Flowchart shows study cohort enrollment criteria. CT indicates computed tomography.
A, Concentration of particulate matter with aerodynamic diameter less than 2.5 μm (PM2.5) per 1 × 1 km2. B, Concentration of nitrogen dioxide (NO2) per 1 × 1 km2.
Percentage increase in CAC scores with 95% CIs (error bars). The interquartile range increases in pollutants are 30 μg/m3 for particulate matter with aerodynamic diameter less than 2.5 μm (PM2.5), 20 μg/m3 for nitrogen dioxide (NO2), and 15 μg/m3 for ozone (O3); there was a 50% decrease for distance from a roadway. The primary model included age, sex, body mass index, smoking status, smoking years, cigarettes per day, alcohol consumption, education, exercise, urbanization, regions, distance to hospital, and Beijing residence (yes or no). The primary model plus biomarkers also included levels of total cholesterol, high-density lipoprotein cholesterol, low-density lipoprotein cholesterol, triglycerides, and high-sensitivity C-reactive protein. The primary model plus multiple exposures also included PM2.5, NO2, O3, and distance to road variables.
Odds ratios and 95% CIs (error bars) for the presence of CAC and severe CAC (>400 Agatston units) adjusted for age, sex, body mass index, smoking status, smoking years, cigarettes per day, alcohol consumption, education, exercise, urbanization, region, distance to hospital, and Beijing residence (yes or no). NO2 indicates nitrogen dioxide; O3, ozone; and PM2.5, particulate matter with aerodynamic diameter less than 2.5 μm.
eMethods. Supplemental Methods
eTable 1. Summary Statistics and Correlations of the Exposure Variables in the Study Participants
eTable 2. Main and Sensitivity Analyses for Percent Change and 95% CI in CAC Associated With a Difference in Long-term Exposure Variables Among the CREATION Participants
eTable 3. Sensitivity Analyses With Detailed Individual-Level Risk Factors for Associations Between Long-term Air Pollution Exposure Variables and CAC-score Among a Subset of Participants (n = 1850)
eTable 4. Effect Modifications in Associations of CAC With Long-term Exposure to PM2.5 and NO2 for Selected Demographics and Risk Factors
eTable 5. Comparisons of Health Effect Estimates in and Outside Beijing
eFigure 1. Spatial Distribution of Estimated Annual Mean Exposure to PM2.5, NO2, and O3 in the Year of 2015 at the Participants’ Home and Regional Classifications
eFigure 2. Percent Change and 95% CI in CAC Associated With PM2.5 (30 µg/m3) Averaged Over Multiple Years Prior to Baseline Using Land Use Regression Model With Adjustment for Satellite-derived PM2.5 Observations
eFigure 3. Concentration-Response Relationships Between Long-term Exposure to PM2.5 and NO2 and the Estimated Percent Change in CAC Score, Modeled by a Natural Spline With 3 Degrees of Freedom
eFigure 4. Associations Between CAC and Long-term Exposure Variables Categorized by Quartiles
eFigure 5. Comparisons of Heath Effect Estimates for Associations of PM2.5 and Proximity to Traffic Exposures With Degrees of CAC, Thoracic Aortic Calcification (TAC) or Abdominal Aortic Calcification (AAC) Between This Study and the Previous Studies
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Wang M, Hou Z, Xu H, et al. Association of Estimated Long-term Exposure to Air Pollution and Traffic Proximity With a Marker for Coronary Atherosclerosis in a Nationwide Study in China. JAMA Netw Open. 2019;2(6):e196553. doi:10.1001/jamanetworkopen.2019.6553
Are long-term exposure to ambient air pollution and proximity to traffic associated with subclinical atherosclerosis?
In this population-based cross-sectional study of 8867 Chinese participants, long-term exposure to ambient nitrogen dioxide and fine particulate matter with aerodynamic diameter less than 2.5 μm was independently associated with a higher coronary artery calcium score, a key atherosclerotic marker. Associations with ozone and proximity to traffic were less consistent.
