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were to be more completely documented, it might explain some of the striking rise in the prevalence of chronic respiratory diseases which has been observed recently.

The best indication of all of the chronic effects of air pollution is undoubtedly provided by the statistics on chronic bronchitis in Great Britain (19). There, the disease is the third leading cause of death and the leading cause of disability.

In the United States there has been increasing acceptance of the view that a group of chronic respiratory diseases in this country, comprising emphysema, chronic bronchitis, bronchiectasis, and "other chronic interstitial pneumonia," is similar to the chronic bronchitis syndrome observed in Great Britain and that the apparent differences reported in the two countries may merely reflect differences in medical diagnostic criteria and terminology in patients with cases of differing severity and degree of infection.

We are aware that in the United States no evidence has been produced to demonstrate that air pollution is an etiologic agent for the emphysema syndrome. Nonetheless, there is an ever-mounting accumulation of evidence linking the two. Well known is the phenomenal rise of deaths from emphysema in the American population as a whole since 1950 (20). One may, with considerable certainty, ascribe part of the increase to the increasing acceptance of this classification as a cause of death, which in turn is due to the increasing discussion of chronic respiratory disease in the medical literature. Nevertheless, we have no reservation in stating that part, perhaps most, of the sevenfold increase in the frequency of this diagnosis as a cause of death is due to the greater prevalence of the disease.

One reason for assuming an air pollution factor as a cause of emphysema is the urbanrural comparison of mortality in the United States. Certainly, when the age-adjusted urban rates are double the rural rates, there would appear to be some factor which is directly related to residence in cities. Attention has been drawn previously to the fact that smoking differences among males, by residence, are relatively small and presumably do not account for the urban-rural ratio found for

emphysema (21). The well-documented greater pollution of urban atmospheres as compared with rural points to a possible causal relationship.

It is recognized, of course, that there may also be an occupational exposure factor. The records of the Social Security Administration show that emphysema is the second leading cause of disability among male workers 50 years of age and older (22). It is clear that the evaluation of the role of air pollution in the increase in mortality from emphysema will have to take account of the occupational history of the decedent as well as his smoking habits.

Because of the increased interest in chronic respiratory diseases there has been a growing awareness of the need to inform people of the importance of certain symptoms. Accordingly, the National Tuberculosis Association has announced its intention of conducting a campaign during the spring of 1963 to alert people to the significance of "shortness of breath" and "chronic cough" (23). It is quite possible that people become so accustomed to these symptoms that they pay little attention or attach no importance to them. An increasing amount of data on the prevalence of emphysema and chronic bronchitis should be forthcoming as this educational campaign progresses.

In order to learn more about the long-term effects of air pollution, it was found necessary to conduct extensive field studies on selected populations. In 1959 the Division of Air Pollution of the Public Health Service, in cooperation with the Pennsylvania Department of Health, the Pennsylvania Electric Co., and others, undertook a study of two small communities in Pennsylvania, Seward and New Florence (24). The study had the elements of a natural laboratory setting inasmuch as the towns were virtually identical demographically. These towns, inhabited by about 1,000 persons each, are approximately 4 miles apart, with a soft-coal-burning electric power plant between them. The prevailing wind pattern was such that the town of Seward was subject to much higher levels of air pollution than New Florence. Thus, for the period of the study, the level of dust fall in Seward was three times that of New Florence, the level of sulfation was seven times as high, and the level of SO, was

at least nine times as high. Nevertheless, the SO, level in Seward was below that generally found in London (25).

The purpose of the study was to determine the long-term effects of low concentrations of air pollutants. An attempt was made to include the entire adult population of both sexes 30 years old and over. In addition to X-rays, the study used the long Medical Research Council questionnaire, with slight revisions, chiefly in terms of a much more detailed work-experience history. A battery of pulmonary function tests, including the body plethysmograph, was administered to the study group. The analysis, which was scheduled for completion in the summer of 1962, takes into account such variables as smoking and occupational and residence exposure of the townspeople.

In the preliminary report, one significant finding was that the average airway resistance (measured by the body plethysmograph) was higher in Seward than in New Florence even after differences in height and age were taken into account.

A curious finding was that the male population of the polluted area was almost 1 inch shorter than that of New Florence. One would rightfully hesitate to attribute this difference in height to the difference in the environment. Yet this possibility should not be dismissed arbitrarily because of its apparent implausibility. One may only say that differences of this sort would have to be documented in many other communities before we could accept the hypothesis that the stature of the inhabitants was related to exposure to air pollutants rather than to ethnic or socioeconomic differences.

Since this study was completed, considerable effort has been made by the industry to reduce the pollution in the area. A restudy some time in the future might prove of considerable interest in evaluating the possible benefits of such reduction in pollutant levels as may have been achieved.

