Introduction

Numerous reports have indicated that risks of morbidities and mortalities are associated with ambient concentration of fine particles with aerodynamic diameters less than or equal to 2.5 μm (PM2.5)1,2,3,4,5. In a cohort of 4.5 million US veterans, in comparison with a theoretical minimum risk exposure level of 2.4 μg/m36, results indicated that the 99% mortality burden of nonaccidental causes associated with ambient PM2.5 level is below the US national annual PM2.5 standard (12 μg/m3)4. Researchers identified the source apportionments of PM2.5 including industrial emission (or combustion-related source), motor vehicular exhaust, secondary aerosol (secondary nitrate and secondary sulfate), soil dust, natural source, and others (e.g., cooking). Thus, short- and long-term health risks associated with constituents of PM have been comprehensively reviewed1,2,3,5,7,8.

Most studies identified the robust short-term effects of ambient black and organic carbon on mortality from and morbidity of all causes and cardiovascular diseases1,3,5. Study conducted in China found that the effects of PM2.5 on respiratory diseases were getting stronger after 50 h exposures of it9. By contrast, no PM constituent had consistent significant risks under long-term exposure2,7. The constituents of PM2.5, which vary by study area, source, and season, resulting in various toxicities, are worthy of investigation3,10,11,12.

Previous studies evaluating temperature-health associations often used mortality, outpatients visits, or emergency room visits as health outcome in their studies8,13,14. Risks of ambulance dispatch services are rarely evaluated due to a lack of sufficient records. Ambulance call-out data provide new and valuable real-time information that is useful to assess the impact of environmental conditions, such as temperature and air pollution upon human health15.

Previous study conducted in Taiwan reported that pollutant constituents were attributable to anthropogenic emissions12. A China study observed that emissions from coal burning activities were common dominant sources of OC and EC, they also found that industrial area had higher concentration compared with urban area and coastal area16. Compare to other cities in Taiwan, the main sources of air pollution in Kaohsiung City is a combination between urban and industrial areas with a high proportion of factories and petrochemical industry clusters17. Even though the air pollution condition in Taiwan is not as severe as Beijing or Dehli, air pollution is still a major issue and has repeatedly induce public concerns in Central and Southern Taiwan since 201018. Therefore, this study aimed to evaluate the risks of ambulance services of respiratory distress, coma and unconsciousness, chest pain, headaches/dizziness/vertigo/fainting/syncope, lying at public, and out-of-hospital cardiac arrest (OHCA) in association with total mass and constituents of fine particulate matters of 2.5 μm in Kaohsiung City, an industrialized city of Taiwan, using records of PM2.5, and its constituents (elemental carbon (EC), organic carbon (OC), nitrate, and sulfate), from 2006 to 2010.

Materials and methods

Data sources

This study collected the ambulance services data of Kaohsiung City from the Ministry of Health and Welfare from 2006 to 2010. The information and privacy protection of the ambulance services database was described in a previous report19. Daily ambulance services records of cases diagnosed with respiratory distress, coma and unconsciousness, chest pain, headaches/dizziness/vertigo/fainting/syncope, lying at public, and OHCA were extracted from non-accidental disease code and analyzed for the association analysis with ambient environmental conditions.

The daily meteorological data, including average air temperature (oC), relative humidity (%), wind speed (m/s), were monitored at Kaohsiung surface meteorological observatory (station No. 467440) and collected from the Taiwan Central Weather Bureau. Hourly records of PM2.5, and its constituents (elemental carbon (EC), organic carbon (OC), nitrate, and sulfate) from 2006 to 2010 that were measured at three air quality supersites (Fooyin, Qiaotou, and Qianzhen stations; Fig. 1) were collected from the Taiwan Air Quality Monitoring Network. The sampling heights at the Fooyin, Qiaotou, and Qianzhen stations supersites are 4.7 m, 14.8 m, 11.1 m10. Sunset OC/EC (Sunset Laboratory, USA) helped to measure the continuous PM2.5, OC and EC in Kaohsiung City20. Studies conducted by Lin et al. (2008) and Kuo et al. (2011) provide detailed information on the monitoring instruments, stations, and quality assurance criteria related to the air quality supersites in Kaohsiung City.

Figure 1
figure 1

Locations of weather observatories and ambient air quality monitoring stations and district-level population density in 2010 in Kaohsiung City. Generated with ArcGIS Version 10.7 (http://www.esri.com/software/arcgis).