Long-term exposure to ambient air pollution may be an important risk factor for coronary atherosclerosis.
Epidemiologic evidence of the mechanisms of the association between long-term exposure to air pollution and coronary heart disease (CHD) is limited and relies heavily on studies performed in Europe and the United States, where air pollution levels are relatively low. In particular, the association between air pollution and CHD in patients with underlying risks for CHD is understudied.
To determine whether air pollution and proximity to traffic are associated with the coronary artery calcium (CAC) score, a key atherosclerotic marker.
Design, Setting, and Participants
In this prospective, population-based cross-sectional study in a large-scale setting in China, 8867 consecutive patients aged 25 to 92 years with suspected CHD were recruited between November 17, 2015, and September 13, 2017. Participants were excluded if they had previous myocardial infarction, stenting, or coronary artery bypass grafting or incomplete risk factors and exposure data. Each participant underwent assessment of CAC and CHD risk factors at baseline. Data were analyzed from December 2017 to November 2018.
Annual means of fine particulate matter with aerodynamic diameter less than 2.5 μm (PM2.5), nitrogen dioxide (NO2), and ozone (O3) were estimated at the participants’ residences using a validated geostatistical prediction model. Exposure to a nearby roadway was also estimated.
Main Outcomes and Measures
Computed tomography measurement of CAC score.
The mean (SD) age of the 8867 participants was 56.9 (10.4) years; 4378 (53.6%) were men. Annual mean (SD) PM2.5, NO2, and O3 measurements were 70.1 (20.0), 41.4 (14.7), and 93.9 (10.5) μg/m3, respectively. The mean (SD) CAC score was 91.4 (322.2) Agatston units. Exposure to PM2.5 and NO2, adjusting for CHD risk factors and multiple pollutants, were independently associated with increases in CAC scores of 27.2% (95% CI, 10.8% to 46.1%) per 30 μg/m3 PM2.5 and 24.5% (95% CI, 3.6% to 49.7%) per 20 μg/m3 NO2. For PM2.5, odds of both detectable CAC (Agatston score >0; odds ratio, 1.28; 95% CI, 1.13 to 1.45) and severe CAC (Agatston score >400; odds ratio, 1.59; 95% CI, 1.20 to 2.12) were increased. Associations of CAC with PM2.5 and NO2 were greater among male participants (PM2.5: 42.2%; 95% CI, 24.3% to 62.7%; NO2: 45.7%; 95% CI, 25.3% to 69.5%) and elderly participants (PM2.5: 50.1%; 95% CI, 28.8% to 75.0%; NO2: 55.5%; 95% CI, 31.8% to 83.6%) and those with diabetes (PM2.5: 62.2%; 95% CI, 30.9% to 101.0%; NO2: 31.2%; 95% CI, 13.9% to 51.0%). Independent association with CAC score was 9.0% (95% CI, −1.4% to 20.4%) for O3 per 15 μg/m3 and 2.4% (95% CI, −0.6% to 5.4%) for distance near roadway per 50% decrease.
Conclusions and Relevance
In this large Chinese study, long-term exposures to PM2.5 and NO2 were independently associated with severity of CAC. This finding may provide support for the pathophysiological role of coronary atherosclerosis through which air pollution exposure may be associated with CHD.
Ambient air pollution is a major contributor to the global burden of disease, accounting for an estimated 4.2 million deaths in 2015.1 Although the effect of air pollution on public health is potentially very large, the current air pollution guidelines used worldwide have relied principally on findings from studies conducted in Europe and North America where air pollution levels are relatively low compared with other areas experiencing more recent rapid industrialization.2 Information on associations between exposure and disease from regions with exceptionally high ambient air pollution, such as China, would be useful to produce more accurate estimates of air pollution–attributable disease burden, which in turn can be used to prioritize public health responses, especially in developing countries.