The long-term effects of the Donora disaster have also been studied in the United States (26). The resurvey of Donora 10 years after the disastrous smog of 1948 has shown that the persons who became ill during the outbreak have had a less favorable morbidity and mortality experience than the persons who were

not affected in 1948. While it is true that those who became ill were probably less healthy to begin with than those who did not, it is quite likely that chronic effects due to unusually high levels of air pollution have been manifested in the affected group. Further, it is possible that repeated exposure to air pollution, even at very low levels, may have contributed to the longterm unfavorable experience.

The responsibility of air pollutants for the increasing frequency of lung cancer in the United States is at the moment a matter of some disagreement. Authoritative quantitative estimates of the role of air pollution as an etiologic agent do not exist, and only informed guesses can be made. Nevertheless, it is our thesis that, without decrying the importance of cigarette smoking as a factor, air pollution is also an important etiologic agent. This is not a novel idea. The World Health Organization report on lung cancer mentioned a number of possible etiologic agents and noted the prominence of air pollution in the list (27). Once again the sharp urban-rural differential in mortality rates for this disease is manifested. Also, lung cancer mortality rates appear to be related to the size of the urban area, the larger areas having the higher age-standardized mortality ratios.

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many and varied sources in every category, industrial, residential, municipal, and automotive, and makes necessary a wider range of research activities than in many other countries.

In summary, we in the United States are devoting considerable time and effort to this important question: Does longtime exposure to low concentrations of air pollution result in adverse health effects? Our preliminary answer, based on both laboratory and epidemiologic studies, is yes. The evidence as yet is only qualitative; much more will have to be done before the necessary quantitative answers are found on which to base rational control standards. Hopefully, with the data the Public Health Service is able to collect and that amassed by researchers in Europe and throughout the world, this goal can be attained.

REFERENCES

(1) Stokinger, H. E., Wagner, W. D., and Dobrogorski, O. J.: Ozone toxicity studies. III. Chronic injury to lungs of animals following exposure at a low level. A.M.A. Arch. Indust. H. 16: 514-522, December 1937.

(2) Ball, C. O. T., et al.: Survival of rats chronically exposed to sulfur dioxide. Physiologist 3:15, August 1960.

(3) Amdur, M. O., Silverman, L., and Drinker, P.: Inhalation of sulfuric acid mist by human subjects. A.M.A. Arch. Indust. Hyg. & Occup. Med. 6: 305-313, October 1952.

(4) Amdur, M. O., Melvin, W. W., Jr., and Drinker, P.: Effects of inhalation of sulfur dioxide by man. Lancet 2: 758-759, October 10, 1953. (5) Research in air pollution; conference report. Pub. Health Rep. 75: 1173-1189, December

1960.

(6) Hofreuter, D. H.: The automotive exhaust problem. A.M.A. Arch. Environ. H. 2: 559-563, May 1961.

(7) Hofreuter, D. H., Catcott, E. J., and Xintaras, C.: Carboxyhemoglobin in men exposed to carbon monoxide, A.M.A. Arch. Environ. H. 4: 81-85, January 1962.

(8) Rose, A. H., Jr., Stahman, R. C., and Stevenson, H. J. R.: Exhaust contamination in passenger cars. Technical Report A61-2. Robert A. Taft Sanitary Engineering Center, Public Health Service, Cincinnati, Ohio, February 1961.

(9) U.S. Public Health Service: Six years of research in air pollution, July 1, 1955, to June 30, 1961. Washington, D.C., 1961, (a) p. 196, (b) pp. 204-208, (c) p. 137.

(10) Clayton, G. D., Cook, W. A., and Fredrick, W. G.:

A study of the relationship of street level carbon monoxide concentrations to traffic accidents. Am. Indust. Hyg. A. J. 21: 46-34. February 1960.

(11) Wiseley, D. V., Kotin, P., Fowler, P. R., and Trivedi, J.: The combined effect of repeated viral infection on pulmonary tumor induction in C57 black mice. Proc. Am. A. Cancer Res. 3: 278 (1961).

(12) Kotin, P.: Combination of stimuli in experimental lung cancer. Presented at the Fifth Air Pollution Medical Research Conference. Los Angeles, Calif., December 4-7, 1901. (13) Greenburg, L., et al.: Report of an air pollution incident in New York City, November 1953. Pub. Health Rep. 77: 7-16, January 1962. (14) Greenburg, L., Field, F., Reed, J. I., and Erhardt. C. L.: Air pollution and morbidity in New York City. J.A.M.A. In press.

(15) Schoettlin, C. E., and Landau, E.: Air pollution and asthmatic attacks in the Los Angeles area. Pub. Health Rep. 76: 545-348, June 1961. (16) Zeidberg, L. D., Prindle, R. A., and Landau, E: The Nashville air pollution study: I. Sulfur dioxide and bronchial asthma; a preliminary report. Am. Rev. Resp. Dis. 84: 489–503, 06 tober 1961.

