Air pollutants and primary allergy prevention
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Air pollutants such as particulate matter (PM2.5) and nitrogen dioxide (NO2) in outdoor air have long been suspected of causing the development of asthma and allergic rhinitis. However, a variety of systematic reviews have reached different conclusions in the last 15 years on whether these air pollutants do in actual fact play a causal role in the onset of asthma, allergic rhinitis, and eczema.
Based on published systematic reviews and the most recent publications, the current state of knowledge on epidemiological evidence is presented and the potential for primary prevention of these allergic diseases by reducing or avoiding exposure to these air pollutants evaluated.
Despite conducting an extensive literature search, analyzing the most recent results, and focusing on the birth cohort studies most relevant to the question in hand, epidemiological results do not adequately support the concept of a causal relationship between the two air pollutants in question, PM2.5 and NO2, and asthma. Epidemiological studies predominantly show no effect of these air pollutants on allergic sensitization and the onset of allergic rhinitis. The small number of studies that have investigated the link between air pollutants and eczema largely revealed there to be no link.
If the evidence for the causal role of air pollutants in the onset of allergies is inconclusive, one must assume that it is probably not possible to achieve primary prevention of allergies by improving air quality. However, there is sufficient evidence to show that air pollutants can trigger exacerbations of allergic diseases. This alone justifies ensuring that the existing threshold values for air pollutants are adhered to, in order to protect particularly allergy sufferers from health impairments.
KeywordsParticulate matter Nitrogen dioxide Asthma Allergic rhinitis Allergic sensitization
Chronic obstructive pulmonary disease
Geographic information systems
Land-use regression model (to determine the distribution of air pollutants)
Traffic-related air pollution
Type 2 T-helper cells
Volatile organic compounds
Ambient air always contains a mixture of numerous substances that have been shown to have adverse health effects. Extensive scientific evidence has demonstrated incontrovertibly that pollutants in ambient air can harm not only the lungs, but also the cardiovascular system. Particulate matter (PM) is considered the most important air pollutant for the healthy general population, followed by ozone, which affects the respiratory tract in particular. No distinction is made in general German terminology between PM with an aerodynamic diameter of less than 10 µm (PM10) and particles with an aerodynamic diameter of less than 2.5 µm (PM2.5), whereas in scientific terminology, the term “fine particulate matter” is reserved for PM2.5 particles. Nitrogen dioxide is considered an easy-to-measure indicator of the traffic-related overall mixture, even though direct negative effects on individuals with mild asthma have also been observed in experimental and epidemiological studies. The role played in health by nitrogen monoxide (NO) will not be discussed in more detail here, since NO is of less relevance in terms of health, is rapidly oxidized to NO2 following emission anyway, and NO2 is the air pollutant indicator more commonly used for traffic-related emissions in epidemiological studies. As such, the focus of this article is on the two pollutants PM2.5 and NO2, taking into special consideration the situation in Germany and in German cities in particular. Nevertheless, it should be pointed out that PM is the air pollutant that poses the greatest and most diverse health risks in heavily trafficked cities; see, for example, the review articles on air pollution and airway diseases [1, 2, 3].
Characterization of air pollutants
Outdoor air pollutants
Particulate matter (PM, PM10, PM2.5, UFP), nitrogen dioxide (NO2), nitrogen monoxide (NO), ozone (O3), volatile organic compounds, sulfur dioxide (SO2), carbon monoxide (CO)
Tobacco smoke, biological pollutants such as animal allergens, molds, and bacteria, VOC, emissions from burning biomass in open fires to heat or cook in developing countries
Emissions from traffic, construction equipment, fossil-fueled power stations, heating with coal or wood in private homes, agriculture and industry, in particular heavy industry and the construction industry
Volcanic emissions, forest fires
PM10, PM2.5, and UFP (particles with aerodynamic diameters of <10 µm, <2.5, and <0.1 µm)
Number of particles in a certain volume
Number concentration of UFP
Elements (e. g., elemental carbon, lead, cadmium, vanadium, mercury) or chemical compounds (e. g., sulfate, nitrate, ammonium, organic substances)
The following article looks only at pollutants in outdoor air, although exposure to tobacco smoke as a result of active and passive smoking, i. e., the inhalation of tobacco smoke caused by third parties, has shown the clearest effects of all air pollutants in terms of the development of asthma and exacerbations of existing asthma [4, 5, 6].
