Short-term effects of air pollutants on hospital admissions for asthma among older adults: a multi-city time series study in Southwest, China

Background This study aimed to explore the relationship between air pollution and hospital admissions for asthma in older adults, and to further assess the health and economic burden of asthma admissions attributable to air pollution. Methods We collected information on asthma cases in people over 65 years of age from nine cities in Sichuan province, as well as air pollution and meteorological data. The relationship between short-term air pollutant exposure and daily asthma hospitalizations was analyzed using the generalized additive model (GAM), and stratified by gender, age, and season. In addition, we assessed the economic burden of hospitalization for air pollution-related asthma in older adults using the cost of disease approach. Results The single pollutant model showed that every 1 mg/m3 increase in CO was linked with an increase in daily hospitalizations for older adults with asthma, with relative risk values of 1.327 (95% CI: 1.116–1.577) at lag7. Each 10 μg/m3 increase in NO2, O3, PM10, PM2.5 and SO2, on asthma hospitalization, with relative risk values of 1.044 (95% CI: 1.011–1.078), 1.018 (95% CI: 1.002–1.034), 1.013 (95% CI: 1.004–1.022), 1.015 (95% CI: 1.003–1.028) and 1.13 (95% CI: 1.041–1.227), respectively. Stratified analysis shows that stronger associations between air pollution and asthma HAs among older adult in females, those aged 65–69 years, and in the warm season, although all of the differences between subgroups did not reach statistical significance. During the study period, the number of asthma hospitalizations attributable to PM2.5, PM10, and NO2 pollution was 764, 581 and 95, respectively, which resulted in a total economic cost of 6.222 million CNY, 4.73 million CNY and 0.776 million CNY, respectively. Conclusion This study suggests that short-term exposure to air pollutants is positively associated with an increase in numbers of asthma of people over 65 years of age in Sichuan province, and short-term exposure to excessive PM and NO2 brings health and economic burden to individuals and society.


Introduction
Bronchial asthma (abbreviated as asthma) is a common chronic respiratory disease with clinical manifestations of wheezing, shortness of breath, chest tightness, and cough (1,2).So far, about 330 million people worldwide are suffering from asthma, which causes a heavy medical burden (3).Meanwhile, the pace of population ageing is much faster than the past, and the number of older patients with asthma is expected to increase significantly (4).The prevalence of asthma in people over 65 years of age is currently reported to be 4%-13% globally (5), and this is likely to be an underestimate (6).Asthma surveillance data released by the US Centers for Disease Control and Prevention (CDC) showed that the asthma prevalence among those aged ≥65 years in the US in 2020 was 7.8% (7).Notably, the 2010 to 2012 China Asthma and Risk factors Epidemiologic survey (CARE) reported that the prevalence of asthma in China was 2.26% in people aged 61-70 years and 3.10% in those aged ≥71 years (8).while the data from 2012 to 2015 China Pulmonary Health (CPH) study showed that asthma prevalence increased to 6.0% in people aged 60-69 years and to 7.4% in people aged ≥70 years (9).
Asthma results from the combined action of genetics and environment, with air pollution being an important factor in triggering asthma (10) and its exacerbation (11,12).Even when the pollutant concentrations are lower than guideline levels, there are still have serious effects on susceptible individuals (13).Several mechanisms reasonably explain how air pollutants contribute to the development and exacerbation of asthma, including eosinophilic and neutrophilic inflammation through stimulation of airway epithelium, increased production of pro-inflammatory cytokines, oxidative stress, and deoxyribonucleic acid (DNA) methylation changes (14,15), these changes subsequently induce sensitization to airborne allergens and allergic inflammation (14).With the increase of age, lung function appears physiological decline (16).Compared with young patients with asthma, older adults patients with asthma show more severe symptoms and have an increased risk of frequent medical visits and even death (17), which indicates that they are more likely to consume medical resources due to air pollution (18) and have a greater economic burden (19).
Asthma in children and adults has long been a concern (20,21).However, numerous studies have shown that the prevalence of asthma increases with age (8,22,23).So far, there is limited evidence that air pollution increases the risk of medical visits in older adults with asthma (24, 25).Studies in China have indicated that air pollutants have adverse effects on asthma in older adults.A study in Beijing (26) found that for every 10 μg/m 3 increase in PM 2.5 , hospitalizations for asthma increased by 0.67%.In contrast, Zhang et al. (27) analyzed daily records of respiratory disease hospitalizations and air pollution data in Shenzhen during 2015-2016 and did not identify an association between asthma hospitalization and PM 10 or PM 2.5 .Analysis by Luo et al. (18) found that every 10 μg/m 3 increase in SO 2 was associated with a corresponding 7.27% increase in hospitalizations among older adults patients with asthma; whereas PM 2.5 , PM 10 , and NO 2 were not associated with asthma exacerbation.Noticeably, these studies were primarily conducted in economically developed areas (20,28), and most of them were single-city studies.Sichuan has become one of the regions with the worst combined air pollution in China (29), and there are large differences in concentrations of different pollutants temperature and humidity in different cities (30).However, current researches mainly focused on the provincial capital city Chengdu (31,32), with studies in multiple cities in this province lacking.
To fill this data gap, in this study, we aimed to assess the associations between short-term exposure to air pollutants and hospital admissions (HA) of asthma in older adults people over 65 years of age, and quantify the corresponding health and economic loses of asthma caused by PM and NO 2 pollution, with these two hypothesis: (1) short-term exposure to air pollution is positively associated with acute exacerbation of asthma in older adults patients in Sichuan province resulting in being hospitalized; (2) excess air pollutants may increase the economic burden of asthma-related diseases among older adults.