(17) Phelps, H. W., Sobel. G. W., and Fisher, N. E: Air pollution asthma among military personnel in Japan. J.A.M.A. 173: 990-943, March 18, 1961.

(18) Dohan, F. C.: Air pollutants and incidence of respiratory disease. A.M.A. Arch. Environ.

H. 3: 387-395, October 1961. (19) Ogilvie, A. G., and Newell, D. J.: Chrenic bron chitis in Newcastle-Upon-Tyne. Livingstone. Ltd., Edinburgh and London, 1957, p. 2. (20) U.S. National Office of Vital Statistics: Vital Statistics of the United States: 1950, 1959. U.S. Government Printing Office, Washington. D.C., 1952, 1961.

(21) Prindle, R. A.: Some considerations in the interpretation of air pollution health effects data. J. Air Pollut. Control A. 9: 12-19 (1959). (22) U.S. Social Security Administration: Disability applicants under the Old-Age Survivors and Disability Insurance Program, 1960. Social Security Administration, Washington, DC, January 1962, tables 10 and 11.

(23) Williams, G.: Program possibilities in respiratory diseases. Presented at the 58th annual meeting of the National Tuberculosis Association, Miami Beach, Fla., May 20-23, 1962.

(24) Prindle, R. A., et al.: Comparison of pulmonary function and other parameters in two communities with widely different air pollution levels. Am. J. Pub. Health. In press. (25) World Health Organization: Air pollution. WHO Monograph Series No. 46, Geneva, 1961. (26) Ciocco, A., and Thompson, D. J.: A follow-up of Donora ten years after: methodology and find

ings. Am. J. Pub. Health 51: 155-164, February 1961.

(27) World Health Organization: Epidemiology of cancer of the lung; report of a study group. WHO Technical Report Series No. 192, Geneva, 1960, pp. 5-6.

(28) Dean, G.: Lung cancer among white South Africans. Report on a further study. Brit. M.J. 16: 1599-1605, December 16, 1961.

(29) Eastcott, D. F.: The epidemiology of lung cancer in New Zealand. Lancet 1: 37-39, January 7, 1956.

Dr. KAILIN. The evidence cited in this article is consistent with the conclusion that long-term exposure even to low metropolitan concentrations of air pollution probably result in adverse health effects.

Drs. Snell and Feinberg yesterday told you of the effects of air pollutants on the lungs. Asthma aggravated by air pollution is receiving attention by more and more allergists.

This little gadget (indicating) will give you an idea of what the magnitude of the problem will be. This is a little bag of activated carbon-charcoal. I have given out dozens of these to patients to use. I tell them to fold it up in a handkerchief and hold it under their noses when they come across heavy air pollution and they need it. The asthmatic who is stopped in traffic behind a bus or even a person who steps on the elevator and somebody steps in with a pipe or heavy perfume, this will send their lungs right into spasm. They grab this out of their pocket and put it in front of their noses. The people are carrying gadgets like this in our city right now.

Senator TYDINGS. That is along the lines of the children in some big cities of the world who have to wear gas masks in certain playgrounds.

Dr. KAILIN. Japan. I don't think we have gotten to that point yet. But our more sensitive individuals are finding this a practical comfort in our city now.

Some of these are used by asthmatic persons, but the people who concern me most are the people who get cerebral effects from air pollution and there is very little written about this. These are people whose brain cells almost literally short circuit when they breathe motor exhaust fumes, or road tar fumes, and certain other fat soluble substances. These highly sensitive people show changes in the chromosome material of their cells under a microscope and under stress. They are not genetically different from ordinary people. This is change that comes and goes. A person given a stress, and the stress may be air pollution in the sense in which you are studying it today, it may be air pollution in the sense of ragweed pollen in a ragweed sensitive person. And these people, when we take scrapings of the cells of their cheeks and put them under a microscope to see how the chromosome materials clumped, at the time of stress, chemical pollen, other allergic stresses will do it, one of the chromosomes disappears from view temporarily. You relieve the stress and it appears again. So there is an effect on chromosome material as a result of

stress.

I cite this not to give you so much of that particular aspect of it as to try to tell you that cerebral effects can occur, can be real and it is not just a case of whether you hated your mother when you were a child. The brain is also a physical organ and we are likely to think of it simply in terms of neuroses these days.

There these same highly susceptible people who get this same effect in their brain function and also have very high susceptibility to

cancer.

I am running around 10 percent in a small relatively young group. They are not rare. My practice is allergy. I get hay fever, I get asthma, I get migrains, fruit allergic problems, stomach aches, all kinds of things. Whatever happens to come in I get.

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