Cardiovascular disease is the leading cause of death worldwide, with available evidence showing that it is associated with long-term exposure to air pollution and proximity to traffic.3 A likely pathway underlying these associations involves the initiation or acceleration of atherosclerosis.3 Atherosclerosis is a lifelong process; therefore, the effects of air pollution exposure on atherosclerosis are likely to be long term. If an association between air pollution and subclinical atherosclerosis were established, it could provide an opportunity to intervene before disease is manifested clinically by way of community-level efforts to control pollution exposures. Common approaches to detecting subclinical atherosclerosis include noninvasive measurement of coronary artery calcium (CAC) or carotid intima-media thickness.4 Compared with carotid intima-media thickness, CAC reflects a more advanced stage of atherosclerosis involving calcification of plaque and is a better predictor of cardiovascular disease.4 Associations between air pollution and carotid intima-media thickness have been reported in some previous studies.5-8 Evidence regarding the association between air pollution and coronary atherosclerosis, determined using CAC scoring, is still very limited.8,9
China is the most populated country in the world and has a large estimated disease burden associated with air pollution.1 Cohort studies of air pollution and cardiovascular health are still scarce and have been largely limited to the investigation of effects on mortality.10 Given the increasing public concern regarding air pollution, the Chinese government has recently implemented an unprecedented effort to characterize major air pollutant exposures with more than 1400 widespread monitoring stations established nationwide.11 Here we use this valuable resource by applying advanced exposure estimation methods for health effect investigation. We hypothesize that long-term exposure to air pollution or proximity to traffic is associated with increased risk of CAC in a well-characterized cohort of Chinese adults.
This cross-sectional study used baseline data collected from a prospective cohort (the CREATION cohort) of 8867 consecutive patients aged 25 to 92 years at Fuwai Hospital in Beijing, China (eMethods in the Supplement). The participants were suspected of having coronary heart disease (CHD) and for this reason underwent cardiac computed tomography to evaluate the presence and amount of CAC between November 17, 2015, and September 13, 2017. Cardiac imaging was ordered by primary cardiologists. The participants had relatively low pretest probability of CHD (mean [SD], 27.3% [15.1%]); 2587 patients had no symptoms, 5721 had nonanginal chest pain, 449 had atypical angina, and 110 had typical angina. Participants were excluded if they had previous myocardial infarction, stenting, or coronary artery bypass grafting or incomplete risk factors and exposure data. More details regarding the study cohort are available in Figure 1 and eMethods in the Supplement. All participants provided written informed consent, and the study was approved by the institutional review board of the Chinese Academy of Medical Sciences Fuwai Hospital. This report follows the Strengthening the Reporting of Observational Studies in Epidemiology (STROBE) reporting guideline.
Details of the measurement of CAC have been published elsewhere.12 In brief, all patients underwent imaging with a second-generation dual-source computed tomography system (Somatom Definition Flash; Siemens Healthcare) with a standardized scanning protocol, using 128 × 3-mm section collimation, 75-millisecond rotation time, and 120-kV tube voltage. Coronary calcium lesions were defined as having an attenuation threshold greater than or equal to 130 Hounsfield units (HU) and an area greater than or equal to 1 mm2. Images were analyzed with the system’s integrated software (Syngo.Via; Siemens Healthcare). The total calcium burden in the coronary arteries was quantified by the scoring algorithm proposed by Agatston et al.13 The products of the area of each calcified plaque and peak attenuation, defined as 1 (130-199 HU), 2 (200-299 HU), 3 (300-399 HU), and 4 (≥400 HU), were summed for the left main coronary artery, left anterior descending coronary artery, left circumflex coronary artery, and right coronary artery to determine the total CAC score.