Study area
Sichuan province is located in the southwestern region of China and consists of two major parts, the Sichuan Basin in the east and the western Sichuan Plateau.Sichuan province is ranked as one of the most heavily polluted areas in China due to high pollutant emissions and its unique topography which is not conducive to atmospheric dispersion (33).Meanwhile, Sichuan has a large older adults population with 14.168 million people aged ≥65 years, ranking second in China following Shandong (34).
Sichuan province has a total of 21 cities/prefectures, including 18 cities in the Sichuan Basin and 3 autonomous prefectures in the West Sichuan Plateau.Medical institutions in nine cities and prefectures across Sichuan province, including Chengdu, Mianyang, Nanchong, Guang'an, Meishan, Zigong, Yibin, Luzhou and Liangshan Yi Autonomous Prefecture, were selected for the study, of which 8 were from the Sichuan Basin and 1 from the West Sichuan Plateau, and medical institutions are all types of hospitals in the area, including general hospitals, Chinese medicine hospitals, specialist hospitals and private hospitals, representing the overall situation of Sichuan province to a certain extent covering different economy and population (Figure 1).

Data sources
Information on asthma patients aged ≥65 years between January 1, 2017 to December 31, 2019 was collected from hospital electronic health records (EHRs) of 273 hospitals in 9 cities of Sichuan province, with data variables including gender, age, home address, date of birth, hospitalization and discharge dates, and total cost of hospitalization.The International Classification of Diseases tenth edition (ICD-10) codes, including J45 (asthma) and J46 (status asthmaticus) were used to identify asthma-related hospitalization cases.Additionally, hospitalization data for 6,092 asthma patients aged ≥65 years were identified.This study was approved by the Ethics Committee of Hospital of Chengdu University of Traditional Chinese Medicine (Approval No. 2020KL-001).
Daily average levels of CO, NO We adopted inverse distance weighting (IDW) method to estimate the exposure levels of the individual cases (35).Specifically, the locations of all monitoring stations and home addresses of hospitalized asthma patients were geocoded using the Gaudet Map API, 2 the next, for each older asthma patient, the inverse distance (1/d 2 ) weighted average of the concentrations from all monitoring stations was used to assess the air pollutant exposure for a specific period of hospitalization, including single-day lag exposure (lag0-lag7) and multi-day moving average lag exposure (lag01-lag07).