When investigating the health effects of exposure to polluted air, a general distinction needs to be made between those effects that explain the onset of disease and those effects that cause exacerbations, increased drug use, or more rapid progression of existing disorders. Numerous studies have unanimously shown that PM (PM10, PM2.5) and NO2 exposure in asthmatics causes more exacerbations (more respiratory tract symptoms), poorer pulmonary function, and greater drug use in children as well as in adults [7, 8, 9]. Likewise, PM and NO2 exposure in patients with chronic obstructive pulmonary disease (COPD) results in more frequent exacerbations, poorer pulmonary function, and accelerated disease progression . However, with regard to the potential for the primary prevention of allergic diseases by avoiding or reducing exposure to these air pollutants, these important results are irrelevant to affected patients.
This article discusses the potential to prevent allergies by avoiding or reducing high air pollution exposure to PM2.5 and NO2. Thus, the aim is to investigate the risks for primarily healthy individuals to develop an allergy as a function of air pollution exposure. First of all, however, an example highlighting the complexity of the study aim is presented below.
A comparison of allergy prevalences in East and West Germany
Environmental factors: An increase in traffic-related pollutants; better insulation of residential buildings leads to a reduction in air exchange rates as well as possibly to indoor mold problems and greater exposure to chemicals emitted indoors
Lifestyle factors: more convenience food and other consumption patterns, more foreign travel and resultant contact with foreign allergens, less physical activity, more stress, in particular shortly after the breakdown of the GDR as a result of high unemployment, anxiety about the future, more living space, and hence less “crowding”
Other factors: fewer infectious diseases in early childhood, rarer infestation with worms and other parasites; generally less exposure to bacteria, fewer siblings, later contact with large numbers of children due to later attendance at child daycare centers
It is important to point out here that none of these Western lifestyle factors alone is able to explain the increase in allergies in East German children . Evidently, the rise in allergies in transition societies can only be adequately explained by a combination of several or all of these factors, or hitherto unidentified factors.
Air pollution exposure and allergies in epidemiological studies
Underlying design: cross-sectional studies, cohort studies, case crossover studies, registry studies, and use of routine statistical data
Allergic diseases investigated and allergy risk markers: asthma, allergic rhinitis, allergic sensitization, dermatitis and how these are methodologically determined (self-reporting by subjects, medical examination, registry study data)
Air pollutants included: PM10, PM2.5, black smoke, NO2, coarse particles (PM10–2.5), ozone, SO2, traffic-related air pollution (TRAP)
Exposure estimate: individual exposure estimate using land-use regression (LUR) models or dispersion models, calculating the distance to the main source of air pollution emitters by means of geographic information systems (GIS) or self-reporting
Main sources of air pollution levels: traffic, power stations, and heavy industry, etc.
Continent and region
Children and adults, recruiting mode, and number of study participants included
Prospective study design beginning at birth (birth cohort studies)
Reliable data on asthma, allergic rhinitis, and allergic sensitization through repeated and, where appropriate, medical examinations
Individual estimate of exposure to PM10, PM2.5, and NO2 using LUR or dispersion models
Neonates observed to adolescence
Birth cohort studies are superior to all other designs, since they take into account the perinatal period, which is a potentially relevant time window of exposure; lifelong exposure can be determined despite relocations; neonates and young children are considered particularly vulnerable to air pollutants ; and, finally, the time course of diseases and their remission can be best evaluated. For this reason, the relationships between air pollution exposure and selected allergic diseases are presented for the last systematic review of birth cohorts  in a first step and, in a second step, these are expanded on by the summaries of other systematic reviews and high-quality original publications that were published after this review.
