Effects of ambient ozone on respiratory function in active, normal children

Acute effects of ambient ozone on pulmonary function of children in The Netherlands

In the spring and summer of 1989 an epidemiologic study was conducted to evaluate the acute effects of photochemical air pollution episodes on pulmonary function of children living in three nonindustrial towns in the Netherlands. Spirometry was performed repeatedly in the schools of the children, mostly during the morning hours. Data from 533 children having more than four valid pulmonary function tests were included in the analyses. The association between previous-day ambient ozone concentration and pulmonary function was evaluated, using individual linear regression analysis and subsequent evaluation of the distribution of individual regression coefficients. One hour maximum ambient ozone concentrations frequently exceeded 160 micrograms/m3 but were all lower than the Dutch Air Quality Guideline of 240 micrograms/m3 for all three populations. Significant negative associations of previous-day ambient ozone with FVC, FEV1, peak expiratory flow (PEF), and maximal midexpiratory flow (MMEF) were observed. There were indications of systematic differences in responses among the children. Children with chronic respiratory symptoms did not have a stronger response than children without these symptoms.

Respiratory effects of air pollution on allergic disease

Allergic patients have an increased susceptibility to the adverse effects of both natural and man-made air pollutants. This goes for both indoor and outdoor air pollutants and manifests itself with biochemical, cellular, and pathophysiologic expressions of adverse health effects in allergic individuals. Also occupationally induced allergic diseases will remain very important. This area has been reviewed recently by Cullen et al. Since allergic patients comprise somewhere between 15% and 20% of the population, this increased susceptibility is of crucial importance not only for medical care and research but for legislative and regulatory consideration to protect these vulnerable individuals.

Epithelial injury and interstitial fibrosis in the proximal alveolar regions of rats chronically exposed to a simulated pattern of urban ambient ozone

Electron microscopic morphometry was used to study the development of lung injury during and after chronic (78 weeks) exposure to a pattern of ozone (O3) designed to simulate high urban ambient concentrations that occur in some environments. The daily exposure regimen consisted of a 13-hr background of 0.06 ppm, an exposure peak that rose from 0.06 to 0.25 ppm, and returned to the background level over a 9-hr period, and 2-hr downtime for maintenance. Rats were exposed for 1, 3, 13, and 78 weeks. Additional groups of rats exposed for 13 or 78 weeks were allowed to recover in filtered clean air for 6 or 17 weeks, respectively. Rats exposed to filtered air for the same lengths of time were used as controls. Samples from proximal alveolar regions and terminal bronchioles were obtained by microdissection. Analysis of the proximal alveolar region revealed a biphasic response. Acute tissue reactions after 1 week of exposure included epithelial inflammation, interstitial edema, interstitial cell hypertrophy, and influx of macrophages. These responses subsided after 3 weeks of exposure. Progressive epithelial and interstitial tissue responses developed with prolonged exposure and included epithelial hyperplasia, fibroblast proliferation, and interstitial matrix accumulation. The epithelial responses involved both type I and type II epithelial cells. Alveolar type I cells increased in number, became thicker, and covered a smaller average surface area. These changes persisted throughout the entire exposure and did not change during the recovery period, indicating the sensitivity of these cells to injury. The main response of type II epithelial cells was cell proliferation. The accumulation of interstitial matrix after chronic exposure consisted of deposition of both increased amounts of basement membrane and collagen fibers. Interstitial matrix accumulation underwent partial recovery during follow-up periods in air; however, the thickening of the basement membrane did not resolve. Analysis of terminal bronchioles showed that short-term exposure to O3 caused a loss of ciliated cells and differentiation of preciliated and Clara cells. The bronchiolar cell population stabilized on continued exposure; however, chronic exposure resulted in structural changes, suggesting injury to both ciliated and Clara cells. We conclude that chronic exposure to low levels of O3 causes epithelial inflammation and interstitial fibrosis in the proximal alveolar region and bronchiolar epithelial cell injury.