The daily mean temperature and mass concentrations of PM2.5 and its constituents (nitrate, sulfate, OC, and EC) were calculated and evaluated in a risk association model.

Statistical models

Non-linear risk association

A distributed lag non-linear model (DLNM) with quasi-Poisson function proposed by Gasparrini et al.21 was applied to assess the time-series non-linear exposure–response relationship between the daily mean measurements of temperature, mass concentrations of PM2.5, and its constituents (EC, OC, nitrate, and sulfate) and cause-specific number of ambulance services. The model was specified as

$$\mathrm{Log}\left[\mathrm{Y}\right] \sim \mathrm{ BS}\left(\mathrm{T},\mathrm{ lag\, }6\mathrm{\,day}\right)+\mathrm{ BS}\left({\mathrm{PM}}_{2.5}\mathrm{\,or \,constituents},\mathrm{\,lag\, }6\mathrm{\,day}\right)+\mathrm{NS}\left(\mathrm{time},7\mathrm{\,per\,year}\right)+\mathrm{NS}\left(\mathrm{ws},5\right)+\mathrm{ NS}\left(\mathrm{rh},4\right)+\mathrm{ holiday\, effect}+\mathrm{ dow}+\mathrm{PI}$$

where Y is the daily cause-specific number of ambulance services, and T is the daily mean temperature. We used the B-splines (BS) function with two equal knots for average temperature and two knots for lag response to estimate the lag-response risk association. The reference temperature, the temperature with the lowest number for cause-specific ambulance services, was evaluated. Overall 6-day (lag0–5) relative risk (RR) and related 95% confidence interval (CI) of cause-specific ambulance services associated with extreme temperatures (5th and 99th percentiles) were estimated and displayed, controlling for daily mass concentration of PM2.5.

Daily mass concentrations of PM2.5 and its constituents, set as BS function with 2 degrees for measurements and lag effect, were evaluated and included in the model separately. Cumulative 6-day risks of cause-specific ambulance services associated with mass concentration of PM2.5 were evaluated and displayed at 90th percentile of measurements, controlling for daily average temperature. The reference concentration was set at Q1 measurements. The cumulative 6-day risks of cause-specific ambulance services associated with mass concentration of PM2.5 constituents, controlling for daily average temperature and mass concentration of PM2.5, were evaluated and displayed in concentration and percentile scales.

The daily wind speed (ws) and relative humidity (rh) were included in the model and set as the natural spline (NS) function with 4 df, respectively. Time is included in the model for controlling long-term trend and seasonality22. Dow is dummy variable for controlling “day of a week effect” in the model9. Daily deaths from pneumonia and influenza (PI) were also included in the model.

All analyses in this study were carried out using the mgcv and dlnm packages in RStudio Version 1.2.1335 (http://www.R-project.org/).

Ethics approval and consent to participate

All methods were carried out in accordance with relevant guidelines and all protocols were approved by Taiwan National Health Research Institutes (code: EC1050701-E).

Results

Descriptive characteristics of ambient environment and ambulance services

In Kaohsiung, Taiwan, the proportions of ambulance services were 3.74% for respiratory distress, 3.04% for coma and unconsciousness, 1.99% for chest pain, 5.12% for headache/dizziness/vertigo/fainting/syncope, 3.33% for lying at public, and 2.04% for OHCA from 2006 to 2010. The daily average case numbers of ambulance services were 4.59 (range: 0–13) for respiratory distress, 3.73 (range: 0–12) for coma and unconsciousness, 2.44 (range: 0–10) for chest pain, 6.28 (range: 0–17) for headache/dizziness/vertigo/fainting/syncope, 2.40 (range: 0–9) for lying at public, and 2.51 (range: 0–11) for OHCA from 2006 to 2010 in Kaohsiung City (Table 1). No seasonal variations in daily numbers of cause-specific ambulance services were observed (Supplementary Fig. S1).

Table 1 Descriptive statistics for daily cause-specific ambulance services, mass and constituents concentrations of fine particulate matter (PM2.5), and weather measurements from 2006 to 2010.