The method for estimating long-term outdoor air pollution concentrations for each study participant has been described in detail elsewhere.14 In brief, we developed a hierarchical land-use regression modeling approach for fine particulate matter less than 2.5 μm in aerodynamic diameter (PM2.5) and nitrogen dioxide (NO2) on the basis of annual mean daily monitoring data (2014-2015) from 1419 regulatory monitors nationwide. The models incorporated a wide diversity of geographic features (eg, traffic network, point of interest, population density, and land use), satellite-derived PM2.5 or NO2 observations at ground level calibrated by chemical transport model estimates, and meteorological data, with regression residuals smoothed by universal kriging. The performance of these models ranged from good to excellent, as assessed by the cross-validation (out-of-sample validation; R2 = 0.73-0.89). The model resolution was finer than 1 × 1 km2 for the entire country of China. Residence-specific annual mean PM2.5 and NO2 concentrations were estimated for 2015 and were used as the primary exposure measures. For O3, we estimated annual mean concentrations by interpolation of O3 observations from the proximal O3 monitoring sites using ordinary kriging. As an alternative assessment of traffic-related associations, we assessed residential proximity to traffic, estimated by the distance to any of the nearest roadways on a natural logarithm scale,15 as a secondary exposure variable. This variable is a proxy of exposure to traffic mixtures, including tailpipe and nontailpipe emissions and roadway noise.
In the sensitivity analysis, we tested different exposure time windows to our outcome. For PM2.5, we estimated cumulative exposures back for 3-, 4-, 5-, 6-, and 10-year periods before 2015. This analysis took advantage of our single-year fine-scale land-use regression predictions together with the 10-year temporal trend (2004-2014) generated from national satellite-derived data16 (eMethods in the Supplement). For NO2 and O3, a monitoring period averaged between 2014 and 2015 was examined.
We fit multiple linear regression models in analyzing associations of long-term air pollution exposure (PM2.5, NO2, and O3) and proximity to traffic with the CAC score in separate, single-pollutant models. The CAC score was modeled on a continuous scale using a logarithm (CAC score + 1) transformation to account for skewness of the distribution.
We developed statistical models in stages, by incrementally increasing control for a large set of covariates according to a priori knowledge from previous studies.8,17 We also used a change-in-estimate criterion by including variables if they changed the effect estimates for the unadjusted association between air pollutants and CAC by more than 10%. The primary model included the following individual-level variables: age, sex, body mass index, smoking (status, duration, and intensity), alcohol consumption, education, and physical activity. To address potential behavioral confounders that differed by geography, we also added area-level variables, including urbanization (≥2500 population per 1 × 1-km2 grid), study region (ie, north, southeast, and southwest), Beijing residence (yes or no), and categories of residence distances to Fuwai Hospital (<30, 30-150, 151-300, 301-500, and >500 km) in the primary model. Potential effect modification was evaluated for specific participant characteristics (age and sex), disease risk factors (body mass index, smoking, diabetes, and statin use), and geography (region and urbanization), which have been suggested to act as effect modifiers in prior studies.7-10,18 Because cardiovascular disease mortality risk increases in women after menopause,3 in an additional analysis, we restricted our analysis to postmenopausal women. To assess exposure-response associations, we refit the models using natural regression splines. To explore nonlinearity associations, we categorized exposure estimation by quartiles.
In sensitivity analyses, we used the same model but restricted analysis to participants with predicted annual exposure concentrations lower than the national standards in China (<35 and <40 μg/m3 for PM2.5 and NO2, respectively) or median exposure for O3 (<100 μg/m3). Second, we added to the model high-sensitivity C-reactive protein, total cholesterol, high-density lipoprotein cholesterol, low-density lipoprotein cholesterol, and triglyceride levels in the subset of 6538 participants from whom blood samples were collected. Third, the use of lipid-lowering and antihypertensive medications was added to the models. Fourth, individual-level data that included detailed information on the built environment, socioeconomic status (eg, income and employment status), and residential moving history were available for a subset of 1850 participants who completed an additional environmental survey. The sensitivity of our primary model estimates to the addition of each or a group of those covariates was also assessed. Fifth, to account for possible spatial clustering of the outcome, we used a mixed-effects model with a random effect for the 6-digit postal code (n = 917). Sixth, to assess the robustness of effect estimates in the primary model, we estimated the associations in a subset after excluding the most influential participants (Cook distance > 4/total sample size). Seventh, as noted already, we examined the effects of replacing our primary exposure variables with exposures of longer durations (2-year means for NO2 and O3, and 2-, 3-, 4-, 5-, 6-, and 10-year means for PM2.5). Eighth, multipollutant models were used to assess the independent effects of all the air pollutants and distance variable.