Relation of peak expiratory flow rates and symptoms to ambient ozone

The temporal association between peak expiratory flow rates (PEFRs) and ambient ozone (O3) was studied in a group of 287 children and 523 nonsmoking adults in Tucson. In children, noon PEFRs were decreased on days when there was a higher O3 concentration; children with physician-confirmed asthma experienced the greatest decrease in noon PEFR. Evening PEFR levels were also significantly related to O3 in children, especially asthmatics. Among adults, evening PEFRs were decreased in asthmatics who spent more time outdoors on days when O3 levels were higher. After we adjusted for covariates, significant effects of interactions of 8-h O3 levels with particulate matter (PM10) and temperature on daily PEFR were found. There was some overnight effect of 8-h O3 on morning PEFRs. In general, the respiratory response to low-level ambient O3 is acute, occurs more in asthmatics, and increases as temperature and PM10 increase.

Air pollution and the duration of acute respiratory symptoms

The possibility that air pollution exposure can extend the duration of respiratory symptoms was examined in a diary study of student nurses. This diary study has already shown associations between air pollution and incidence rates of respiratory symptoms. After individual risk factors and temperature were controlled for, photochemical oxidants were significantly (p less than .0001) associated with the duration of episodes of coughing, phlegm, and sore throat. Some heterogeneity of response to oxidants was seen; there was little effect on asthmatics, but the impact increased as family income increased. Plots of the mean duration of symptoms, by quintiles of oxidants, for which the other covariates were controlled, showed strong signs of a dose-response relationship for coughing and phlegm and moderate signs of a monotonic dose-response relationship for sore throat. The relationships continued for concentrations below the current ambient standard for ozone. Chest tightness or discomfort was significantly associated with sulfur dioxide (p = .016), but the effect seemed mainly restricted to asthmatics. However, evidence for a dose-dependent increase was weak.

Valuing the health benefits of clean air

An assessment of health effects due to ozone and particulate matter (PM10) suggests that each of the 12 million residents of the South Coast Air Basin of California experiences ozone-related symptoms on an average of up to 17 days each year and faces an increased risk of death in any year of 1/10,000 as a result of elevated PM10 exposure. The estimated annual economic value of avoiding these effects is nearly $10 billion. Attaining air pollution standards may save 1600 lives a year in the region.

Pulmonary responses of asthmatic and normal subjects to different temperature and humidity conditions in an environmental chamber

Determining the possible adverse health effects of air pollutants can be complicated by differences in the environmental conditions of temperature and humidity. To evaluate the potentially confounding effects of differences in temperature and humidity, we exposed 8 normal male subjects and 8 male subjects with asthma to the extremes in temperature and humidity that could be maintained in an environmental chamber. We performed serial pulmonary function tests for these subjects before and during 6 hr exposure periods on 5 separate occasions: cold, dry (10 degrees C, 10% relative humidity); cold, humid (10 degrees C, 50% relative humidity); normal ambient (22 degrees C, 40% relative humidity); hot, dry (37 degrees C, 15% relative humidity); and hot, humid (37 degrees C, 60% relative humidity). The exposure period included a 12 min exercise on a cycle ergometer. We found no significant change in spirometry, airways resistance, or diffusing capacity for either group of subjects at rest alone over the 6 hr period of exposure for any exposure condition. However, there were changes in spirometry and airways resistance as a result of the 12 min period of exercise. The subjects with asthma had significant decreases in forced expiratory volume in 1 sec (FEV1) (20-21%) and increases in specific airways resistance when exercising in conditions of cold and dry, cold and humid, and hot and dry. The normal subjects had an average increase in FEV1 of approximately 6% when exercising in the hot and humid conditions. We found significant correlations for the changes in FEV1 with the water content of the exposure conditions for both groups of subjects. We also found that the work performance (expressed as the external work performed divided by the oxygen consumed) was decreased for the subjects in both groups at the conditions of the higher temperature (37 degrees C) compared with the lower temperature (10 degrees C). These results confirm that controlling for the conditions of temperature and humidity is essential in chamber studies, field studies, or epidemiologic evaluations determining the adverse effect of an air pollutant.

