Ambient particulate matter (PM) with an aerodynamic diameter ≤2.5 µm (PM2.5), capable of penetrating and depositing in the deep lung, constitutes a large size fraction of PM present in modern urban atmospheres (1-3). PM2.5 has been associated with a range of adverse respiratory health effects include respiratory diseases and changes in lung function (4,5). Lung function is a noninvasive measure of respiratory health and has been commonly used in previous studies to assess the respiratory health effects of air pollution (6-8). The lack of a fully developed lung function during childhood is a risk factor for many diseases like chronic obstructive pulmonary diseases (9) in adulthood. Unfortunately, children are more susceptible than adults to the respiratory effects of air pollution largely due to the fact that children’s lung is still under development (10-12). Moreover, children generally inhale more PMs due to higher metabolic rate and high physical activity level as well as their time-activity patterns often leading to increased exposure (13).
Exposure to ambient PM has been associated with reduced lung function in many studies (3,14-16). For example, in school-age children living in southern California, exposure to PM2.5 was associated with clinically and statistically significant deficits in the forced expiratory volume in 1 second (FEV1); and the growth of FEV1 was slower in more polluted (higher PM2.5) communities (17). In fact, most studies (18-21) on the association between PM2.5 exposure and lung function to date were carried out in populations exposed to certain concentration levels of air pollution. While some studies reported an association between higher air pollution exposure and reduced lung function in school-age children (22,23), other studies did not find such an association (24,25). The inconsistency may be due to differences in PM2.5 composition and/or exposure misclassification that has been common in cohort and population studies in which individual differences in exposure were not considered. To overcome the problem of exposure misclassification, assessment of exposure dose can more accurately reflect the dose-response relationship. Estimating dose requires integrating exposure concentration, behavior patterns and individual inhalation rate that depends on activity state (26).
In the present study, we aim to use dose estimates to assess the dose-response, instead of conventional exposure-response relationships, between long-term PM2.5 exposure and lung function in school-age children. To estimate dose, we used a spatiotemporal model to estimate PM2.5 concentrations for main micro-environments (residence, school, and in-transit routes between school and residence) over the 5-year period preceding lung function measurements. Multi-year dose estimates were used to identify the time window most influential to lung function.
Study site and population
The study was conducted in children living in Lanzhou, the capitol city of Gansu Province, comprised of five municipal districts of Chengguan, Qilihe, Xigu, Anning, and Honggu, covering an area of approximately 13,085 km2, with a population of about 3,729,600 in 2017 when this study was conducted (27). Lanzhou is an important industrial base and broad transportation hub in northwest China and is an important node city in the Silk Road economic belt. Lanzhou is located in the transition zone between monsoon climate and non-monsoon climate. Recent rapid urbanization has resulted in a significant increase in the number of vehicles and factories. This, coupled with Lanzhou’s valley topography, make Lanzhou among one of the most polluted Chinese cities. Across the city, the heterogeneity in industrial development and the varying topology result in spatial variability in ambient pollution levels.
Two primary schools were selected in the urban and suburban area for this study, with most students living nearby. In totality, 401 students from the urban area and 590 from the suburban area, with an aged range from 6 to 12, were recruited randomly from the aforementioned schools. The Ethics Committee of Biomedicine Research, Duke Kunshan University, approved the study and written consent was obtained from the parents. The questionnaire on child’s behavior patterns, health state and environmental and other risk factors was completed on requested. The lung function measurements were conducted among healthy children from grade 1 to grade 6, about 192 from urban and 492 from the suburban areas, from November 27 2017 to December 29 2017.
The study was conducted in accordance with the Declaration of Helsinki (as revised in 2013). This study was reviewed and approved by the Committee on Ethics of Biomedicine Research, Duke Kunshan University, Jiangsu (No. FWA00021580). All patients enrolled completed the informed consent form.