To compare with similar studies,6,19,20 we also assessed the association using 2 binary categorizations of CAC—detectable (CAC score >0 Agatston units) or severe (CAC score >400 Agatston units)—in logistic regression models. The presence and severity of CAC represent underlying coronary atherosclerosis in incipient and advanced stages.21 R statistical software version 3.4.2 (R Foundation) was used for developing the pollution exposure models, and SAS statistical software version 9.4 (SAS Institute) was used for the health model analyses. The statistical significance threshold was .05, and all tests were 2-sided.
Of the 8867 participants with a CAC score, 8168 had estimated outdoor residential pollutant concentrations for the year of the baseline examination. The participants’ mean (SD) age was 56.9 (10.4) years; 4378 (53.6%) were men (Table). More than 30% were smokers, 14.5% had at least a college education, 49.0% had diagnosed hypertension, and 5.0% had moved residence in the last 5 years.
Annual mean PM2.5, NO2, and O3 measurements were 70.1 (20.0), 41.4 (14.7), and 93.9 (10.5) μg/m3, respectively. Annual mean air pollutant concentrations varied substantially among the study participants (eTable 1 in the Supplement), with all pollutants being highest for participants in the Hebei province and lowest for those in the south (Figure 2; eFigure 1 in the Supplement). The participants were exposed to higher concentrations of PM2.5 and NO2 in urban areas than in rural areas. Predictions for PM2.5 were positively correlated with NO2 and O3 (Spearman correlation coefficients, 0.72 and 0.53, respectively) and negatively correlated with proximity to a roadway (Spearman correlation coefficient, −0.10). Of the participants, 7728 (95.0%) had estimated exposures greater than 35 μg/m3 for PM2.5 and 4551 (56.0%) had estimated exposures greater than 40 μg/m3 for NO2.
The mean (SD) CAC score was 91.4 (322.2) Agatston units. Long-term exposure to PM2.5, NO2, and O3, as well as distance to the nearest roadway, were all associated with higher CAC score in the crude, moderately adjusted, and fully adjusted single-pollutant models (fully adjusted single-pollutant model, PM2.5 per 30 μg/m3: 29.6%; 95% CI, 15.7%-45.2%; NO2 per 20 μg/m3: 33.2%; 95% CI, 16.4%-52.4%; O3 per 15 μg/m3: 10.8%; 95% CI, 0.9%-21.8%; distance to roadway per 50% decrease: 3.2%; 95% CI, 0.3%-6.2%) (Figure 3; eTable 2 in the Supplement). Independent association with CAC score was 9.0% (95% CI, −1.4% to 20.4%) for O3 per 15 μg/m3 and 2.4% (95% CI, −0.6% to 5.4%) for distance near roadway per 50% decrease. Associations were not substantially changed by additional adjustment for medications and blood biomarkers, accounting for neighborhood clustering, use of alternative exposure durations, and exclusion of data with extreme observations (eTable 2 and eFigure 2 in the Supplement). The addition of individual home environment variables (eg, environmental tobacco smoking, use of air conditioner, air purifier, cooking stoves, or a ventilation system) in a subgroup analysis of 1850 participants, the addition of socioeconomic status variables (eg, income and employment status), or the exclusion from the subgroup analysis of 88 participants who had moved similarly did not meaningfully change the estimates (eTable 3 in the Supplement).
When we restricted the analyses to the subset of participants with predicted exposure concentrations below the national standard (or median of exposure distribution), the association between NO2 and CAC was statistically significant (NO2 per 10 μg/m3: 24.0%; 95% CI, 6.4% to 44.5%). The association with O3 was not significant (O3 per 10 μg/m3: 7.4%; 95% CI, −0.5% to 16.1%). The association between PM2.5 and CAC in postmenopausal women was significant (PM2.5 per 10 μg/m3: 34.5%; 95% CI, 5.8% to 70.9%).