Sulfuric acid-layered ultrafine particles potentiate ozone-induced airway injury

Urban air pollution in the United States is composed of a complex mixture of particles and gases. Among the most prominent products of the atmospheric pollutants are sulfur oxides and ozone. In this report, we use two exposure protocols to examine the interaction between exposure to these two pollutants. In the first exposure regimen, guinea pigs were exposed to sulfuric acid (pure sulfuric acid mist or sulfuric acid layered on ZnO) for 1 h. Each exposure is followed 2 h later by another exposure to 0.15 ppm ozone for 1 h. Pulmonary function parameters were measured immediately after the ozone exposure. In guinea pigs that were exposed to 300 micrograms/m3 pure sulfuric acid mist, subsequent exposure to 0.15 ppm ozone did not produce additional change in pulmonary functions. In guinea pigs that were exposed to 84 micrograms/m3 sulfuric acid layered on ZnO, subsequent exposure to 0.15 ppm ozone produced more than additive alterations in vital capacity and diffusing capacity. In the second exposure regimen, guinea pigs were exposed to 24 micrograms/m3 sulfuric acid layered on ZnO for 3 h/d for 5 d. On d 8 and 9, animals received two additional daily 3-h exposures to 24 micrograms/m3 sulfuric acid layered on ZnO, and pulmonary functions were measured at the end of the daily exposure. Greater reductions in lung volumes and diffusing capacity were observed in animals on d 9 than would be observed in animals that received no additional exposure. In the third exposure regimen, guinea pigs were exposed to 24 micrograms/m3 sulfuric acid layered on ZnO for 3 h/d for 5 d. On d 9, animals were exposed to 0.15 ppm ozone for 1 h and pulmonary functions were measured at the end of the ozone exposure. Ozone exposure on d 9 induced reductions in lung volumes and diffusing capacity that were not observed in animals receiving exposures to either ozone or sulfuric acid layered ZnO alone. We conclude that single or multiple exposure to sulfuric acid-layered ZnO sensitizes guinea pigs to subsequent sulfuric acid or ozone exposure.

Effects of air pollution resulting from wire reclamation incineration on pulmonary function in children

This study evaluated the effect of long-term air pollution resulting from wire reclamation incineration on pulmonary function in children. General physical examination and the determination of spirometric parameters, including forced vital capacity (FVC), forced expiratory volume in 1 s (FEV1), and forced mid-expiratory flow (FEF25-75%) were conducted in 400 primary school children between ages 9 and 11 years who reside in one control and three polluted areas. A survey using ATS-DLD-78-C questionnaire indicated that there were no significant differences in their demographic characteristics among children in the four areas under study. Those who had nonrespiratory diseases that might affect pulmonary function and those who failed to perform spirometric measurements were excluded from the study; therefore, 382 children were included in data analysis. The results revealed that (1) the mean values of FVC and FEV1 (expressed as percentage of predicted values calculated from Polgar's equations) in the polluted areas were significantly lower than the nonpolluted area (p less than 0.05), and (2) the incidence of pulmonary function abnormality in the polluted areas was greater than that of the nonpolluted area (p less than 0.05). The results indicated that air pollution produced by wire reclamation incineration can impair children's pulmonary function.

Effects of single- and multiday ozone exposures on respiratory function in active normal children

Ventilatory function was measured twice daily on 46 healthy children aged 8-14 years on at least 7 days for each child during a 4-week period at a northwestern New Jersey residential summer camp in 1988. The highest 1-hr O3 concentration was 150 ppb, while the highest 12-hr H+ concentration (as H2SO4) was 18.6 micrograms/m3. The highest temperature-humidity index was 81 degrees F. The regressions of FVC, FEV1, FEF25-75, and PEFR on O3 in the hour preceding the afternoon function measurements yielded slopes essentially the same as those measured on other children at the same camp in 1984. Regressions of the changes in function between the late morning and late afternoon function measurements on average O3 concentration between them produced significant, but somewhat smaller effects, while regressions of morning function on O3 during the previous day indicated small but still significant effects. There were no significant correlations with other measured environmental variables including H+. Based on the results of this study and similar previous studies, we conclude that O3 exposures in ambient air produce greater lung function deficits in active young people in natural settings then does pure O3 in controlled chamber exposure studies because of: (1) longer exposures; (2) potentiation by other factors in the ambient exposures; (3) the persistence of effects from prior day's exposures; and (4) the persistence of a transient response associated with the daily peak of exposure. It follows that projections of likely effects in the real world from controlled chamber exposure studies should either have a large margin of safety, or the judgment of the extent of effects likely to occur among populations should be based directly on the effects observed in field studies.