We used a questionnaire adapted from the American Thoracic Society (ATS) Epidemiologic Standardization Project questionnaire on respiratory symptoms and illnesses (28). We also collected additional information on household environmental conditions. The information is classified into the following categories: (I) indoor environment like per-person living area, type of fuel used for cooking, type of kitchen ventilation devices, passive smoking exposure, renovation, dampness and mold, use of air purifiers, air freshener, mosquito-repellent and incense stick, and indoor ventilation and duration; (II) parental health and socioeconomic status like whether parents had doctor-diagnosed asthma and bronchitis, parental education attainment, and parental occupation; (III) early life factors like maternal smoking during pregnancy and the first year after birth, duration of exclusive breastfeeding, and whether child was born prematurely; (IV) children’s respiratory health histories like whether child had doctor-diagnosed asthma, bronchitis, and/or allergic rhinitis; (V) information on nutrition and exercise in children, including frequency of fruit and vegetable intake and type and frequency of exercise.
The questionnaire was administered with children’s parents prior to the lung function measurements. Only the children whose parents returned a completed questionnaire were included in the lung function measurements.
Lung function measurements
Lung function measurement were performed using calibrated spirometers (Spiro-lab New, MIR, Italy) following the ATS guidelines for spirometry (29). Children were measured in the standing position inside an air-conditioned room with stable air circulation. Body height and weight were measured immediately before test and input in the spirometer to automatically obtain child’s predicted lung function. Spirometric lung function was assessed in terms of the four representative indicators, i.e., forced vital capacity (FVC, mL), the forced expiratory volume in one second (FEV1, mL), peak expiratory flow (PEF, mL/s) and the FEV1/FVC ratio (%). Values were also expressed as a percentage of the predicted value (observed value/predicted value ×100) for the participant’s age, height, weight and gender, using previously established equations (built in the spirometers) (30). For each participant, the spirometry test was repeated for up to five times until acceptable, reproducible flow volume loops were obtained. Each participant was given once lung function test during the study phase. Between one test and the next, the device evaluates the repeatability of the following parameters: repeatable when the difference between the two highest values was ≤150 mL for FVC, ≤150 mL for FEV1, and ≤10% for PEF. Acceptable spirograms were defined as smooth flow-volume curve without artefacts, and satisfactory exhalation with forced expiratory duration >6 s (3 s for children younger than 10 years). If the difference between the two largest FVC readings was within 150 mL, the test was concluded. The highest acceptable values of FVC and FEV1 were used for statistical analysis.
In this study, a validated PM2.5 concentration modeling method, namely timely structure adaptive modeling (TSAM) (31) was employed to simulate the PM2.5 concentrations (January 2013 to December 2017) at 10 km spatial resolution. After that, a geostatistical interpolation approach (i.e., Ordinary Kriging) was applied to map the 1 km spatial resolution PM2.5 concentrations (32,33). Generally, the structure of a TSAM model can be simply defined as Eq. , containing dependent variable (PM2.5 concentration) and three types of explanatory factors (satellite-retrieved Aerosol Optical Depth (AOD), pollutant emissions and dispersion conditions).
Where PM2.5 indicates the dependent variable of PM2.5 concentration; AOD is the satellite measurement indirectly representing the PM2.5 concentrations, collected from Atmosphere Archive and Distribution System (AADS, https://ladsweb.nascom.nasa.gov/search/index.html); emissions are the factors related to industrial smoke and dust, vehicle exhaust and surface dust, such as land use type (e.g., built-up, forest, grass, water), road level and so on; Dispersion factors mainly include meteorological and topographical conditions influencing the PM2.5 dispersion such as wind speed, relative humidity, elevation etc.
In order to evaluate the exposure level of individuals, we divided the exposure scenarios into three parts: school, residence and in-transit routes between school and residence. The calculation formula is as follows:
in which C was the average individual exposure level of outdoor PM2.5 (µg/m3), Ci was the average concentration of outdoor PM2.5 (µg/m3) in this place during this period (i=1, 2, 3), Ti the length of time (h) the child stayed at the site (i=1, 2, 3). In our study, we set the time spent at home as 15.5 hours daily (T1=15.5), the time spent in school was 6.5 hours daily (T2=6.5) and the time spent on the routes between residence and school was 2 hours daily (T3=2). Then we deduced outdoor PM2.5 annual average from 2013–2017.