In the multipollutant models with all exposure variables included, the effect estimates for both PM2.5 and NO2 were largely unchanged, with a 27.2% (95% CI, 10.8%-46.1%) greater CAC score for a 30-μg/m3 increase in PM2.5 and a 24.5% (95% CI, 3.6%-49.7%) greater CAC score per 20-μg/m3 increase in NO2. The concentration-response curve suggested little evidence of a nonlinear association with either PM2.5 or NO2, (eFigure 3 in the Supplement). Estimating associations by quartiles of the pollutants confirmed the reasonably linear nature of the concentration-response curves (eFigure 4 in the Supplement).
In the logistic regression analyses, there were higher odds of the presence of CAC with increasing exposures to all air pollutants and distance to roadway variables (PM2.5 per 30 μg/m3: odds ratio [OR], 1.28; 95% CI, 1.13-1.45; NO2 per 20 μg/m3: OR, 1.27; 95% CI, 1.23-1.32; O3 per 15 μg/m3: OR, 1.12; 95% CI, 1.01-1.24; distance to roadway per 50% decrease: OR, 1.04; 95% CI, 1.00-1.07) (Figure 4). Also, the associations with severe CAC scores were greater in participants with increased exposure to PM2.5 (OR, 1.59; 95% CI, 1.20-2.12) or NO2 (OR, 1.60; 95% CI, 1.18-2.17).
We observed stronger associations between air pollutants (PM2.5 and NO2) and CAC score in men (PM2.5: 42.2%; 95% CI, 24.3% to 62.7%; NO2: 45.7%; 95% CI, 25.3% to 69.5%) and older (age >60 years) participants (PM2.5: 50.1%; 95% CI, 28.8% to 75.0%; NO2: 55.5%; 95% CI, 31.8% to 83.6%) (eTable 4 in the Supplement). Participants with diabetes had larger NO2 association estimates than did participants without diabetes (PM2.5: 62.2%; 95% CI, 30.9% to 101.0%; NO2: 31.2%; 95% CI, 13.9% to 51.0%), and participants in the north had larger association estimates than did participants in the southeast regions (NO2 per 20 μg/m3, north region: 42.0%; 95% CI, 21.7% to 65.6%; southeast region: −9.2%; 95% CI, −32.1% to 21.4%). There were no clear differences in the pollutant association estimates between local Beijing and non-Beijing residents (local Beijing residents, per 1-SD increase in PM2.5: 10.3%; 95% CI, 1.8% to 19.4%; NO2: 9.2%; 95% CI, 0.9% to 18.3%; and O3: −3.2%; 95% CI, −11.5% to 6.0%; and non-Beijing residents, per 1-SD increase in PM2.5: 16.1%; 95% CI, 9.4% to 23.1%; NO2: 14%; 95% CI, 7.1% to 21.4%; O3: 9.9%; 95% CI, 3.5% to 16.7%) (eTable 5 in the Supplement).
In this large Chinese study, long-term exposures to PM2.5, NO2, and O3 and proximity to traffic were associated with subclinical coronary atherosclerosis as assessed by the CAC score in residents with potential risk of CHD. The findings for PM2.5 and NO2 were robust to the use of various exposure durations and to controlling for major known CHD risk factors and copollutants. The associations were stronger among men, elderly participants, and those with diabetes. Given that CAC is strongly associated with total CHD events,4 coupled with the recently reported finding that higher long-term PM2.5 exposure was associated with a higher risk of CHD mortality in China,10 this study may provide evidence suggesting that coronary atherosclerosis is a pathological pathway through which air pollution exposure potentially increases mortality associated with CHD.
Major strengths of our study include the large population sample size, the use of advanced methods for estimating individual-level long-term outdoor exposure concentrations, and the high quality of individual information on both the outcome measures and potential confounding factors. Compared with numerous epidemiological studies in China that estimated air pollution exposures from either proximal monitors22 or regional modeling estimates (≥10 × 10-km spatial resolution),10 our exposure models produced individually resolved exposure estimates that allowed us to use accurate fine-scale contrast in investigating the association between air pollution exposure and atherosclerosis.
