United States
                     Environment Protection
                     Agency
 Health Effects Research
 Laboratory
 Research Triangle Park NC 27711
                     Research and Development
 EPA-600/S1-84-002   Mar. 1984
&EPA          Project  Summary
                     Interaction  of  Complex  Pollutant
                     Mixtures  and  Particulates  in
                     Causation   of   Pulmonary  Disease
                     Richard Ehrlich
                      Studies were conducted to determine
                    the effects of exposure to particulate
                    and  gaseous air  pollutants  on the
                    resistance to experimental respiratory
                    infection.  Changes in resistance to
                    bacterial pneumonia, expressed as in-
                    creases in mortality rate and decreases
                    in mean survival time, served as the
                    most sensitive and consistent indicators
                    of damage produced by the exposure.
                    Using these parameters it was possible
                    to rank the effects of single 3-hr inhala-
                    tion exposure to various sulfate and
                    nitrate particulate aerosols. Among the
                    particulate pollutants included  in these
                    studies, cadmium sulfate and cadmium
                    nitrate were  most toxic.  They  were
                    followed in decreasing order of toxicity
                    by copper, aluminum and magnesium
                    sulfate or nitrate aerosols. The metallic
                    cation appeared to be  most important
                    in altering the resistance to infection.
                    Multiple 3-hr exposures to significantly
                    lower concentrations of zinc or cupric
                    sulfate similarly reduced the resistance
                    to the respiratory infection.

                      Nitrogen dioxide (IMO2) and ozone (O3)
                    mixtures  reduced the resistance to
                    bacterial pneumonia after 6-month in-
                    halation exposure to various regimens
                    of these photochemical oxidants.

                      This Project Summary was developed
                    by  EPA's Health Effects  Research
                    Laboratory, Research Triangle Park, NC,
                    to announce key findings  of the
                    research project that is fully docu-
                    mented in a separate report of the same
                    title (see Project Report ordering infor-
                    mation at back).
 Introduction
  Changes in resistance to respiratory infec-
 tion provide a highly sensitive experimental
 animal model system for studies of the ef-
 fects of air  pollutants at concentrations
 resembling those found in urban  en-
 vironments. The model reflects the impair-
 ment of the  host defense mechanisms by
 combined exposures to air pollutants and to
 infectious bacterial aerosol.
  The objectives of this program were to
 determine the effects of single or multiple
 short-term exposures to various sulfate and
 nitrate particulate aerosols on resistance to
 streptococcal pneumonia and to study the
 changes in  resistance to this infection
 resulting from long-term exposures to N02
 and 03 mixtures. In the latter experiments
 it was of special interest to determine the ef-
 fects of short-duration peaking of the N02
 and 03 mixture superimposed on a con-
 tinuous exposure to low N02 concentrations.

 Materials  and  Methods
  The basic experimental protocol used in
 the studies called for exposure of a group of
 animals to the pollutants and a second group
 to clean filtered air. After the exposure the
 two groups were combined and within less
 than 1 hr challenged by the respiratory route
 with an aerosol of infectious bacteria. After
 the challenge the animals were kept for 14
 days, during which mortality rates and sur-
vival time were observed.
  The  short-term  exposures to the  air
 pollutants were carried out in 432 liter Plexi-
glas chambers. The pollutants were diluted
 in filtered room air and introduced into the
chambers. To assure a homogeneous dis-
tribution of the pollutants, a small fan was
operated continuously in each chamber.  For