Since the main exposure route for human exposure to PM2.5 is inhalation, we further estimated the average daily doses (ADD, µg/kg-d) of each child using Equation , according to the recommended exposure assessment models in the U.S. Exposure Factors Handbook EPA (34).
In which C is subject-level outdoor PM2.5 (g/m3) averaged over a defined period (5-yr average or annual average from 2013–2017), IR was the inhalation rates considering gender and age (m3/hour), ET was the exposure time (hour/day), EF was the exposure frequency (day/year), ED was the exposure duration (year), BW was the body weight (kg) and AT was the average exposure time (day). The exposure time related to age of children and their BW were obtained through the questionnaire. The other exposure parameters, such as IR were obtained from Exposure Factors Handbook of Chinese Population (children 6–17 years) (35). All the parameters in Equation  were specific to the age at which exposure was estimated.
Covariates and effect modifiers
In our statistical models, a lung function indicator was the main dependent variables, whereas PM2.5 concentration or dose (ADD) was the independent variable and other questionnaire-derived variables were covariates. Variables related to individual characteristics of children included age, school location, gender, whether preterm birth, allergy status, nutrition intake, and physical exercise. “Asthma in past year”, “Pneumonia in past year” and “Allergy in past year” refers to that the child had any of these three ailments in the last year. Nutrition related variables were constructed from frequencies of eating vegetables, fruit, dairy product, fish, high-fat and caloric products. Information about nutrition was grouped according to the Dietary guidelines for Chinese residents (36). Physical exercise variable was based on the information on frequency of exercise and whether child sweated after exercise. We defined parental education and occupation as measures of socioeconomic status and parental history of asthma as a potential effect modifier. Non-manual laborer was similar to the so-called “white collar worker”, such as teacher, doctor, businessperson, clerk and housewife, whereas manual laborer was like the so-called “blue collar worker”, such as factory worker, construction worker, building cleaning worker and farmer. Children’s exposure to indoor air pollution was measured by questionnaire survey such as parental smoking, kitchen style, solid fuel use, ventilation condition, fuel for heating in winter, air purifier use, keeping pets, and room having mold condition. Fuel such as coal, firewood for cooking and heating were defined as solid fuels, whereas clean fuel referred to electricity, natural gas, and liquefied petroleum gas or marsh gas. Finally, the recent history of the children’s infection of respiratory diseases, in addition to preterm birth status and breast-feeding status were considered as covariates.
Data analyses were conducted in 684 participants comprised of 371 boys and 313 girls. We used lung function parameters (outcome variables) as dependent variables to analyze their response to PM2.5 exposure. Univariate summary statistics and distributional plots were examined for all variables. We used analysis of variance (ANOVA) for bivariate analysis to explore the distribution of PM2.5 exposure and ADD among other potential confounders. We performed ‘screening’ analyses in multivariate linear regressions to select co-variates that either changed the main effect estimate by >10% by including them or showed a P value <0.1 for the regression coefficients. We also conducted subgroup analyses stratified by gender to evaluate the potential modifying effects.
We examined the association between ADD of PM2.5 and lung function, considering each parameter separately. The models included a linear function of ADD and all covariates listed above. The results are presented as estimated changes (β) of lung function parameters per 1 unit increase in PM2.5 ADD and 95% confidence interval. Statistical analyses were conducted using R version 3.4.3.
Description of the population
This study integrated children’s behavior (time-activity) patterns into ambient PM2.5 concentration to estimate average daily exposure dose (ADD) for each child. The baseline characteristics of schoolchildren by covariate are present in Table 1. There are twice as many children in the suburbs (71.9%) as in the urban (28.1%). Almost half of the children were girls. Children were between 7 to 12 years old, although the majority (72%) of them were in the age group of 8–10 years.
