Scientific Issues in Oxidant and Aerosol Modeling
Breakout Session Summary
DOE Atmospheric Chemistry Program Annual Meeting, February 1998
Chaired by
Joyce Penner, University of Michigan, Ann Arbor
Dan Imre, Brookhaven National Laboratory
1. State of the Models
To update information and provide a basis for further discussion, an
inventory of current models and their capabilities was constructed. The
resulting table is shown below. Further information on GChM-O, MOZART,
IMAGES, and an additional chemical-transport model is given in the breakout
session report titled "Progress in Global and Hemispheric Modeling of Oxidants
and Aerosols."
|
Model
|
Scale Resolved
|
Thrust
|
Aerosols
|
|
STEM
|
1o by 1o
|
Oxidant cycle
|
Size distribution
|
|
GChM-O (global)
|
1o by 1o
|
Sulfur cycle
|
Size distribution
|
|
GChM (regional)
|
5 km by 5 km
|
Oxidants
|
Size distribution
|
|
BOX
|
NA
|
Oxidants
|
No
|
|
IMPACT
|
1o by 1o
|
Oxidants
|
Not yet
|
|
GRANTOUR
|
300 km by 300 km
|
VOCs
|
Not yet; separate
|
|
MOZART
|
2.5o by 2.5o
|
Oxidants
|
Not yet
|
|
IMAGES
|
5o by 5o
|
Oxidants
|
-
|
Aside from the regional version of GChM, which is in early stages of
construction, the ACP chemical models noted above address scales appropriate
for global studies. The global scales are considerably larger than the
regional scales addressed in most of the field experiments in which ACP
participates. As a result, present ACP modeling activities do not interface
well with the needs of ACP field observational efforts. Many of the above
models could in principle be adapted to address the scales of about 5 km
by 5 km that would be necessary for regional-scale studies. A simple scale
shrinkage is usually inappropriate or difficult, however, because new processes
that are important only on a local scale would have to be introduced. Moreover,
the present models resulted from many years of research, are used in global
studies for programs other than ACP, and strongly represent the current
interests of the principal investigators. Hence, very few of these global
models are likely to be adapted for regional-scale studies in the near
future.
2. Scientific issues that ACP might address
Several overarching scientific questions are addressed in this report:
What is the best method to evaluate models?
To what extent can urban plumes be used to test understanding?
How important is it to represent heterogeneous chemistry?
How important are the scales of interaction? What is the importance
of nonlinearity of chemical processes in going from plume to urban, regional,
and larger scales?
2.1 Methods to Evaluate Models; Model-Measurement Coupling
Several strategies and activities were mentioned:
a. Measurements upwind and downwind of an area being modeled should
be attempted.
b. Ratios of species concentrations estimated in the models should
be compared to measurements.
c. Models should be used to design the best location for measurements
and to derive diagnostic indicators that may transcend scale. This latter
issue was emphasized because many of the models in the ACP program are
not well suited to being tested through comparison with data from the field
programs.
d. The models should be used to calculate the concentration of intermediate
species so that researchers making measurements will know how well they
need to be measured.
To test the models with measurements, a number of issues need to be addressed:
a. Additional, more fundamental information might be needed, such as
VOC oxidation leading to aerosol formation.
b. An intercomparison of models should be carried out to evaluate their
treatment of VOCs.
c. The optimal vertical resolution in models needs to be investigated,
which is particularly important for studies of nighttime chemistry.
d. The importance of aerosol-oxidant interactions needs to be investigated.
It is not known whether there are testable consequences that result from
this interaction.
Aerosol measurement capabilities for ACP field programs are currently being
enhanced. Modeling activities in conjunction with this field program should
be carried out.
2.2 Issues Involved in Understanding the Chemistry of Urban Plumes
Several questions were put forward that might be the focus of future
field campaigns:
a. To what extent do oxidants increase nucleation and secondary aerosol
formation?
b. Does the presence of aerosols exert a significant effect on the
chemistry? How would it do so? For example, does an optically dense boundary
layer change the actinic flux and therefore the photochemistry?
c. Do the models correctly predict the growth of pre-existing particles
and nucleation of new particles? It was suggested that knowledge is particularly
primitive in this area.
d. What is the effect of industrial chlorine emissions and/or the presence
of sea salt?
2.3 Issues in Incorporating Aerosols, Especially The Representation
of Heterogeneous Chemistry
Scientific knowledge is still lacking on several fundamental processes,
making it difficult to incorporate the processes into models:
a. What are the rates of reaction of NO2 with aerosol particles
such as dust and what are the products?
b. Is there special chemistry taking place at the liquid interface
on aerosol surfaces? Models could be used to address how important this
might be.
c. Is the production of HONO on aerosol surfaces important?
d. A need exists for data on the properties of aerosol surfaces and
the rates of chemical transformation in these surfaces. The surface composition
properties of ambient aerosols is not known.
e. Although the gaseous phase processes that produce the precursors
of sulfate and nitrate aerosols seem to be well understood, the level of
knowledge for corresponding processing involving organics is much lower.
f. What are the organics in aerosols? How are these particulate organics
created? What is the role of organics in the formation of new particles?
2.4 Scales of interaction and the importance of nonlinearity of chemical
processes in going from plume to urban, regional, and larger scales
Field measurements typically require models with grid scales of less
than or equal to 5 km but very few of the models in the program typically
are run at this scale. Two approaches were discussed under this topic:
a. One suggestion is that ACP devote resources to develop an all-purpose
or "community" model that could be used by ACP researchers. A "plug-and-play"
model composed of individual modules that could be modified by the users
could be developed. Experience by the U.S. Environmental Protection Agency
(EPA) indicates that the level of resources required might be quite large
and that the amount of time needed to achieve a sufficiently user-friendly
model could be up to 10 years. An EPA effort has been devoted to producing
a plug-and-play model that can operate on various scales, even within a
single run, be able to utilize various types of emission inventory datasets,
meteorological datasets, etc. This model, which is due to be released in
late 1998, can be made available to ACP researchers.
b. Another suggestion is that ACP enlist the large-scale modelers to
apply their models in a "box model" approach to try to simulate a particular
data set. This approach would allow both a model-to-model intercomparison
and a models-measurements comparison. Careful thought would be needed initially
on identifying a set of measurements that would help constrain the models.
The meeting ended with the general feeling that ACP has a number of important
scientific questions that need to be addressed. Several of these will become
amenable to testing our scientific understanding in the future.