The daily mean temperature was 25.4 °C (range: 13.5–31.5 °C), with mean PM2.5 concentration of 33.3 μg/m3 (range: 6.92–119 μg/m3). The mass concentrations were 4.35 μg/m3 (range: 0.34–21.5 μg/m3) for nitrate, 9.37 μg/m3 (range: 1.09–32.9 μg/m3) for sulfate, 8.00 μg/m3 (range: 1.38–27.1 μg/m3) for OC, and 2.21 μg/m3 (range: 0.43–13.2 μg/m3) for EC (Table 1). The annual concentrations of PM2.5, sulfate, and EC decreased from 2006 to 2010, but the concentrations of nitrate and OC remained stable during the study period (Supplementary Fig. S2). Figure 2 shows the boxplots for average mass concentrations of PM2.5, and its constituents by month. The average mass concentrations were lower in summer (June to August), but the proportions of EC and OC of PM2.5 were particularly high in summer (Supplementary Fig. S3).

Figure 2
figure 2

Boxplots for concentrations of mass and constituents of fine particulate matter (PM2.5) by month from 2006 to 2010 in Kaohsiung City. Generated with RStudio Version 1.2.1335 (http://www.R-project.org/) using packages ‘mgcv’ and ‘dlnm’ (The box encloses the interquartile range with the lower edge at the first quartile, q1, upper edge at the third quartile, q3. A line is drawn through the box at the second quartile (which is the 50th percentile or median). A whisker extends from each end of the box which is the smallest and largest values.

Relative risk of ambulance services associated with daily ambient temperature and PM2.5 concentration

Figure 3 shows the cumulative 6-day RR of cause-specific ambulance services in association with daily average temperature. The temperatures for the lowest number of ambulance services (reference temperature) were 18 °C for respiratory distress, 19 °C for coma and unconsciousness, 24 °C for chest pain, 28 °C for headache/dizziness/vertigo/fainting/syncope, 22 °C for lying at public, and 25 °C for OHCA. Ambulance services of coma and unconsciousness, chest pain, lying at public, and OHCA were elevated at extremely high temperature; the RR ranged from 1.37 to 1.81 at the 99th percentile of temperature (Table 2). By contrast, increased ambulance services of chest pain, headache/dizziness/vertigo/fainting/syncope, and OHCA were associated with extreme low temperature, with RR ranging from 1.19 to 1.48 at the 5th percentile of temperature (Table 2). Supplementary Fig. S4 shows temperature-related lag effects (lag0-5) on cause-specific ambulance services. The risks of ambulance services associated with heat peaked at lag0-1, but risks of ambulance services peaked at various lag days in cold environments.

Figure 3
figure 3

Cumulative 6-day risks of cause-specific ambulance services associated with ambient temperature in Kaohsiung City from 2006 to 2010. Generated with RStudio Version 1.2.1335 (http://www.R-project.org/) using packages ‘mgcv’ and ‘dlnm’.

Table 2 Cumulative 6-day (lag0-5) relative risks (RR) and related 95% confidence intervals (CI) for cause-specific ambulance services associated with daily average temperature at 5th and 99th percentiles and concentration of fine particulate matter (PM2.5) at 90th percentile.

Figure 4 shows the cumulative 6-day RR of cause-specific ambulance services in association with daily PM2.5 concentration. This study identified that only ambulance services of respiratory distress, lying at public, and OHCA increased as the PM2.5 concentration increased, with RR of 1.07–1.14 at 55.1 μg/m3 (90th percentile vs. 25th percentile; Table 2). Risk of ambulance services of lying at public was significantly associated with PM2.5 concentration ranging from 20 μg/m3 to 60 μg/m3, while the risk was significant for ambulance services of respiratory distress as PM2.5 concentration exceeded 60 μg/m3. Supplementary Fig. S5 shows lag effects (lag0-5) of the PM2.5 concentration on cause-specific ambulance services. Risk of ambulance services of respiratory distress, chest pain, and OHCA generally peaked at lag 0–1 in a high PM2.5 concentration environment.

Figure 4
figure 4

Cumulative 6-day risks of cause-specific ambulance services associated with mass concentrations of fine particulate matter (PM2.5) in Kaohsiung City from 2006 to 2010. Generated with RStudio Version 1.2.1335 (http://www.R-project.org/) using packages ‘mgcv’ and ‘dlnm’.