Within each covariate shown in Table 1, we conducted a simple t-test to compare average PM2.5 or ADD across the categories. We found that suburban children have significantly lower PM2.5 concentration and ADD than urban children. Boys had significantly higher ADD than girls (but not PM2.5), mainly due to higher inhalation rate for boys. Compared to the oldest age group (>10 years old), the youngest group (<8 years old) had the lower PM2.5 but higher ADD. We listed indoor air quality related variables (parental smoking, kitchen style, cooking fuel, kitchen ventilation, heating in winter, heating fuel, and air fresher use) in the table to show their distributions. Given PM2.5 and ADD were solely based on ambient (outdoor) PM2.5 concentrations, comparing PM2.5 or ADD within each of these variables did not provide any “causal” insights. Similarly, ADD values or PM2.5 concentrations for other covariates are compared without a causal inference. These comparisons showed the following results.
Children who characterized with solid cook fuel use, mother’s education below senior high school, mother had asthma, fruit frequency below reference showed significant higher (P<0.05) exposure to PM2.5. Moreover, children who were characterized with parental smoking, opened kitchen, no ventilation use, coal for heating, dairy frequency below reference presented significant (P<0.001) higher individual exposure to PM2.5, compared to the reference group. Of the children living in urban area, father’s education below senior high school, mother’s education below senior high school, fruit frequency below reference showed significant (P<0.05) higher of ADD of PM2.5.
PM2.5 exposure and lung function
Summary statistics of the distributions of the long-term PM2.5 averaged over defined periods [2013–2017] and lung function variables measured in 2017 are provided in Table S1. Because of a lack of home addresses or errors in latitude and longitude resolution, in total the PM2.5 data of 613 children was available for further regression analysis. The 5-year average personal PM2.5 concentrations had a mean of 48.1 µg/m3, and a range of 43.8–69.1 µg/m3 across 613 subjects. Average personal 5-year averaged ADD was 50.5 µg/kg-d, ranging from 26.3 to 76.2 µg/kg-d. Mean (± SD) FVC to predict (%), FEV1 to predict (%), PEF to predict (%), FEV1/FVC were 104 (±10.7), 102 (±9.7), 77 (±0.8), 91 (±0.3), respectively.
Univariate analysis of lung function was showed in Table 2. As expected, height, weight, body mass index (BMI) and age of children were significantly and positively associated with FVC, FEV1 and PEF. Mean lung function variables were lower among girls than boys for FVC (β=−172.75 mL, P<0.0001), FEV1 (β=−134.69 mL, P<0.0001) and PEF (β=−399.07 mL, P<0.0001). Children sleeping alone in a bedroom or alone in bed had significantly higher FVC, FEV1 and PEF than children living in a shared bedroom or shared bed. Having pets (β=−101.89 mL, P=0.0454) and using air fresher (β=−89.98 mL, P=0.0243) was significantly and negatively associated with FVC. Father’s occupation of non-manual laborer was significantly and positively associated with FVC (β=102.68, P=0.0088) and FEV1 (β=77.13, P=0.0231). Children sweating more after sports activities had significantly higher FVC (β=112.26 mL, P=0.0022), FEV1 (β=83.92 mL, P=0.0077) and PEF (β=173.13 mL, P=0.0342).