Respiratory response of humans exposed to low levels of ozone for 6.6 hours

Recent evidence suggests that prolonged exposures of exercising men to 0.08 ppm ozone (O3) result in significant decrements in lung function, induction of respiratory symptoms, and increases in nonspecific airway reactivity. The purpose of this study was to confirm or refute these findings by exposing 38 healthy young men to 0.08 ppm O3 for 6.6 h. During exposure, subjects performed exercise for a total of 5 h, which required a minute ventilation of 40 l/min. Significant O3-induced decrements were observed for forced vital capacity (FVC, -0.25 l), forced expiratory volume in 1 s (FEV1.0, -0.35 l), and mean expiratory flow rate between 25% and 75% of FVC (FEF25-75, -0.57 l/s), and significant increases were observed in airway reactivity (35%), specific airway resistance (0.77 cm H2O/s), and respiratory symptoms. These results essentially confirm previous findings. A large range in individual responses was noted (e.g., percentage change in FEV1.0; 4% increase to 38% decrease). Responses also appeared to be nonlinear in time under these experimental conditions.

Ambient air pollution and respiratory disease

OBJECTIVE

To review the literature on ambient air pollution and respiratory disease, and to consider the criteria for defining causation.

DATA SOURCES

Medical and scientific journals indexed by Medline, conferences, proceedings and monographs.

STUDY SELECTION

Two kinds of study were selected--(i) controlled clinical trials which have exposed normal or asthmatic subjects and/or patients with chronic obstructive airways disease to sulphur dioxide, nitrogen dioxide or ozone; and (ii) epidemiological studies which have investigated the chronic toxicity of these pollutants, acid aerosols and polycyclic aromatic hydrocarbons.

DATA EXTRACTION AND SYNTHESIS

Experimental studies were tabulated under the headings "Design", "Subjects", "Pollutant concentration", "Duration of exposure", "Outcome measures" and "Conclusions". Epidemiological studies were summarised and compared in an attempt to reconcile conflicting results. (The experimental and epidemiological evidence has been used by regulatory bodies to develop ambient air quality guidelines.)

CONCLUSIONS

At the present state of knowledge, it is not possible to conclude that air pollution can cause respiratory disease de novo, but levels marginally above current guidelines certainly have adverse effects on individuals with pre-existing chronic lung disease.

Exposure of humans to ambient levels of ozone for 6.6 hours causes cellular and biochemical changes in the lung

An acute (2 h) exposure of humans to 0.4 ppm ozone initiates biochemical changes in the lung that result in the production of components mediating inflammation and acute lung damage as well as components having the potential to lead to long-term effects such as fibrosis. However, many people are exposed to lower levels of ozone than this, but for periods of several hours. Therefore, it is important to determine if a prolonged exposure to low levels of ozone is also capable of causing cellular and biochemical changes in the lung. Nonsmoking males were randomly exposed to filtered air and either 0.10 ppm ozone or 0.08 ppm ozone for 6.6 h with moderate exercise (40 liters/min). Bronchoalveolar lavage (BAL) was performed 18 h after each exposure, and cells and fluid were analyzed. The BAL fluid of volunteers exposed to 0.10 ppm ozone had significant increases in neutrophils (PMNs), protein, prostaglandin E2 (PGE2), fibronectin, interleukin-6 (IL-6), and lactate dehydrogenase (LDH) compared with BAL fluid from the same volunteers exposed to filtered air. In addition, there was a decrease in the ability of alveolar macrophages to phagocytize yeast via the complement receptor. Exposure to 0.08 ppm ozone resulted in significant increases in PMNs, PGE2, LDH, IL-6, alpha 1-antitrypsin, and decreased phagocytosis via the complement receptor. However, BAL fluid protein and fibronectin were no longer significantly elevated. We conclude that exposure of humans to as low a level as 0.08 ppm for 6.6 h is sufficient to initiate an inflammatory reaction in the lung.

Technological disasters--towards a preventive strategy: a review

Technological or man-made disasters are a growth industry. Widely publicized industrial disasters like those in Bhopal and Chernobyl are only the tip of the iceberg of human and environmental risk from technological development. Other less well publicized disasters, including the contamination of food, water and air, have affected millions of people. The 'slow' technological disasters - like air pollution, pesticides, radiation, lead, asbestos and other industrial hazards - also compromise human intellectual, behavioural and physical development. Although it can be argued that there are hazards attached to virtually every industrial activity and that it is almost impossible to remove completely the risk of technological disasters, it is possible to reduce this risk by decentralizing or deconcentrating knowledge on technological processes. Global recommendations may provide a framework for priority action, but they are obviously not applicable everywhere with the same intensity. A measurement-based approach is described that is beginning to have an effect in several developing countries.