Altogether, 15 studies, with results published up to January 2016, were identified in the relevant databases in the last systematic review on the subject of air pollutants and allergies in birth cohorts . Of these, eight were located in Europe (Oslo, Norway; BAMSE, Sweden; GINIplus and LISAplus, Germany; PIAMA, the Netherlands; INMA, Spain; GASPII, Italy; MAAS; Great Britain), four in Canada (SAGE, CAPPS, CHILD, and BCBC), two in the US (CCAAPS and CCCEF), and one in Taiwan (TBCS). The cohort sample size varied between 178 (SAGE, Canada) and 37401 (BCBC, Canada). The majority of studies on asthma had a relatively long observation period of approximately 10 years. The prevalence of allergic diseases varied between cohorts: 4–10.9% for asthma, 5–28.9% for a main asthma symptom (wheezing), 2.6–11.5% for allergic rhinitis, 16–40.4% for allergic sensitization to aero- or food allergens, and 4.9–15.5% for eczema. These differences are mainly due to the selection of a high-risk population (CAPPS) and differences in the observation time and, thus, in the age of subjects. To this, one can add geographic and cultural factors, which affect the prevalence of allergies. Most subjects were exposed to air pollutants that fall below the WHO recommendations of 10 µg/m3 for PM2.5 and 40 µg/m3 for NO2. All studies were able to draw on individually determined exposure data, and most on LUR modeling results.
Whereas the systematic reviews of birth cohort studies were able to include a maximum of 10 studies in their analyses, another systematic review published recently was able to consider 41 studies, since cross-sectional studies were also included . These meta-analyses reveal pooled effects of OR 1.03 (95% CI 1.01–1.05) for a PM2.5 increment of 1 µg/m3 and of OR 1.05 (95% CI 1.02–1.07) for an NO2 increment of 4 µg/m3. Although some of these studies are less methodologically sophisticated and there are differences between studies in terms of exposure assessment strategies, the collection of data on asthma, and the monitoring of confounding factors, the larger number of studies included significantly increases the power to detect air pollution effects. However, one should not forget that results of cross-sectional studies are not suited to determining the reasons for a causal relationship between air pollution and asthma.
Another systematic review conducted a few years earlier by Anderson et al.  also combined results from cross-sectional studies and prospective studies with similar results: the risk for asthma in childhood was statistically significantly increased depending on traffic-related air pollution.
The most comprehensive review of the topic traffic-related air pollution and asthma incidence reaches a more conservative conclusion, i. e., that there is insufficient evidence for a causal role . This conclusion summarizes the state of knowledge from studies published up to 2010. Although numerous other studies have been published on this issue since then, no compellingly different assessment has emerged. This does nothing to change the pros [27, 35, 36, 37, 38, 39, 40, 41] and cons [3, 7, 28, 42] for the effect of air pollution on the development of childhood asthma in other reviews and statements over the past 20 years.
The role of air pollutants in the new onset of asthma in adulthood is even less well understood. The handful of relevant studies show inconsistent results. Three studies report statistically significantly higher risks for asthma in increased NO2 exposure [43, 44, 45], as well as in a subpopulation of atopic individuals . Other studies, some of which evaluate several cohorts together , reveal increased risks, which, however, are not statistically significant [47, 48, 49, 50]. The handful of studies that have investigated the effects of PM2.5 on the new onset of asthma in adulthood found non-statistically significantly increased risks [47, 49].
Long-term exposure to PM2.5 and NO2 was not associated with an increased incidence of allergic rhinitis in adults in two large European cohorts .
Meta-analyses of birth cohort results revealed no statistically significant links between air pollution and allergic sensitization . A weak, statistically non-significant association was reported for PM2.5 (OR 1.05; 95%CI 1.00–1.11) per 2‑µg/m3 increment and specific sensitization to aeroallergens, but not for NO2 (OR 1.02; 95%CI 0.92–1.13) per 10-µg/m3 increment . These associations are based on six and eight studies, respectively. Only one small Australian study on adults found statistically positive links between NO2 and allergic sensitization . Therefore, the extent to which the lack of associations in childhood on the basis of virtually ideal study design with a large sample size should be interpreted more cautiously than a zero result remains questionable.