Association of lung function with ADD of PM2.5
The results of individual average daily exposure dose of PM2.5 with relation to lung function are shown in Table 3. In general, the ADD representing long-term (5-year average) exposure dose of PM2.5 had statistically significant negative associations with FVC, FEV1 and PEF, respectively. For the crude model of adjusting no covariates, a 1-unit increase in ADD of long-term PM2.5 exposure was significantly associated with 27.08 mL (95% CI: −32.41 to −21.75, P<0.0001) decrease in FVC, 23.65 mL (95% CI: −28.30 to −19.00, P<0.0001) decrease in FEV1 and 31.16 mL/s (95% CI: −44.04 to −18.28, P<0.0001) decrease in PEF. No significant association was observed for FEV1/FVC. Adjustment for potential confounding variables showed in Table 1, resulted in attenuations in effect estimates for FVC and FEV1 without changing the statistical significance. However, adjusting the covariates resulted in losses of statistical significance for the ADD-PEF associations. After accounting for age, weight, height and gender, the ADD of long-term exposure of PM2.5 was associated with a 14.87 mL (95% CI: −22.86 to −6.88, P=0.0003) lower FVC and a 10.02 mL (95% CI: −16.79 to −3.25, P=0.0039) lower FEV1. Children’s exposure to indoor air pollution, socioeconomic status and parental history of asthma, children’s infection of respiratory diseases recently, pre-birth (premature birth) and breast feeding were adjusted in model I. Nutrition and exercise related variables were further added in Model II. The ADD was still associated with a 10.49 mL (95% CI: −20.47 to −0.50, P=0.0402) lower FVC and a showed 7.68 mL (95% CI: −15.80 to −0.44, P=0.0386) lower FEV1.
When we used 1-year averaged based ADD of PM2.5 for the year of lung function test  and each of the previous 4 years, we observed generally similar patterns of ADD-lung function association (Figure 1). A closer examination showed that ADD averaged in 2016, 1-year prior of lung function measurement, had the strongest association with FVC and FEV1 in terms of both statistical significance and effect size, suggesting that exposure in the immediate past year may be most relevant to the PM2.5 effects in children.
When stratified the analyses by gender, we observed larger decreases in FVC and FEV1 associated with a unit increase in ADD in girls than in boys (Table S2). We also performed stratified analyses by district (urban vs. suburban) (Table S3) and sweating after sports activities (less versus more) (Table S4). Larger decreases in FVC and FEV1 associated with a unit increase in ADD were found in suburban and less sweating after sports activities group. When replacing ADD with the 5-year average PM2.5 concentrations (calculated as time-weighted PM2.5 by Formula 2) in the same models (see Table S5), we observed no significant associations of PM2.5 concentrations with any of the lung function indictors including FVC and FEV1 that were significantly associated with ADD as described above. Considering no measurement data of indoor PM2.5 concentration, we referred to studies focused on indoor/outdoor (I/O) ratio of PM2.5 performed in northern China (37,38). Two reference values of I/O (I/O =0.88; I/O =0.49) were selected to recalculated the concentration of individual PM2.5 and ADD, then assess indoor PM2.5 exposure effects on lung function for sensitivity analysis (Table S6). Lung function is affected by indoor exposure to PM2.5 concentration and may have different effects with different I/O coefficients considered. Further research is needed to explore this relationship.
In this study, we assessed individual-level PM2.5 exposure over the past 5-year period. This long-term exposure, calculated as ADD, was then related to lung function of children living in Lanzhou, China. The strengths of this study include the consideration of school and home address, the use of ADD to assess exposure, and detailed individual-level information on a suite of socioeconomic, parental health, and residential environmental conditions. The exposure dose (ADD) incorporated ambient PM2.5 concentration with individual’s inhalation rate, duration of exposure and the average exposure time. ADD, hence, is a more accurate indicator of individual-level exposure than concentration that has been commonly used.
Study subjects’ average exposure to PM2.5 levels were estimated over a 5-year period, by assessing concentrations at different locations, including school, residence and the routes between residence and school. We described the PM2.5 level and ADD by subjects’ attributes collected in a questionnaire survey. Results showed that PM2.5 levels differed by school/residence location, parental smoking, kitchen style, cook fuel, ventilation use, heating in winter and heating fuel type. Results showed that ADDs of PM2.5 differed by school/residence location, gender, and parental education attainment. Children living in the suburban area showed a significant lower PM2.5 and ADD levels in 2013–2017, consistent with previous studies in Lanzhou (39-41).
