Introduction
Air pollution is a complicated process involving the spread of distinct pollutants throughout the atmosphere. Air pollution has been found to induce diseases in humans and disorders in other living organisms, as well as destruction of the natural environment
[ 1–
2]. One type of pollutant, particulate matter (PM)
[ 3], has been associated with serious public health problems
[ 4], as has combinations of PM and other air pollutants
[ 5]. PM is classified according to its aerodynamic diameter, and the gold standard used to evaluate its transport capacity in the atmosphere and inhalation capacity through the respiratory tract
[ 6]. PM is primarily categorized as coarse (PM
10), of median aerodynamic diameter≤10 μm, and fine (PM
2.5), of median aerodynamic diameter≤2.5 μm
[ 6].
PM originates from a wide range of sources, including road dust, agricultural dust, industrial emissions, construction sites, mining operations, river beds, crustal materials, and combustion, or as secondary aerosols from distant sources
[ 7–
9]. Due to the diversity of sources, human exposure is high. Entry of PM into the respiratory tract depends on the physical characteristics, breathing mode and rate, and size of an individual
[ 10]. Moreover, PM size has been significantly related to the etiology of pertinent diseases. Frequently, smaller PM such as PM
2.5 penetrates the respiratory tract more deeply at a higher rate, and is deposited in the respiratory bronchioles and alveoli or enters the bloodstream, influencing lung function and eventually causing other disorders
[ 11]. Exposure to PM has been shown to be harmful to public health, increasing the incidence of respiratory symptoms, reducing lung function, and aggravating respiratory and cardiovascular diseases
[ 12].
PM
2.5 can also act as a carrier of other harmful constituents, such as heavy metal ions, which add to the deleterious effects of "inert" material
[ 13]. Studies analyzing the induction of respiratory diseases by exposure to PM
2.5 have yielded different outcomes. To quantitatively and accurately assess the effects of exposure to PM
2.5 on respiratory tract diseases, we performed a meta-analysis that included all relevant cohort studies published to date. This meta-analysis showed that exposure to PM
2.5 increased the risk of respiratory tract disease.
Materials and methods
Systematic ascertainment of correlative studies
The online databases, including PubMed (National Library of Medicine, Bethesda, MD, USA), Web of Science (Thompson Scientific, Philadelphia, PA, USA), and Embase (Excerpta Medica Database, the Netherlands) were searched for cohort studies published and indexed through May 4, 2016 on the epidemiology of respiratory tract diseases associated with PM2.5 air pollution. Search strings, both free text and medical subject headings (MeSH), included (PM2.5 OR "particulate matter") AND (wheezing OR bronchitis OR cough OR asthma OR pneumonia OR COPD OR "lung cancer" OR "respiratory infections" OR "respiratory tract diseases"). Based on article titles, abstracts, and full texts, these cohort studies were screened for those fulfilling our inclusion criteria. Cohort-specific results reported in previous meta-analyses alone were also considered in the current analysis.
Inclusion criteria
All epidemiological studies involving the impact on human health of exposure to PM2.5 were screened. Health outcomes of interest were morbidities of respiratory tract diseases, according to ICD9 or ICD10, including pneumonia, asthma, bronchitis, upper respiratory tract infections, lower respiratory infections (LRI), wheezing, cough, chronic obstructive pulmonary disease, and lung cancer (Supplementary Table 1). Studies were included if they had cohort designs for respiratory diseases and if they reported relative risk (RR) or odds ratio (OR) with 95% confidence intervals (CIs).
If multiple studies reported an association between respiratory tract disease and PM2.5 in the same study cohort at different times, the latest one was chosen. However, if these studies reported different outcomes in the same cohort, each was included. Only studies published in English and exclusively involving human subjects were included. Cohort-specific results reported in previous meta-analyses were considered. If that cohort was included in a meta-analysis that included several other cohorts, the latest publication by this cohort was included.
Exclusion criteria
Case-control studies, case series, and case reports were excluded, as were studies lacking appropriate data (e.g. useful RRs or ORs and 95% CIs in related cohort studies). These criteria were used to maximize sensitivity and ensure non-omission of any relevant study.
Data extraction
All selected publications were screened independently by two investigators (Q.L. and C.X.), and data extracted using a standardized form. Conflicts were resolved by discussions between the two investigators.