Study design and statistical analyses 2.3.1 Effects of air pollutants on asthma HAs
The collected patient information, pollutants and meteorological data were statistically described.Spearman's rank correlation coefficient was used to analyze the correlation between air pollutants The relationships between asthma hospitalization and explanatory variables are mostly nonlinear (20).Therefore, we use generalized additive model (GAM) to evaluate the association between ambient air pollutants and hospitalizations of older adults patients with asthma.Amongst the entire population, hospitalization for asthma is a low-probability event, and its actual distribution approximates a Poisson distribution.Therefore, a GAM with quasi-Poisson regression was used to analysis the associations between the six air pollutants (CO, NO 2 , PM 10 , PM 2.5 , SO 2 , and O 3 ) and the daily asthma hospitalizations, while controlling for the effects of confounding factors such as long-term and seasonal trends, meteorological factors, and day-of-week effects.Previous studies have shown that the lagged effect of air pollutants were usually short (36,37).In this study, single-day lags (from lag0 to lag7) combined with multiple-day lags (from lag01 to lag07) were applied to evaluated the lagged effects of air pollutants.The model is as follows Equation (1): where Y t is the number of asthma hospitalizations on day t; E Y t is the expected medical visits for asthma on day t; β is the regression coefficient; Z t is the pollutant concentration at a certain lag day, (unit μg/m 3 or mg/m 3 ); s is the smooth function; k is the degrees of freedom df + 1; DOW is the day of the week; Holiday is a binary variable for national holidays in China; time is the date, and the degrees of freedom in the model are taken according to the literature and the principle of minimum AIC value in the Akaike information criterion (AIC) (38).The degrees of freedom corresponding to the date, daily average temperature, daily average relative humidity, atmospheric pressure, and wind speed are 7, 6, 3, 3, and 5, respectively (21,26,39).
After establishing the basic model, the pollutant concentration data were introduced to estimate the regression coefficient β for the air pollutants.The relative risks (RR) and their 95% confidence intervals (CI) were calculated for each 10 μg/m 3 (NO 2 , O 3 , PM 10 , PM 2.5 , SO 2 ) or 1 mg/m 3 (CO) increase in pollutant concentrations, using the following equations Equations (2,3): To identify potential high-risk groups and to further consider the effects of temperature, subgroup analyses were carried out for gender (male and female), age (65-69 years, ≥70 years), and seasonal factors (warm season: April to September; cold season: October to March), respectively.We analyzed each subgroup using a single-pollutant model, and then selected the exposure response coefficients of the maximum impact estimates in the single-pollutant model for comparison.Differences in effect estimates between subgroups were assessed using Z tests using the following equation ( 40) Equation ( 4): where  All statistical analyses in this study were conducted using R4.2.0, and the quasi-Poisson regression model was constructed using the "mgcv" and "splines" packages.The statistical tests were two-sided, and associations with p < 0.05 were considered statistically significant.

Economic costs of asthma hospitalization attributable to air pollution
In general, exceeding air quality guideline levels is associated with significant risks to health.Since the concentrations of pollutants CO, O 3 and SO 2 at lag0 to lag7 days are far lower than the WHO air quality standard (CO 24 h mean value is 4 mg/m 3 , O 3 8 h mean value is 100 μg/m 3 , SO 2 24 h mean value is 40 μg/m 3 ) (41).Therefore, we did not measure the burden related to CO, O 3 and SO 2 .Although previous research suggests that most of the burden from air pollution is attributed to PM pollution, the effects of NO 2 cannot be ignored (42).Based on the expose-response coefficient analyzed by GAM model, we included NO 2 , PM 2.5 and PM 10 whose pollutant concentrations exceeded the reference standard (24 h averages for NO 2 of 25 μg/m 3 , PM 10 of 45 μg/m 3 , and PM 2.5 of 15 μg/ m 3 ) into the burden analysis range.We used the attributable risk method to calculate the number of HAs for asthma patients over 65 years old due to exposure to air pollutants (40,43), the formulae are as follows Equations (5,6): where i is the number of days in the study period (from 1 to 1,076).β s is equal to the sum of the β coefficients of the lag days with significant effects (for example: the effect of PM 2.5 is significant only from lag5 to lag7, and the coefficient βs is equal to the sum of the coefficients from lag5 to lag7) (44,45).In this study, the β values of PM 2.5 , PM 10 and NO 2 were 0.0044, 0.0041and 0.0043, respectively.AR i is the attributable risk on day i.∆AP i is the difference between the observed concentrations of pollutants on day i and the reference concentrations.N i is the number of asthma hospitalizations on day i.AN is the total number of asthma inpatients attributable to air pollution.
The next, based on the AN, we used the cost of illness method to estimate the economic cost of HAs for asthma due to PM and NO 2 exposure, which involved with direct medical cost and indirect economic cost (40,46) Equations (7,8).
DC is the direct medical cost attributable to air pollution.Cost total is the average direct medical cost per patient during the study period.IC is the indirect economic cost attributable to air pollution.mean d H is the average number of hospitalization days per case.dPCDI is the per capital daily disposable income of residents in Sichuan province, since our research object is the people over 65 years old, most of whom may be in the state of retirement, we introduced the Labour force participation rate (47) of people aged 65 years or over of China reported by the International Labor Organization 3 to adjust dPCDI.