The present study estimated the effects of annual-averaged ambient PM2.5 on lung function in a cross-sectional study of primary school children, and found that increasing exposure levels were primarily associated with reductions in two major lung function indices (FVC and FEV1) examined in the study. Most previous studies have focused on PM2.5 concentration level in the air and the effects on lung function indices. The Framingham Heart Study (42) found negative associations with FEV1 and FVC (each 2 µg/m3 increase in PM2.5 was associated with a 13.5 mL lower FEV1 and 18.7 mL lower FVC), but not for the FEV1/FVC ratio. ESCAPE study (43) found an increase of 10 µg/m3 in PM10 was associated with a lower level of FEV1 (−44.6 mL, 95% CI, −85.4 to −3.8) and FVC (−59.0 mL, 95% CI, −112.3 to −5.6), but not other PM metrics (PM2.5, coarse fraction of PM, PM absorbance).
To the best of our knowledge, our study is the first to use exposure dose in examining the effects of long-term ambient PM2.5 exposure on children’s lung function. We are aware of only one previous study that used predicted average daily intake (ADD) of respirable PM (44), which found that the risk for having impaired respiratory function was 1.3 times greater in children with higher ADD due to living in industrial areas than those in the control group. In the present study, we only found significant associations of lung function with estimated ADD of PM2.5 but not with concentrations of PM2.5, after adjusting for individual information, indoor air pollution factors, and nutrition and exercise variables in the models.
Our findings are consistent with previous findings on the long-term PM2.5 effect on children’s lung function or lung function growth. In a series of publications on lung function growth in Austrian schoolchildren, Ihorst et al. (45) and Horak et al. (46), reported on detected deficits in lung growth among children in highly polluted areas over a study period of 3.5 years. In the Californian Children’s Health Study (CHS) (47), children living in the most polluted community had a growth deficit in FEV1 of approximately 100 mL, as compared with those living in communities with better air quality over an 8-year period. However, the adverse effect of PM2.5 on lung function was more pronounced by use of ADD, but not the concentration of PM2.5, in our study. A study in California showed that a pollutant-related delay in lung development in children can be attenuated if children move to cleaner geographic areas (48). In our study, the 5-year average concentration level of PM2.5 was 48.1 µg/m3, and even the highest concentration in 2013 was 67 µg/m3, both of which meet the China’s PM2.5 standard of 75 µg/m3. The concentration of fine PM was relatively low compared to other cities in developing countries, which may partly explain the discrepancy of the results in our study from previous researches. Additionally, in our study, the subjects are from two schools in a city. Age- and gender-weighted ADD can better reflect the exposure gradient, while the concentration gradient is smaller because the subjects live near the school. This might account for no significant associations of lung function with concentrations of PM2.5.
In our study, girls appeared to be more susceptible than boys to ambient PM2.5 exposure. Early studies found that negative associations between pollutants, including PM10, PM2.5, NO2, and O3, and the expiratory flow variables, including FVC, FEV1, PEF, FEF25% and FEF50%, especially in girls (49,50). Different gender*pollutant interaction effects occurring in different regions may be due to gender differences in hormonal factors and lung development physiology (51). There are gender disparities in the relationship between lung volume and flows (52), which might result in a gender-related response to air pollutants.
We found that the average daily exposure dose of PM2.5 in the year before the lung function test had the greatest effect on lung function. A large cohort study in the US investigated the association of air quality regulations in the 1990s, and lung function in 600 eight-year-old children. The authors found no significant associations between air pollution exposure and lung function, except for PM2.5 exposure one year before lung functional testing, and reduced FEV1 values (53). This weak association supports our findings, where we adjusted rigorously for potential confounders (e.g., living district, asthma status of the child), and found only associations of FVC and FEV1 one year before the lung function measurement within the overall population. For the lagging effect of PM on lung function, the analysis was done by reviewing previous studies and found that more attention had been paid to the short-term acute effect (54,55), while fewer studies on the long-term effect can be referred to. Our study suggests that ADD may be used in future studies addressing the effects of long-term air pollution exposure.