Meta-analysis
Effect estimates for all data collected from the selected studies were summarized using STATA software (version 11; Stata Corp, College Station, TX, USA). The unadjusted RRs and ORs with their 95% CIs were integrated to analyze the strength of the risk of respiratory tract diseases in participants exposed to PM
2.5. Heterogeneity among studies was examined using a chi-square-based Q-statistic test and the standard
I2 test. The Q-statistic test can only determine the presence or absence of heterogeneity, not the degree of heterogeneity. As the
I2 test may quantify the extent of heterogeneity in a meta-analysis
[ 14], two methods were chosen to simultaneously assess heterogeneity. Between-study heterogeneity reflected variations in study outcomes among different studies due to inherent differences in study design/populations/exposures, not to chance alone. All pooled RRs were calculated using a random effects model.
I2 showed that heterogeneity accounts for a percentage of the overall variability in random error.
I2<40%, 30%-60%, 50%-90%, and 75%-100% represented unimportant, medium, substantial, and high degree of heterogeneity, respectively
[ 15].
Subjects were stratified into subgroups based on heterogeneity, age, region, PM
2.5 exposure level and source, and differences between groups and risk factors were calculated
[ 16]. Moreover, sensitivity analyses were performed to estimate the stability of the outcomes. That is, one study at a time was iteratively removed and the results of the remaining studies were determined
[ 17]. Begg funnel plots and the Egger test of asymmetry were performed to statistically evaluate publication bias; a
P value<0.05 was considered indicative of publication bias.
Results
Characteristics of the eligible studies assessed by meta-analysis
A review of the PubMed, Web of Science and Embase identified 1,126 eligible studies published in English. Based on the inclusion/exclusion criteria for the effects of exposure to PM
2.5 pollution on respiratory tract diseases, 35 related studies were retrieved
[ 18–
52]. A flow diagram of the literature search and selection procedure is shown in
Fig. 1.
Table 1 shows the details of each of the 35 studies; in these articles, there were 12 outcomes related to wheezing, 5 to bronchitis, 12 to cough, 14 to asthma, 1 to pneumonia, 4 to lower respiratory tract illness (LRI), 0 to upper respiratory tract illness (URI), 4 to lung cancer, 0 to COPD, and 2 to respiratory infections. These 35 articles included a total of 1,135,203 subjects with different respiratory tract diseases. Primary outcomes in our meta-analysis included the incidence of newly developed or exacerbated respiratory tract diseases. These participants resided in a variety of countries or regions and included subjects in different age groups. The mean, median and 50% interquartile range (IQR) for PM
2.5 ranged from 3.60 to 100 μg/m
3. There were seven articles on traffic-related air pollution and two meta-analyses that included unpublished data of some birth cohort studies (
Table 1).
Evidence synthesis
Pooled analysis of the 35 included articles showed that exposure to PM2.5 pollution significantly increased the RR for respiratory tract diseases for (RR= 1.076, 95% CI: 1.050, 1.103; Pheterogeneity<0.001, I2 = 93.6%). To assess differences among subgroups, studies were divided by the age of the participants (children or adults), geographic areas (North America, Europe, Oceania, or Asia), types of diseases, and sources of PM2.5 (traffic-related or non-traffic related air pollution) (Figs. 2-5). Studies in children were stratified by types of disease, and extent of exposure concentrations (Table 2, Fig. 6). The pooled RRs in the random-effects model were 1.104 (Table 2 and Fig. 2) for children, 1.099 for Europe, 1.090 for North America, 1.064 (Fig. 3) for Asia, 1.073 for wheezing, 1.153 for LRI, and 1.048 (Fig. 4) for cough. In addition, the pooled RRs exposed to traffic-related and non-traffic related air pollution were 1.085 and 1.076 (Fig. 5), respectively. The pooled RRs in children showed that the rates of wheezing (8.2%), cough (7.5%), and LRI (15.3%) were significantly increased. In adults, however, no positive association was found (Table 2). The pooled RRs in children exposed to PM2.5 concentrations<25 μg/m3 and≥25 μg/m3 were 1.091 and 1.126 (Fig. 6), respectively. However, other subgroups showed no association between RR and exposure to PM2.5.
Sensitivity analysis
Sensitivity analysis was performed by re-analyzing RR after removing one study at a time. The correlation between exposure to PM2.5 pollution and the RR of respiratory tract disease was not driven by any individual study, with no alterations in the significance of the pooled RRs, suggesting that the combined RR remained stable and reliable. Sensitivity analysis indicated that the omission of any one study resulted in RRs between 1.057 (95% CI: 1.038, 1.075) and 1.080 (95% CI: 1.049, 1.112).
Publication bias
Table 2 shows no funnel plot asymmetry, while P values of the Begg and Egger tests were greater than 0.05 in both the global and stratified analyses, respectively. These findings indicated a lack of publication bias.