Relative risk of ambulance services associated with daily concentrations of PM2.5 constituents

Figure 5 illustrates the RR of cause-specific ambulance services associated with concentrations of PM2.5 constituents. After controlling for cumulative 6-day effects of temperature and PM2.5 concentration, the risk associations in percentile scale are displayed in Supplementary Fig. S6. Risks of ambulance services of respiratory distress and coma and unconsciousness increased as the nitrate concentration increased. Ambulance service of lying at public increased as the sulfate concentration was at 90th percentile (15.8 μg/m3) with RR of 1.35 (95% CI: 1.08–1.68). The risk of ambulance services of headache/dizziness/vertigo/fainting/syncope was significantly associated with OC concentration at 90th percentile (3.39 μg/m3) with RR of 1.31 (95% CI: 1.09–1.58). Elevated EC concentration increased the risks for respiratory distress, headache/dizziness/vertigo/fainting/syncope, lying at public, and OHCA with RRs of 1.08 (95% CI: 0.92–1.26), 1.11 (95% CI: 0.97–1.27) , 1.20 (95% CI: 1.02–1.41), and 1.20 (95% CI: 0.97–1.48) at 90th percentile (13.2 μg/m3), respectively.

Figure 5
figure 5

Cumulative 6-day risks of cause-specific ambulance services associated with mass concentrations of PM2.5 constituents. Generated with RStudio Version 1.2.1335 (http://www.R-project.org/) using packages ‘mgcv’ and ‘dlnm’.

Discussion

This study comprehensively evaluated the risk associations between cause-specific ambulance services, extreme temperatures, and mass concentrations of PM2.5 and its constituents. The significant cold effects on chest pain and headache/dizziness/vertigo/fainting/syncope and heat effects on coma and unconsciousness and lying at public were observed, while the risk of ambulance services of OHCA was elevated in both extreme heat and cold environments. Ambulance services of respiratory distress, lying at public, and OHCA increased as the PM2.5 concentration increased, and the risk was significant at the PM2.5 concentration of 20–60 60 μg/m3 for ambulance services of lying at public and higher than 60 μg/m3 for respiratory distress. After controlling for effects of daily average temperature and PM2.5 concentration, this study still identified the significant effects of sulfate and EC on ambulance services of lying at public and OC on headache/dizziness/vertigo/fainting/syncope as the concentrations of PM2.5 constituents were at 90th percentile.

Limited studies assessed associations between ambulance calls and ambient environment9,13,19,22,23,24,25,26,27. Studies in Emilia-Romagna in Italy23, Brisbane in Australia26, Taiwan19, and Huainan and Luoyang in China22,24, have indicated the numbers of ambulance calls associated with extreme heat; the risks generally increase as the daily temperature exceeds 27 °C19,23,26. However, no consistent finding for cold threshold was identified19,28. Kaohsiung City has a tropical climate (daily temperature ranging from 13.5 °C to 31.5 °C), but it is cooler than cities located near the equator, e.g., Singapore and Manila. Except for ambulance service of OHCA, we found that the significant risks associated with temperature were only identified in environments with extreme temperatures (< 5th and > 90th percentiles; Fig. 3).

Fine particulate matter (PM2.5) are characterized with a small diameter (< 2.5 µm) that can carry various toxic substances and reach the end of the respiratory tract with airflow, accumulate by diffusion, and damage other parts of the body through air exchange in the lungs29. A China review reported that organic aerosols account for 20%–45% of PM2.5 at sites across China with seasonal and spatial variation11. However, as the Taiwan Environmental Protection Administration has declared Kaohsiung City with the worst air quality in Taiwan, particulate sulfate was identified as a primary variable to explain the PM2.5 concentration for this metropolitan10. This study observed that the proportions of PM2.5 constituents were 12.1% for nitrate, 28.2% for sulfate, 25.5% for OC, and 7.56% for EC (Supplementary Fig. S3).

The European Study of Cohorts for Air Pollution Effects (ESCAPE) reported that the hazard ratio of PM2.5 should be 1.14 (95% CI: 1.04–1.26) per 10 μg/m3 for all-cause mortality2. A Korean study reported that the OHCA risk increased for 1.30% after 1 to 2 days exposure to PM2.5 by an elevation of 10 μg/m330. Our previous study19 identified that ambulance events are associated with high concentrations of PM2.5 (about 90 μg/m3) and significantly elevate the ambulance care for respiratory distress and OHCA. Previous research evaluated the health risks associated with components of PM2.5 in recent years3,5,7,8,14,31,32,33. Most studies identified significant short-term effects of PM2.5 and its constituents at lag0-28,14,33. Particulate matter significantly increased emergency ambulance dispatched at lag0-1 day in Japan34, at lag 0 in Chengdu, China35, and Sydney, Australia36.