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long-term exposure, 4420 liter aluminum-
lined walk-in chambers were used. The ran-
domly selected mice were housed in inhala-
tion cages provided with an automatic water-
ing system. To assure unbiased exposure to
the experimental atmospheres the  cages
were rotated weekly to various positions on
the cage rack. Ammonia build-up during the
exposures was prevented by the placement
of deotized boards beneath each cage row.
The exposures to the pollutants were inter-
rupted twice weekly for a total of approxi-
mately 3 hr to provide clean cages and fresh
feed.
   A high-voltage generator was used to con-
vert oxygen to 03. To  provide the desired
concentration, 03 was  diluted with filtered
air in a glass mixing chamber and passed into
the exposure chamber. The 03 concentra-
tion  was  monitored with an 03  chemi-
luminescent analyzer. A 1 or 5% mixture of
N02 in air was diluted with filtered  air and
the N02 concentration in the chambers was
monitored continuously by an  N0-N02-N0x
chemiluminescent analyzer.
   The particulate aerosols were generated
by a nebulizer from  aqueous solutions of
crystalline materials. The estimated mass
median  aerodynamic  diameter of  the
evaporated particles was 0.63 ^m and the
median diameter, approximately  0.31 ^m.
For particle size  analysis, aerosol samples
were collected through  a 7 ^m single-stage
preimpactor onto 25 mm glass discs cleaned
with methanol and  coated  with a  50%
glycerol-water solution.  Microscopic  ex-
amination indicated that approximately 90%
of the airborne  particles were <3 pm in
diameter.
   Infectious challenge with Streptococcus
sp. (Group C) was performed  in a 400-liter
exposure  chamber  housed  within  a
microbiological safety cabinet. A continuous
flow nebulizer (DeVilbiss Model 841) was
used to produce the bacterial aerosol. For
infectious challenge, mice were housed in in-
dividual compartments of stainless steel wire
cages. After the challenge the mice were
removed from the chamber and housed for
a  14-day observation period in an isolated
clean-air animal room or were returned to the
pollutant exposure chambers.
   Effects of the exposures were measured
in terms of changes in  mortality  rates and
mean survival time.  Free pulmonary cells
were obtained by tracheobronchial lavage
and total cell counts were made on fixed cell
smears. Viability of the alveolar macrophages
was determined by dye exclusion, and the
cellular ATP concentration in the lavaged
cells was monitored. Pulmonary bactericidal
activity was determined in individual mice,
whereby the ratio of viable count to the
radioactive count of Klebsiella pneumoniae
in the lungs provided the rate at which the
bacteria were killed by the lung in a given
time after infection. The clearance of inhaled
viable bacteria from lungs was determined
and expressed as the time in hours required
for 50% of the inhaled bacteria to clear the
lungs.
   The significance of the differences in mor-
tality rates  was  determined  by the Chi-
square (X2) test with  a 2 x 2 contingency
table. The Student's t test, analysis of vari-
•ance, and least square linear regression were
applied to the data, as appropriate.

Conclusions
   Results  of  the studies  reconfirmed
previous observations  that an increase in
mortality  rates  resulting from  bacterial
pneumonia is a reproducible and sensitive in-
dicator of adverse effects of air pollutants.
   A single 3-hr exposure to cadmium, cupric
or aluminum sulfate or nitrate resulted in
significant  increase  in  mortalities and
decrease in  mean survival time in mice in-
fected  with a streptococcus aerosol. These
effects were seen at concentrations of ap-
proximately 0.40  mg/m3 cadmium, 0.85
mg/m3 cupric  or 1.80 mg/m3 aluminum
sulfate or nitrate. In all exposures the metallic
cation  appeared to be the  fraction  of the
pollutant that was effective in altering the
resistance to the infection. Several sulfate,
nitrate and nitrite pollutants used in the ex-
periments had  no effect on the mortality
rates. Thus, the results of this phase of the
program confirmed the utility of this animal
model  in ranking the toxic effects of inhala-
tion of particulate pollutants.
   A 6-month continuous  (24  hr/day,  7
days/week) exposure to 0.19 mg/m3 N02
with superimposed 3 hr/day,  5 days/week
peaks of 0.94 mg/m3 N02 and 0.2 mg/m3 03
mixture resulted in a significant increase in
mortality of mice infected with streptococ-
cus aerosol. A similar effect was seen after
9 months of continuous exposure to 0.38
mg/m3 N02 with superimposed twice daily
peaks occurring 5 days/week. The morning
exposure peak was 1.88 mg/m3 N02 for 1
hr, and the afternoon peak consisted of 0.2
mg/m3 03 for 3 hr  mixed with 1.88 mg/m3
N02 for 1 hr. The changes in the resistance,
however, were not seen after 4 or 8 month
exposure to the same experimental regimen.
  Superimposition of a single 3-hr exposure
to 0.3 mg/m3 cupric sulfate at the end of the
9-month exposure to the photochemical ox-
idant pollutant mixture resulted in further
enhancement of the  mortality due to the
streptococcal pneumonia.

Recommendations
  Studies should continue to define more
precisely the causal relationship between in-
halation of  air  pollutants  and   acute
respiratory infections in laboratory animals.
To simulate environmental pollution condi-
tions, studies should include the use of mix-
tures of gaseous and particulate pollutants.
Exposure to additional stresses such  as ex-
ercise or extremes of temperature should
also be included in such investigations. Since
humans are usually exposed to low concen-
trations of pollutants with superimposed
cyclical  higher concentrations, similar ex-
posure regimens should be used during long-
term exposure studies. This is especially im-
portant in  studies of  pollutants such  as
nitrogen dioxide, where within a given ex-
posure  regimen the concentration   is  of
greater  importance than  the duration of
exposure.
    Richard Ehrlich is with 117 Research Institute, Chicago. IL 60616.
    Donald E. Gardner is the EPA Project Officer (see below).
    The complete report, entitled "Interaction of Complex Pollutant Mixtures and
      Particulates in Causation of Pulmonary Disease," (Order No. PB 84-138 965;
      Cost: $8.50, 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:
            Health Effects Research Laboratory
            U.S. Environmental Protection Agency
            Research Triangle Park, NC27711

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