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 ------- 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 ------- United States Environmental Protection Agency Center for Environmental Research Information Cincinnati OH 45268 Official Business Penalty for Private Use $300 ft ^ L' t t h t t>~ f: U K I ^iw ,> L,r.,:: „.„ , .' U.S. GOVERNMENT PRINTING OFFICE. 1984—759-015/7613 ------- |