The associations identified in our study were likely more apparent than those in prior studies owing to the very broad range of ambient air pollution concentrations we observed. In addition, this is a population at risk for coronary atherosclerosis. Prior studies6,9,19,20 showing an association of air pollution or traffic exposure with the degree of CAC were very limited, with mostly null findings. A higher degree of CAC was associated with exposure to nearby roadways in the Ruhr area of Germany,9 and an association between PM2.5 and thoracic aortic calcifications was recently reported elsewhere.17 In the Multi-ethnic Study of Atherosclerosis,8 higher exposures to PM2.5 and NO2 were associated with faster progression of CAC, but cross-sectional associations, such as those seen in this study, have not been observed.6 Compared with previous studies of calcification in less-polluted regions, the observed magnitude of our estimates seemed smaller for PM2.5 (eFigure 5 in the Supplement). This is in line with a recent Global Burden of Diseases analysis1 indicating a steeper change in relative risk for countries at much lower levels of PM2.5 compared with those at higher values.
In 2015, more than 95% of the Chinese population was exposed to concentrations of PM2.5 and NO2 greater than the minimum level of our study.14 Because more than 40% of all deaths in China are attributable to cardiovascular disease,23 the potential contribution of air pollutants to the burden of cardiovascular disease in China is very large. Improving air quality to, for example, the Chinese national standards of 35 μg/m3 for PM2.5 and 40 μg/m3 for NO2 may lead to a longer life span.24 The association with NO2 exposure on CAC persisted even when the analysis was restricted to concentrations less than 40 μg/m3, suggesting that associations may occur even below this level.
In our study, we also found that long-term exposure to PM2.5 and NO2 was associated with increased likelihood of both the presence of detectable CAC at any amount, and the most severe levels of CAC; the risk of severe CAC was most pronounced. This is consistent with 2 US studies25,26 that observed higher risks of mild and severe CHD associated with exposure to PM2.5. Together, these findings and the results of our study indicate that individuals at potential risk for CHD are a population that is especially susceptible to air pollution exposures.
Mechanisms by which PM2.5 exposure affects atherogenesis are not well elucidated. It has been proposed that the generation of oxidative reaction products is initiated by the reaction of pollutants with lipids or cellular membranes in the airways and lung alveoli, with circulating products triggering atherogenic mechanisms such as lipid peroxidation and high-density lipoprotein dysfunction.3 Persistent activation of this pathway is associated with the development of atherosclerosis.27 We cannot conclude from our study that NO2 per se is the specific pollutant responsible for these estimated effects. Nitrogen dioxide may simply be an indicator of more harmful traffic mixtures, including ultrafine particles and diesel exhaust black carbon. Diesel exhaust and ultrafine particles have been shown to elicit harmful biological responses in experimental models.28 Indeed, we observed that exposure to NO2 was associated with CAC and that adjusting for roadway proximity attenuated its association with NO2. Living close to a roadway is associated with a substantial increase an individual’s exposure to traffic-related air pollutants, including tailpipe (eg, NO2, ultrafine particles, and black carbon) and nontailpipe (eg, particles from tire wear and friction materials) emissions and noise.29 This finding suggests that the synergistic effect of traffic exposure mixtures might, at least in part, operate through this mechanism.
Prior evidence8 has supported the role of PM2.5 and traffic-related air pollutants such as NO2 in the development of atherosclerosis, but less research has focused on the cardiovascular effects of O3; the long-term effect of exposure to O3 on subclinical CHD is still largely unknown. Ambient O3 is a powerful oxidizing agent and common air pollutant worldwide. We observed a significant association between O3 and degree of CAC, although this association could not be disentangled from the effects of PM2.5 and NO2 because of the spatial correlations between these exposure variables.
