identical loss frequencies for NOx. This difference is prim
arily due to differing treatments of vertical transport. An improved d
iagnosis of this transport that is relevant to NOx requires either mea
surements of a surface-based tracer with a substantially shorter lifet
ime than Rn-222 or diagnosis and mapping of tracer correlations with d
ifferent source signatures. Because of differences in transport by the
two models we cannot constrain the source of NOx from lightning throu
gh comparison of average model concentrations with observations of NOx
.