Sensitivity analysis
First, according to the lag day corresponding to the maximum adverse effect in the single-pollutant models, the pollutants at the corresponding lag days were introduced into the model individually to enable the fitting of two-pollutant models.To avoid collinearity, air pollutants with a correlation coefficient r > 0.60 were excluded from the multi-pollutant model.Second, the model was fitted by varying the degrees of freedom of the temporal trends (df = 5-9) to assess temporal stability (48).

Basic situation
From January 1, 2017 to December 31, 2019, a total of 6,092 older adults asthma patients were admitted to the participating hospitals.Among them, 39.3% (n = 2,394) were male, and 60.7% (n = 3,698)

Statistical description of pollutants and meteorological variables during the study period
The daily average concentration of CO was 0.80 mg/m 3 , NO 2 , O 3 , PM 10 , PM 2.5 , and SO 2 during the study period were 28.72, 77.26, 72.07, 47.40, and 11.46 μg/m 3 , respectively.The average daily temperature and relative humidity were 16.17°C and 77.90%, and the average daily atmospheric pressure was 956.78 Pa, with an average wind speed of 1.73 M/s.These data are detailed in Table 1.

Correlations between air pollutants and meteorological factors
The results of the Spearman correlation analysis between air pollutants and meteorological factors are shown in Supplementary Table S1.We can observe significant positive correlation between CO and NO 2 , PM 10 , PM 2.5 and SO 2 , with the correlation coefficient ranging from 0.4006 to 0.7464, and the correlation coefficient r between CO and O 3 is −0.2311.NO 2 and PM 10 , PM 2.5 and SO 2 with the correlation coefficient ranging from −0.172 to 0.7252.In addition, O 3 is negatively correlated with PM 10 and PM 2.5 .PM 10 is positively correlated with PM 2.5 and SO 2 .The correlation coefficient r between PM 2.5 and SO 2 is 0.4902.The temperature was significantly negatively correlated with all six pollutants, while relative humidity was significantly negatively correlated with the remaining five pollutants excluding CO.Atmospheric pressure was negatively correlated with O 3 and positively correlated with CO, PM 10 , and PM 2.5 , while its correlation with NO 2 was not significant.Wind speed was negatively correlated with CO, NO 2 , PM 10 , and PM 2.5 , and positively correlated with O 3 and SO 2 .

Relationship between air pollution and risk of hospitalization for asthma
The results of the single-pollutant model analysis indicated that short-term exposure to pollutants was positively associated with asthma hospitalization among the older adults.According to the single-day lag (lag0-lag7) results, CO exposure increased the risk of asthma hospitalization in the older adults except at lag0, and the maximum risk was identified at lag7 with an RR of 1.327 (95% CI:1.116-1.577).There is obvious association of NO 2 with hospitalization for asthma at lag 7, with an RR of 1.044 (95% CI: 1.011-1.078).PM 10 increased the risk of asthma hospitalization among the older adults at lag4, lag5, lag6, and lag7, and the adverse effects of PM 2.5 exposure were observed at lag5, lag6, and lag7, the maximum RR values were observed at lag5 for both PM 10 and PM 2.5 , being 1.013 (95% CI: 1.004-1.022)and 1.015 (95% CI: 1.003-1.028),respectively.The effect of O 3 on asthma hospitalization at lag1, with an RR value of 1.018 (95% CI: 1.002-1.034).And SO 2 increased hospitalization risk for asthma at lag1, lag6, and lag7 with an RR value of 1.13 (95% CI: 1.041-1.227)at lag7.Among the moving average multi-day exposure (lag01-lag07) results, CO had a significant effect on asthma hospitalizations at lag03, lag04, lag05, lag06, and lag07, with a maximum RR of 1.372 (95% CI: 1.095-1.72)at lag07.SO 2 had a significant effect on asthma hospitalizations at lag01, with a maximum RR of 1.094 (95% CI: 1.002-1.195).These results are shown in Figure 2 and Supplementary Table S2.