Discussion
Previous epidemiological and experimental studies have been unable to definitively determine the specific mechanisms by which exposure to PM has adverse effects on human health. However, accumulated evidence suggests that the most deleterious effects of PM are dependent on particle size, with PM
2.5 being especially harmful
[ 53–
54]. Exposure to PM
2.5 has been found to increase health risks, particularly with regard to respiratory tract diseases
[ 55]. Mortality has been regarded as the one important indicator of the effects of PM
2.5 pollution on health outcomes
[ 56]. Several case-control studies have also assessed daily hospital admissions or emergency department visits
[ 57]. However, these variables are limited by the lack of persistent observation, restriction of end points, and recall bias. Therefore, this meta-analysis was performed to clarify the relationship between exposure to PM
2.5 and the incidence or aggravation rate of respiratory tract diseases in cohort studies. In addition, studies were stratified by age, geographic location, and the source and concentration of PM
2.5.
This systematic review found that exposure to PM
2.5 was positively correlated with risk of respiratory tract disease, especially in children; in subjects with wheezing, cough, and LRI; and in populations in Europe, North America, and Asia; The pooled RRs were greater for traffic-related than non-traffic-related air pollution. Ultimately, we found that PM
2.5 in children was significantly associated with cough, wheezing, and LRI. Furthermore, in children, pooled RRs were greater for high (≥25 μg/m
3) than low (<25 μg/m
3) PM
2.5 concentrations. These findings suggested that traffic-related PM
2.5 did greater harm to the human body, and that exposure to PM
2.5 pollution may pose an increased risk for respiratory tract disease, especially in children exposed to high concentrations of PM
2.5. These results are consistent with those of previous reports
[ 58–
59], as well as being more accurate than the results of a previous meta-analysis of case-control studies
[ 60].
Above all, this meta-analysis included many more articles with a larger population, especially birth cohorts, than previous meta-analyses. Second, longitudinal cohort studies with complete and reliable information are considered less likely to be influenced by confounding and better able to address the temporal sequence of events. Finally, this study not only revealed a strong association between PM2.5 and respiratory tract diseases in general, but also strong correlations between PM2.5 and specific types of respiratory tract diseases (wheezing, cough and LRI). Therefore, the results of this meta-analysis could amplify and complete those of earlier meta-analyses.
However, the pathological mechanisms underlying the effects of PM
2.5 exposure on the respiratory tract are not fully understood. PM size may be affected by chemical, biologic, and physical properties, resulting in various pathological consequences
[ 6]. There are several plausible biomedical explanations for associations between exposure to PM
2.5 and respiratory tract diseases. Owing to its fine consistency, PM
2.5 can be deposited more deeply into the lungs. Moreover, these particles may contain toxic components or contaminants, such as nitrates, sulfates, acids, and metals, originating from combustion processes or similar activities
[ 61]. These particles can therefore lead to stress, inflammation, and allergy. Our results showed that PM
2.5 exposure resulted in a greater incidence of cough, wheezing, and LRI in children than in adults, which may be related to differences in the structure of the respiratory tract in adults and children. Specifically, the immature respiratory system in children may be more sensitive to PM
2.5. PM
c of aerodynamic diameter 2.5-10 μm mainly derives from the soil and abrasive mechanical processes. These particles may transport biologic materials, such as bacteria, molds, and pollens, which may have harmful effects on the respiratory system
[ 62–
63]. Therefore, some infectious bacterial respiratory diseases or hay fever are more likely to manifest after lengthy exposure to PM
c rather than PM
2.5. Our results are consistent with these findings.
We also found that the correlation between PM2.5 exposure and respiratory diseases was stronger in European and North American populations, probably due to more studies of PM2.5 were conducted in these populations. The risk of respiratory diseases was also higher following exposure to high than low quantities of PM2.5, suggesting that the concentration of PM2.5 is also a risk factor for respiratory diseases.
This meta-analysis had several limitations. First, some of the outcomes demonstrated heterogeneity. We utilized a random-effects model, with stratified analysis performed to make up for this shortcoming. Second, non-English publications and unpublished results were excluded. Some of these studies may have included negative outcomes, which could have influenced our results. Third, we could not exclude residual confounders, which may have influenced our results. Fourth, the limitations of data collection from all studies prevented a comparison of results from different climate zones, with different temperatures and humidity, which may have influenced the correlation between PM2.5 exposure and respiratory diseases.
In conclusion, we found that PM2.5 may play an important role in respiratory tract diseases, especially in children exposed to high concentrations of PM2.5. Additional studies are needed to assess the quantification and identification of other, as yet undetermined, harmful compounds in ambient air particles, and to determine the underlying mechanisms that cause these particles to affect human health.
2017 by the Journal of Biomedical Research. All rights reserved