However, there are limited references on the exposure window of PM2.5 affects lung function in children. The small reductions in lung function as reported in this and previous studies should encourage further reduction in ambient air pollution levels to protect susceptible children during vulnerable time windows of lung development. Furthermore, in order to prevent reporting spurious associations, studies should attempt to approximate exposure levels as precisely as possible, taking into account spatial and temporal variation, since factors such as proximity to major roads and short-term air pollutant exposure are known to have an impact on individual exposure levels (56). To better evaluate the effects of improved air quality on children’s health, more accurate exposure estimates are needed, especially in cases where air pollution changes rapidly over time.
This study has several limitations. Firstly, the indoor concentration is considered to be the same as the outdoor concentration, rather than actual measurements. We took into account the microenvironment (residence, school, and in-transit routes between school and residence) of the students and weighted concentration over time to be more consistent with the actual exposure levels, considering strong association between indoor and outdoor PM2.5 level (57). Also, we performed a sensitivity analysis by considering indoor/out (I/O) ratio of PM2.5. Further studies may develop a better understanding of individual exposure pathways in people’s everyday lives by taking account of all environments in which people spend time to support health impact assessment. Secondly, we were unable to ascertain the role of other ambient air pollutants (such as sulfur dioxide and nitrogen dioxide) (58) played in the effects on lung function. This study mainly focuses on PM2.5. There should be future research on two-pollutant or multi-pollutant models to provide a better model fit when gaseous co-pollutants were adjusted for. Nevertheless, the present study demonstrated the usefulness of a new exposure assessment method (exposure dose at the individual level) in examining health effects of air pollution.
Long-term exposure to ambient PM2.5, estimated as ADD, was associated with reduced lung function values of FEV1 and FVC in school children (7–12 years old) living in a typical industrial city located in northwestern China. Comparing the annual ADDs among the past 5 years, the value for the immediate past year prior to lung function measurements had the strongest associations. These findings suggest that accurate exposure estimates are needed where air pollution changes rapidly over time. These associations were stronger in girls than in boys. Using individual-level dose estimates, as opposed to exposure concentrations, is recommended for future studies of air pollution health effects, given that we observed no associations between PM2.5 concentrations (even at the individual level) and lung function.
We are particularly indebted to the children, their parents and the schools for their time and enthusiastic participation. We want to thank the PM2.5 concentration mapping of this work: Bin Zou, PhD, worked in School of Geosciences and Info-Physics, Central South University. We also appreciate all those who helped me during the implementation of the project.
Funding: This work was supported by the National Science Foundation (41977374) the National Key Research and Development Program of China (2016YFC1302501).
Provenance and Peer Review: This article was commissioned by the Guest Editor (Junfengf Zhang, Howard Kipen and Haidong Kan) for the series “Children’s Respiratory Health and Air Quality” published in Journal of Thoracic Disease. The article was sent for peer review organized by the Guest Editors and the editorial office.
Data Sharing Statement: Available at http://dx.doi.org/10.21037/jtd-19-crh-aq-007
Conflicts of Interest: All authors have completed the ICMJE uniform disclosure form (available at http://dx.doi.org/10.21037/jtd-19-crh-aq-007). The series “Children’s Respiratory Health and Air Quality” was commissioned by the editorial office without any funding or sponsorship. JJZ, HK and HK served as the unpaid Guest Editors of the series. JJZ also and serves as an unpaid editorial board member of Journal of Thoracic Disease. The other authors have no other conflicts of interest to declare.
Ethical Statement: The authors are accountable for all aspects of the work in ensuring that questions related to the accuracy or integrity of any part of the work are appropriately investigated and resolved. The study was conducted in accordance with the Declaration of Helsinki (as revised in 2013). This study was reviewed and approved by the Committee on Ethics of Biomedicine Research, Duke Kunshan University, Jiangsu (No. FWA00021580). All patients enrolled completed the informed consent form.
Open Access Statement: This is an Open Access article distributed in accordance with the Creative Commons Attribution-NonCommercial-NoDerivs 4.0 International License (CC BY-NC-ND 4.0), which permits the non-commercial replication and distribution of the article with the strict proviso that no changes or edits are made and the original work is properly cited (including links to both the formal publication through the relevant DOI and the license). See: https://creativecommons.org/licenses/by-nc-nd/4.0/.
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