Stratified analysis
In gender stratification, the effects of CO, PM 2.5 , PM 10 , and SO 2 , exposure were significant on female, only CO and SO 2 had significant effects on male, but the difference between the genders was not statistically significant (p > 0.05).In age stratification, CO and PM 10 have a significant impact on the population aged 65-69, however, we did not observe differences in the effects of air pollutants on different age groups (p > 0.05).As for the effects in different seasons, CO, NO 2 , PM 10 and PM 2.5 had positive and significant effects on asthma HAs in the warm season, but the difference between the cold  Frontiers in Public Health 07 frontiersin.organd warm seasons was not statistically significant (p > 0.05) as shown in Figure 3 and Supplementary Table S3.

Sensitivity analysis
In our sensitivity analyses, we found that the associations between air pollution exposure and asthma exacerbation remained almost unchanged in magnitude and remained statistically significant.Upon introducing other pollutants one by one into the single-pollutant model for adjustment, the effect of the original pollutant was somewhat affected.The effects of some pollutants were weakened.For example, the inclusion of NO 2 , O 3 and SO 2 reduced the RR of hospitalization for asthma attributable to CO exposure among the older adults, but the effect of CO remained significant.Conversely, the inclusion of O 3 in analyses increased the risk of hospitalization for asthma attributable to particulate matter among the older adults.Overall, except for O 3 and SO 2 , there was little change in the effect of the primary pollutant on asthma admissions in older adults after the introduction of another pollutant.This suggests a strong correlation between pollutants, and that the effects of air pollutants on asthma are not simply additive or subtractive, but that complex antagonistic or synergistic effects between pollutants may exist (49,50).These results are shown in Supplementary Table S4.When the temporal degrees of freedom varied from 5 to 9, no significant changes were observed in the daily asthma hospitalization rate for each 10 μg/m 3 increase in air pollutant concentrations (1 mg/m 3 increase in CO), indicating good model stability.The results are shown in Supplementary Table S5.