There was evidence that elderly participants and those with diabetes were more susceptible to these exposure effects than other participants. Patients with diabetes have a greater overall coronary plaque burden and a higher rate of multivessel disease. It is possible that air pollution could worsen the underlying diabetes disease course by exacerbating insulin resistance or by instigating adverse biological responses (eg, endothelial dysfunction) that promote future diabetic atherosclerosis.3 Among women, we observed a stronger association of exposure to PM2.5 with risk of atherosclerosis in postmenopausal women, a group for whom an association between PM2.5 and cardiovascular risk has previously been demonstrated in the United States.30
This study has several limitations. First, because this was an outpatient population, it may not fully reflect the general population. However, this population had relatively low pretest probability of CHD (27.3%); 29.0% had no symptoms, and 64.0% had nonanginal chest pain. Moreover, this population resembled population-based samples8,10,17 in terms of risk factors and CAC levels. Therefore, this cohort can represent a low-risk natural population. Second, we cannot rule out biases due to unmeasured confounders, such as occupation history. In addition, the main analysis of this study did not account for individuals who moved in recent years, although we did sensitivity analysis in a subset of the samples that showed consistent association. Third, this is a cross-sectional study involving the baseline examination of an ongoing prospective cohort study. Future longitudinal analysis of this prospective cohort may provide additional information.
This study found that long-term exposure to outdoor air pollution and traffic pollutants in China, specifically PM2.5 and NO2, was associated with the development of CAC. This finding should contribute to an understanding of air pollutant effects worldwide, providing both much needed locally generated data and supportive evidence to inform the air pollution standard-setting process on a global scale.
Accepted for Publication: May 13, 2019.
Published: June 28, 2019. doi:10.1001/jamanetworkopen.2019.6553
Open Access: This is an open access article distributed under the terms of the CC-BY License. © 2019 Wang M et al. JAMA Network Open.
Corresponding Author: Bin Lu, MD, Department of Radiology, Fuwai Hospital, National Center for Cardiovascular Diseases, Chinese Academy of Medical Sciences, 167 Bei-li-shi St, Xi-cheng District, Beijing 100037, China (firstname.lastname@example.org).
Author Contributions: Drs Wang and Lu had full access to all of the data in the study and take responsibility for the integrity of the data and the accuracy of the data analysis. Drs Wang and Hou contributed equally to this work.
Concept and design: Wang, Hou, Lu.
Acquisition, analysis, or interpretation of data: Wang, Xu, Liu, Budoff, Szpiro, Kaufman, Vedal, Lu.
Drafting of the manuscript: Wang, Hou, Liu.
Critical revision of the manuscript for important intellectual content: Wang, Xu, Liu, Budoff, Szpiro, Kaufman, Vedal, Lu.
Statistical analysis: Wang, Szpiro, Vedal.
Administrative, technical, or material support: Wang, Hou, Xu, Lu.
Supervision: Wang, Budoff, Kaufman, Vedal, Lu.
Conflict of Interest Disclosures: Dr Szpiro reported grants from the National Institutes of Health during the conduct of the study and personal fees from the Health Effects Institute and the Electric Power Research Institute outside the submitted work. Dr Vedal reported grants from the AXA Research Fund Chair and personal fees from the Health Effects Institute outside the submitted work. No other disclosures were reported.
Funding/Support: This study was supported by the Ministry of Science and Technology of China (grant 2016YFC1300400), Chinese National Key Research and Development Project (grant 2016-I2M-1-011), and US National Institute of Environmental Health Sciences (grant K24ES013195). Dr Wang was primarily supported by faculty startup funds from the University at Buffalo.
Role of the Funder/Sponsor: The funders had no role in the design and conduct of the study; collection, management, analysis, and interpretation of the data; preparation, review, or approval of the manuscript; and decision to submit the manuscript for publication.
Additional Contributions: We thank the staff and the participants of the study for their valuable contributions. Michael J. LaMonte, PhD, MPH, University at Buffalo, provided valuable suggestion on this study; he did not receive compensation.
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