Only a handful of studies have analyzed the links between air pollution exposure and the onset of eczema [11, 58, 59, 60, 61, 62, 63]. If anything, these studies generally describe skin symptoms—at different ages (6 months, 6 years, 8–11 years)—that manifest depending on different air pollutants (PM2.5, NO2, SO2, and PM10) and which point to dermatitis. A recently published review on the role of air pollutants in dermatitis concluded that the results are controversial and that no conclusive evaluation could be made due to the scant number of studies and their methodological pitfalls . This evaluation refers to the role of air pollution in existing eczema as well as to air pollution’s causation of eczema. The only meta-analysis on PM and skin disease presents results from 13 studies on PM2.5 exposure and atopic dermatitis in children and adults . The joint effect estimate was not statistically significantly increased (OR 1.04; 95% CI 0.96–1.12) for a PM2.5 increment of 10 µg/m3. The joint effect estimate for PM10 was below 1.00. Restricting the studies to only those including children did not alter the effect estimates significantly.
While it is largely not possible to identify statistically significant links between the selected air pollutants (PM2.5 and NO2) and asthma, allergic rhinitis, eczema, and allergic sensitization, the results of laboratory studies and human exposure support the hypothesis of a possible causal link between air pollution and allergies [3, 7, 8, 66, 67, 68]. The evidence yielded by these laboratory studies on the adverse effects of particles, especially PM and diesel particles, is particularly well demonstrated, while the role of NO2 is less clear, possibly due to less specialized studies on NO2. The following mechanisms are discussed as potentially underlying particle effects: epithelial stress, a particle-induced Th2 response, and an increased Th17 response . In contrast, NO2 effects are discussed in association with neutrophilic bronchial infiltration, the production of proinflammatory cytokines, and adjuvant effects in allergen exposure . What is particularly interesting here is the apparent inconsistency between immunological effects in the laboratory studies and the evidence that is largely lacking in the epidemiological observational studies for air pollution effects on allergic sensitization.
Despite conducting an extensive literature search, presenting the most recent results, and focusing on the qualitatively high birth cohort studies most relevant to the question in hand, this summary of epidemiological results does little to support the concept of a causal relationship between the two air pollutants in question, PM2.5 and NO2, and asthma. Although in vitro studies, animal models, and human exposure demonstrate plausible potential mechanisms between particle exposure and allergic biomarkers by affecting the innate and adaptive immune system, epidemiological studies overwhelmingly show no effects on allergic sensitization and the onset of hay fever and eczema.
Asthma and other IgE-mediated allergic diseases belong to the complex diseases of multifactorial etiology. Besides environmental effects, this also includes exposure that depends on lifestyle and behavior and is determined by genetic and epigenetic make-up . As such, it is not surprising that it is impossible to filter out the effects of a single risk factor from numerous risk factors for allergies in the context of epidemiological observational studies.
If the evidence for a causal role of these air pollutants in the onset of allergies is not clearly demonstrated, one must logically conclude that the primary prevention of allergies due to the air pollutants considered here is likely to be impossible. However, there is strong and undisputed evidence that air pollutants can trigger exacerbations of allergic diseases . This alone justifies ensuring that the existing threshold values for air pollutants are adhered to, in order to protect particularly allergy sufferers from health impairments. To this, one can add the negative effect on life expectancy, cardiovascular diseases, lung cancer (as recently proven), and increased infectious diseases in early childhood, to mention but a few examples. As such, air pollutants are clearly detrimental to the health and must be kept to a minimum.
Conflict of interest
J. Heinrich declares that he has no competing interests.
- 3.Krzyzanowski M, Kuna-Dibbert B, Schneider J, editors. WHO Regional office for Europe. Health effects of transport-related air pollution. Copenhagen: World Health Organization Regional Office for Europe; 2005.Google Scholar
- 8.HEI Panel on the Health Effects of Traffic-Related Air Pollution. Traffic-related air pollution: a critical review of the literature on emission, exposure, and health effects. HEI special report 17. Boston: Health Effects Institute; 2010.Google Scholar
- 29.Heinrich J, Guo F, Fuertes E. Traffic-related air pollution exposure and asthma, hayfever, and allergic sensitisation in birth cohorts: a systematic review and meta-analysis. Geoinfor Geostat Overv. 2016;4:4.Google Scholar
- 41.Lavigne É, Bélair MA, Rodriguez Duque D, Do MT, Stieb DM, Hystad P, et al. Effect modification of perinatal exposure to air pollution and childhood asthma incidence. Eur Respir J. 2018;1701884. https://doi.org/10.1183/13993003.01884-2017. [Epub ahead of print]CrossRefPubMedPubMedCentralGoogle Scholar
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