Discussion
Our study is one of the few multi-urban, multi-pollutant studies in heavily polluted areas in China, and the results enrich the empirical evidence of the positive association between short-term exposure to air pollution and asthma hospitalization among the older adults (51).Taking into consideration controlling factors such as temperature, humidity, atmospheric pressure, wind speed, and holiday effects, our study identified positive associations between short-term exposure to air pollution and the risk of hospitalization for asthma among the older adults, and the economic cost of asthma hospitalizations attributable to air pollution during the study period was calculated to be 11.727 million CNY in total during the study period, 2017-2019.
In the single-pollutant model, when the concentrations of pollutants increased by 10 ug/m 3 (1 mg/m 3 increase in CO), there were positive associations between CO, NO 2 , SO 2 , and O 3 , and the hospitalizations of older adult with asthma, with an RR of 1.327 (95% CI:1.116-1.577),1.044 (95% CI: 1.011-1.078),1.13 (95% CI: 1.041-1.227)and 1.018 (95% CI, 1.002-1.034),respectively, demonstrating a lag effect in the impact of air pollutants on asthma, which was consistent with previous researches.For CO, a study in Dongguan (52) reported that the per interquartile range (IQR) increase in ambient CO at lag03 day corresponded to 8.86% (95% CI, 4.89, 12.98%) increased risk in outpatient visits for asthma.This may be because exposure to CO can lead to tissue hypoxia to cause damage and can promote the development of airway inflammatory diseases (53,54).As irritating air pollutants, NO 2 and SO 2 also have significant effects on respiratory health (55).The study of Raji et al. (25) from Iran Ahwaz discovered that each 10 μg/m 3 increase in NO 2 , and SO 2 concentrations was associated with an increase of 6.9 and 6.9% in the risk of hospitalization for asthma in people aged ≥60 years, respectively.NO 2 is associated with the production of various free radicals that can trigger lipid peroxidation of cell membranes, and these effects can damage the structure and impair airway function, and exposure to NO 2 can also promote the release of inflammatory mediators, leading to asthma (56, 57).Such as Stosic et al. (58) identified a 1.2% increase in the RR of daily asthma hospitalization among people aged ≥65 years in association with a 10 μg/m 3 increase in daily NO 2 concentration.Similarly, SO 2 has been previously shown to cause bronchospasm and to increase the risk of hospitalization for asthma (18,28).O 3 is a highly oxidizing and reactive gas, which has been associated with a variety of adverse respiratory outcomes (59).Previous epidemiological studies have investigated the association between ozone pollution and acute asthma exacerbations (60,61).For example, a study in Hong Kong (62) reported that an interquartile range increment in O 3 (31.6 μg/m 3 ) in a previous week (lag0-6) was associated with 13.2% (8.4%-18.2%)increases in asthma for elders.Although the associations between air levels and asthma admissions are different due to variations in regions, population, and social factors and so on, these epidemiological studies all support that the risk of asthma increases with the concentration of air pollutants.
PM is a complex mixture of solid and liquid particles suspended in the atmosphere, and includes PM 10 (≤10 μm) and PM 2.5 (≤2.5 μm).The former is mainly produced by construction activities and re-suspension of road dust and wind, while the latter arises mainly from combustion processes.Increasing studies reported the positive associations between PM pollution and HAs for asthma among older adults (24-26).For example, Park et al. (63) using adults as the referent, the relative rate (RR) of asthma admissions with 10 μg/m 3 increase of PM 10 is 1.3% (95% CI 0.7-1.9%)higher for the the people over 65 years old.Xie et al. (64) found that the older adults were more susceptible The identification of potentially susceptible populations plays a significant role in public health.In the stratified analysis, we observed stronger associations between air pollution and asthma HAs among older adult in females, those aged 65-69 years, and in the warm season, although all of the differences between subgroups did not reach statistical significance.Previous studies have reported stronger respiratory-related health outcomes in females compared to males (68,69).Similar to our findings, a study conducted in Canadian found that only in females, short-term NO 2 exposure was associated with increased risk of respiratory hospitalizations (70).As for the effects of the season, studies have shown a higher correlation between individual air pollutant exposure and ambient air pollutant concentrations in summer than in winter (71), which makes our findings somewhat reasonable.The above discussion highlights some potential reasons why the associations between air pollution and asthma among older adults in this paper may differ from gender, season.However, our results were inconsistent across pollutants, making it more difficult to explain the biological or physiological mechanisms of effects.In order to better understand the health hazards of air pollution in older adults, future studies need to focus on more information such as individual activity patterns, occupations and regional economy and development situation, etc.
Finally, the present study analyzed the burden attributable to air pollution-induced asthma hospitalizations, which is central for costeffective policy-making and asthma prevention.Assessing the corresponding economic burden of exposure to pollutants that exceed the limits also can shed more light on the potential link between air pollution and health.Previous studies have proved that PM and NO 2 cause serious economic losses to the society (45,72,73).For example, Moradi et al. (74) found that in conditions of PM 2.5 concentration above 5 μg/m 3 , attributed proportion, the total number of attributable cases, and the number of attributable cases per 100,000 population (with moderate relative risk and confidence of 95%) for the admission of respiratory diseases have been estimated at 97.1%, 68 persons and 3 persons, respectively.Guo et al. (20) assessed the economic burden of medical visits for air pollution-induced asthma in Shanghai in 2014, and the economic costs attributable to PM 10 , PM 2.5 , and NO 2 were 30.18,34.50, and 17.15 million USD annually, respectively.Gao et al. (75) evaluated the economic costs associated with the haze event of January 2013 and found that PM 2.5 caused asthma-related economic costs of 7.1 million USD.These studies all show a positive correlation between air pollution and burden.Meanwhile, we found that the number of asthma hospitalizations attributable to PM 2.5 , PM 10 , and NO 2 pollution was 749, 409 and 101, respectively, which resulted in a total economic cost of 5.94 million CNY, 3.5 million CNY and 0.63 million CNY, respectively.These findings suggest that more hospitalizations and economic lost could be avoided if recorded PM and NO 2 levels is at lower levels.Our study only assessed people over 65 years of age, which is different from other population-wide assessments, despite this, it cannot be ignored that the impact of air pollution on the health of the older adults population in Sichuan remains a more serious public health challenge compared with other regions.

