v>EPA
                                 United States
                                 Environmental Protection
                                 Agency
                                                               Environmental Sciences Research x
                                                               Laboratory                   '/
                                                               Research Triangle Park NC 27711
                                 Research and Development
                                                               EPA-600/S3-82-016a  June 1982
                             Project Summary
                                 Outdoor  Smog Chamber
                                 Experiments to Test
                                 Photochemical Models

                                 H. E. Jeffries, R. M. Kamens, K. G. Sexton, and A. A. Gerhardt
o
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                      V
            The smog chamber facility of the
          University of North Carolina (Chapel
          Hill) was used in a study to provide
          experimental data for developing and
          testing kinetic mechanisms of photo-
          chemical smog formation. The smog
          chamber,  located outdoors in  rural
          North Carolina, is an A-frame structure
          covered with Teflon film. Because the
          chamber is partitioned into two sec-
          tions, each with a volume of 156 m3,
          two experiments can be conducted
          simultaneously. The dual chamber is
          operated under  natural conditions of
          solar radiation, temperature, and rela-
          tive humidity. In this study, 115 dual
          all-day experiments were conducted
          using NOX and  various organic spe-
''/?,,        cies. The organic compounds investi-
  ^>     gated  included various paraffins,
          olefins,  aromatics,  and  oxygenates,
          both singly and in mixtures of two or
          more components-.
            This report describes the data col-
          lected over a three-year period of the
          study.  The experimental procedures
          and analytical methods  used in this
          study and the limitations and uncer-
          tainties of the data are discussed. Guid-
          ance for modeling of the data is also
          given, including a detailed discussion
          of how to estimate photolytic rate
          constants from  the available ultravi-
          olet and total solar radiation data and
          how to treat such chamber artifacts as
          dilution, wall sources and losses of
          pollutants, and reactivity of the back-
          ground air.
  This Project Summary was devel-
oped by EPA's Environmental Scien-
ces Research Laboratory. Research
Triangle Park. NC. to announce key
findings of the research project that
is fully documented in a separate re-
port of the same title (see Project Re-
port ordering information at back).

Introduction
  A long-term goal of EPA's research
program  is to develop  urban and
regional air quality simulation models
(AQSMs) for planning accurate and
scientifically-defensible control strat-
egy. Because the pollutants with the
greatest health effects are secondary
pollutants, formed by  chemical  reac-
tions  occurring in the atmosphere, an
understanding of the chemistry that pro-
duces these pollutants is critical to the
development of AQSMs. In recent years
significant effort  has been made to
explain the chemical transformations
that occur in photochemical smog sys-
tems  and to develop chemical kinetic
mechanisms that  can  be  used in the
AQSMs to  explain the formation of
ozone and other secondary pollutants.
  Despite the progress that has been
made towards an  understanding of the
chemical processes that lead to the for-
mation of photochemical smog, there is
still a need for a  comprehensive and
well-characterized data base to serve as
a benchmark from which kinetic models
may be experimentally tested. The pur-
pose of this study was to acquire such a

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data base. Because the ultimate goal of
this research is to produce kinetic mod-
els  that  can  simulate  the processes
occurring in the polluted environment,
it was important to acquire the data
under conditions that were as closely
representative as  possible of actual
atmospheric conditions.  For this reason,
the dual outdoor  smog chamber facility
of the University  of North Carolina,
which is operated using actual sunlight,
temperature, and water vapor condi-
tions, was selected for  this study. The
study was performed by the University
of North Carolina  (Chapel Hill)  under
Cooperative Agreement No. 805843.

Procedure
  The experiments were conducted in
an  outdoor A-frame smog chamber
covered with Teflon (registered trade-
mark). A Teflon panel divided the
chamber into two sections,  each with a
volume of 156 cm3. The chamber was
purged overnight  with the relatively
clean air that prevails at  the site in rural
North Carolina. Shortly  before sunrise,
the chamber doors were sealed and the
reactants of interest were slug-injected
into the chamber. The usual procedure
was to inject the same concentration of
NOX into both sides of the chamber and
then vary the concentration or identity
of the hydrocarbon in the two sides of
the chamber. The chemical constituents
and physical  parameters were  moni-
tored from the time the reactants were
injected until about 6:00 p.m. EOT. A
computer-based data-acquisition and
control system was used to acquire, pro-
cess, and record data from the chamber
instrument system. Instruments were
used  to measure  NO,  NO2, 03, PAN,
HNO3, alkyl nitrates,  HOOH, CO, indi-
vidual hydrocarbons, aliphatic and aro-
matic aldehydes  and other  oxygenates,
such as phenol, acetone, and methyle-
thylketone. Standard  meteorological
instruments  were used to measure
solar radiation,  ultraviolet radiation,
temperature, and dew point.
  The experiments took place  between
May 1977 and August 1980. Of the 115
dual runs conducted in this study, 98
were performed  during the June-
through-October smog  season and 17
were conducted  during the winter and
spring period from November through
May.  The reactivities of 18 individual
organic compounds and 14 mixtures of
two or more organic species were inves-
tigated. The organic compounds and the
mixtures  included in  this study are
shown in Table 1.
Table 1.     Organic Components Used in the Outdoor Smog Chamber Experiments.