Cellular, biochemical and functional effects of ozone: new research and perspectives on ozone health effects

Ozone, a toxic component of photochemical oxidant air pollution, has been the focus of considerable research efforts for several decades. In spite of this large body of work, questions remain as to the potential risks to human health represented by chronic low-level exposure to ozone. Newer studies in animals have provided fundamental information on the range of biochemical, functional and morphologic responses to ozone exposure. While the response to ozone exposure is extremely complex, some generalities have emerged which may aid attempts to apply the results of these studies to decisions regarding the protection of human health.

Environmentally mediated disorders of the respiratory tract

Although much of the evidence in environmental lung disease remains equivocal, some environmental exposures are known to be clinically relevant. Ambient air pollution remains of concern as a source of morbidity, particularly for susceptible populations such as persons with asthma, chronic obstructive pulmonary disease, or cardiac disease and the elderly. The adverse effects of several components of indoor air pollution have been established. Environmental tobacco smoke contributes to lower-respiratory illness in infants; office workers exposed to thermophilic actinomycetes contaminating ventilation systems have developed hypersensitivity pneumonitis; and in the home, components of house dust and fungus spores may provoke asthma via immediate hypersensitivity. The evidence is less compelling for a link between other exposures and disorders of the respiratory tract. For example, formaldehyde may be responsible for provoking vague respiratory symptoms and even nasal cancers; however, the associations are unproved. Likewise, the relation between low-level exposure to asbestos and the development of lung cancer, although a concern, is not conclusively established. The clinician should be aware of practical measures for patients who inquire about air cleaning. Often, relatively simple solutions are effective. A knowledge of sources and exposures as well as an understanding of the principles of inhalation lung injury should prove useful in directing patient care.

Respiratory effects of outdoor air pollution

Outdoor air pollution adversely affects human health and the quality of the environment. However, epidemiologic studies of these effects are difficult to control because of confounding variables such as age and cigarette smoking and the difficulty in estimating doses of pollutants. Drs Griffith and Levin discuss the relationship between major types of pollutants and increased morbidity and mortality from respiratory disease.

Tropospheric ozone: the dynamics of human exposure

The conditions in the ambient atmosphere conducive to ozone exposure are examined, and placed into a context of the time and locations where individuals would be expected to be affected by high ozone. This is done for both 1 h and 8 h averaging times. Concentrations of ozone in the ambient atmosphere can violate the National Ambient Air Quality Standard (NAAQS) and also the Time Weighted Average-Threshold Limit Value (TWA-TLV) for workers. Exposures that occurred in a 1982 episode associated with a health effects study are described in detail. The effective dose received by a camper at a children's summer camp appeared to be similar to that delivered to volunteers during a controlled human exposure study in which effects on pulmonary function were observed.

Exposure assessment: input into risk assessment

The validity of a risk assessment can be no better than that of the exposure assessment upon which it is based. The general paucity of relevant exposure data, combined with the limited appreciation by most risk assessors of the critical dimensions and metrics of exposure, often leads to an overreliance on exposure models of questionable validity. The problems of identifying and interpreting relevant metrics of exposure for epidemiologic studies and risk assessments are illustrated through the presentation of three case studies. The first examines the effects of ozone on respiratory mechanical function and demonstrates that the appropriate averaging time is greater than or equal to 6 hr, rather than 1 hr, as is implied by the current ambient air quality standard. The second case study examines the effects of sulfur oxides and particulate matter in ambient air on morbidity and mortality. It indicates that the effects are most closely associated with the acidity of the aerosol, providing a basis for an index of exposure more relevant than those currently used, i.e., sulfur dioxide and nonspecific gravimetric mass concentration of particulate matter. The third case study examines the effects of lead on blood pressure. It shows that blood lead in concentrations below 35 micrograms/dL correlates with blood pressure in both humans and animals independently of other known causal factors for blood pressure elevation. It also examines the variable relations between levels of lead in blood and in environmental media to illustrate the potential problems which can arise from the use of biological markers, such as lead in blood, as indices of exposure.