Strengths and limitations
This study has made two contributions.First, data were collected from nine cities and prefectures across Sichuan province, which can represent the overall characteristics of the province to some extent.Second, the relationships between air pollutants and asthma hospitalization among the older adults were examined and discussed, and the economic burden was assessed, providing empirical evidence for the association between air pollutants and asthma among the older adults.Meanwhile, this study has certain limitations.First, this is an ecological study, although it was adjusted for several confounding factors such as the day of the week, public holidays, and weather conditions, asthma has multiple etiologic factors, and the interference and influence of confounding factors such as environmental chemicals, personal health status, and individual lifestyle habits were unavoidable in this study.Second, the air pollutant concentration data were obtained from fixed monitoring sites and measurement bias of exposure levels was inevitable.Finally, in calculating the economic costs, we may be underestimating the burden of air pollution because we only consider the number of people treated in hospital and use the number of days in hospital to measure lost productivity.
Based on these findings, first, strategies for prevention of asthma should focus on providing educational health messages in older adults (≥65).Second, because there is no completely safe level of air pollutants, more stringent regulations on industry and automobiles, and a more active notification system for high levels of air pollutants, may help to prevent asthma.Third, reduced air pollution from industrial upgrades, vehicle and fuel renovations, better public transportation and increasing green space (76) can prevent respiratory diseases.Finally, we need a comprehensive pre-warning system to help patients with asthma diseases prepare and take preventive measures in advance, and reduce the social and economic burden of air pollution.

Conclusion
We found that short-term exposure to air pollutants was significantly associated with increased the risk of asthma hospitalization in people aged ≥65 years with a lag effect.Additionally, the number of asthma hospitalizations attributable to PM and NO 2 pollution during the study period was 1,345 and 95, respectively, with a total economic cost of 10.952 and 0.776 million CNY, respectively.These findings are of great importance to the formulation of health 1 http://www.scdata.net.cn/ 2 https://lbs.amap.com/and meteorological factors, with absolute values of the correlation coefficient r closer to 1 indicating a stronger correlation.

1 Q and  2 Q 1 SE and  2 2
are the RR estimates for different categories in each subgroup (e.g., male and female), and  2 SE are their respective standard deviations.

FIGURE 2
FIGURE 2Relative risks (95% CI) of older adults HAs for asthma per 10 μg/m 3 increase in concentrations of air pollutants (1 mg/m 3 increase in CO) for different lag days in the single pollutant models in Sichuan province, China, during 2017-2019.
WHO air quality standard in Sichuan province 2017-2019.Based on the reference concentrations, 764, 581 and 95 total cases of HAs for asthma could be attributable to PM 2.5 , PM 10 and NO 2 , separately.The total economic cost caused by exposure to particulate matter (PM, includes PM 2.5 and PM 10 ) was 10.952 million CNY, including a direct medical cost of 10.788 million CNY, and an indirect economic cost of 0.164 million CNY.Exposure to PM 2.5 caused the highest economic cost of 6.222 million CNY, while that attributable to NO 2 exposure was 0.776 million CNY.

FIGURE 3
FIGURE 3 Stratified analyses by age, season and gender for each air pollutant in Sichuan province, China, 2017 to 2019.(A) Results of stratified analysis of CO, NO 2 and O 3 .(B) Results of stratified analysis of PM 10 , PM 2.5 and SO 2 .

TABLE 1
Statistical description of air pollutants and meteorological variables in the 9 cities of Sichuan province, 2017-2019.

Table 2
listed the attributable number of HAs and the related economic cost due to exceeding PM and NO 2 exposure involving

TABLE 2
The attributable number of hospitalizations and economic cost due to pollution in Sichuan province, 2017-2019.
10.3389/fpubh.2024.1346914Frontiers in Public Health 10 frontiersin.orgcare policies for the older adult population and the direction of public health development.