         Single Components                           Mixtures
         Formaldehyde
         Acetaldehyde
         Biacetyl
         Methyl glyoxal
         Benzaldehyde
         Methylethylketone
         Acetone
         Ethylene
         Propylene

         Butane
         Pentane
         2,3-Dimethylpentane
         Octane

         Toluene

         o-Xylene

         Isoprene
         Alpha-Pinene

         Butyl nitrate
    Formaldehyde/MEK
    Formaldehyde/A cetone
    Formaldehyde/Benzaldehyde

    Ethylene/Formaldehyde
    Ethylene/A cetaldehyde
    Ethylene/ Trichloroethylene
    Ethylene/Trans-2-butene
    Prop ylene/Formaldeh yde
    Propylene/Acetaldehyde
    Prop ylene/B utane
    Propylene/ Toluene

    Toluene/Benzaldehyde

    A Ipha -Pinene/'Isoprene


    Urban Mix
Results
  The data collected in this study are
available in several forms. Included in
the project report are hourly data  list-
ings and plots of  concentration as  a
function of time for 10 experiments that
a re representative of the entire data set.
In general, these runs have reasonably
complete product information, were
conducted  under  favorable sunlight
conditions, and offer the modeler a wide
range of initial conditions. Also con-
tained in the  report are a collection of
plots illustrating interesting features of
the data set. Included in the report are
illustrations of the following:
(1)  Selected  n-butane, n-pentane, n-
    octane and 2,  3-dimethylbutane
    runs and the carbon-containing
    products identified in these experi-
    ments.
(2)  Selected  aromatic runs,  including
    toluene/NOx  runs, in which  the
    intent of  the  experiments  was to
    determine the relative  yields of
    benzaldehyde  and cresol  and to
    identify ring-cleavage products
    such as methyl glyoxal.
(3)  Experiments demonstrating  the
    effect of  adding formaldehyde or
    acetaldehyde to the propylene/NO*
    system.
(4)  Experiments to assess the effect of
    relative humidity on the propylene/
    NOX system. In these experiments
    the air on one side of the chamber
    was dried  by passing it through
    refrigeration cooling coils and the
    other  side of the chamber was left
    undried.
  In addition to the data for selected
runs that are included in the text of the
project report, the data are also avail-
able as: (1) a computer-readable mag-
netic tape  containing all data for all 115
dual experiments and (2) a set of micro-
fiche of listings and plots of the entire
data base. Both the computer magnetic
tape and the microfiche are available
through the National Technical In-
formation  Service, Springfield, VA, as is
the project report (see the ordering  in-
formation  at back).
  In addition to a detailed discussion on
how to access  and use the data, the
report also contains a complete descrip-
tion of  the chamber facility,  the pro-
cedures and analytical methods used in
the study, and the uncertainties and
limitations of the data base.  Guidance

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for modeling of the data is also given
including detailed discussions of how to
treat light intensity data, rates of loss of
Os and NOX to the chamber walls, walls
as a source of free radicals, chamber
dilution, temperature and water vapor
data, and reactivity of the  background
air.

Conclusions
  Smog chamber data collected in this
study  were supplied to  two model
development groups for analysis under
EPA Contract Nos. 68-02-3281 and 68-
02-3479. The analysis of these data by
the two  modeling groups  resulted in
the development  of  improved kinetic
models of  photochemical smog for-
mation.  The purpose of  the project
report  is to  make the experimental data
available to the scientific community at
large to enable other researchers and
modelers to further the development of
chemical transformation models.
  H. E. Jeffries, R. M. Kamens, K. G. Sexton, and A. A.  Gerhardt are with the
    University of North Carolina. School of Public Health, Chapel Hill. NC27514;
    Marc/a C. Dodge (also the EPA Project Officer, see below) is with the Environ-
    mental Sciences Research Laboratory. Research Triangle Park, NC 27711.
  The complete report, entitled "Outdoor Smog Chamber Experiments to Test
    Photochemical Models," (Order No. PB 82-198 508; Cost: $22.50, subject to
    change) will be available only from:
          National Technical Information Service
          5285 Port Royal Road
          Springfield, VA 22161
          Telephone: 703-487-4650
  The EPA Project Officer can be contacted at:
          Environmental Sciences Research Laboratory
          U.S. Environmental Protection Agency
          Research Triangle Park, NC 27711
                                                                                  „ US GOVERNMENT PRINTING OFFICE. 1W2-559-017/0740

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