A Beijing study reported combustion-related PM2.5 constituents, such as secondary nitrate and sulfate that accounted for 45.9% PM2.5 mass concentration, had significant impacts on supraventricular premature beats and atrial tachycardia31. Meanwhile, two Shanghai studies reported that the risk of ischemic stroke hospitalization is significantly associated with previous day EC and heavy metal (Cr, Fe, Cu, Zn, As, Se, and Pb) concentrations33; moreover, the mortality risks of cardiovascular diseases associated with previous 2-day exposure of OC, sulfate, ammonia, potassium, and heavy metals (Cu, As, and Pb) with RRs ranging from 1.02 to 1.03 per interquartile increase14. After adjusting the total PM concentration, hospital admissions of cardiovascular diseases were significantly associated with EC and sulfate of PM2.5 at lag 0, and those of respiratory diseases were associated with sulfate at lag 0 and OC and EC at lag 18. On the basis of the findings of the present study and previous reports, the risks of total PM2.5 and its constituents could be observed at lag0-2.

A plausible mechanism may explain the short-term association between risk of cardiorespiratory diseases and components of PM2.5. One researcher found that elevated blood pressure is associated with ambient increased concentrations of OC, EC, nitrate, and ammonium in patients comorbid with chronic obstructive pulmonary disease37. In addition, the linkages between elevations of airway (fractional exhaled nitric oxide)32 and circulating inflammatory biomarkers (interleukin-8, tumor necrosis factor-α, and monocyte chemoattractant protein-1)38 and increased ambient concentrations of sulfate and potassium at lag 0–2 were identified and reported.

No significant association was reported in a long-term exposure-risk assessment for PM2.5 constituents (Cu, Fe, K, Ni, S, Si, V, and Zn) and mortality from cardiovascular diseases in a study involving 19 European cohorts (ESCAPE and TRANSPHORM projects)2,7. However, increased risks of dementia, Alzheimer’s disease, autism spectrum disorder, and Parkinson’s disease were significantly associated with long-term PM2.5 exposure with RR ranging from 1.16 to 3.2639. Migraines are a significant risk factor for Alzheimer’s disease and all‐cause dementia40. After adjusting the effects of daily temperature and PM2.5, this study identified that increased ambulance service of headache/dizziness/vertigo/fainting/syncope was significantly associated with concentrations of OC and EC. Future studies may discuss detailed biological mechanisms between PM2.5 constituents and neurological disorders.

The present study holds several strengths. Confounders, such as the holiday effect, day of the week, long-term trend, and risk associated with infectious pneumonia and influenza, and effects of daily temperature and total PM2.5 level were considered in the data analysis models. Risk of cause-specific ambulance services associated with daily concentrations of PM2.5 components was evaluated using continuous hourly monitored data. To date, the risk of ambulance service associated with concentrations of PM2.5 components requires further study. The findings from this study can be the ground information to minimize the response time of allocation ambulance services, by knowing which variables should be observed and forecasted in the future41. In addition, the individuals can adapt their behavior to enhance health and resilience against the negative impacts from temperature and concentrations of mass and constituents of PM2.5.

This study also had several limitations. First, our work is an ecological study. Risk was not estimated with individual-based data. Given the lack of information on personal disease history, medicine usage, behaviors of drinking and exercise, and accessibility of medical services, we did not evaluate modifying effects (e.g., socio-economic status) on risk associated with the ambulance events. Cases’ diagnoses in the medical records of ambulance dispatches were based on observations made by medical personnel, and no ICD codes were provided. In addition, this study did not exclude the complicated conditions of ambulance services, including delayed arrival time, restricted service time, and a location hard to reach. Moreover, this study did not collect ions and heavy metal data of gases and aerosols during the study period, so these effects were not evaluated.

Understanding the short-term risk association between ambulance services and ambient environment is a critical concern for organizers of outdoor activities, especially in extreme temperatures and high air pollution events. The present study provides scientific evidence that, other than mortality from and morbidity of cardiorespiratory diseases3,5, cause-specific ambulance services, even for general health symptoms like headache/dizziness/vertigo/fainting/syncope, are associated with concentrations of PM2.5 constituents after adjusting the effects of daily temperature and total PM2.5 level. This study agreed with a review report3, who reported that EC has stronger association with health risks that means elevation of ambulance service in the present study. We also agree that constituents and its proportion of PM2.5 vary with the study area, thus, health risk assessment for various health outcomes and area are recommended1,2.

Conclusions

This study evaluated how ambulance services, including call helps of respiratory distress, coma and unconsciousness, chest pain, headache/dizziness/vertigo/fainting/syncope, lying in public, and OHCA, were associated with daily temperature, total PM2.5 level, and concentrations of constituents in the city with worst air quality, Kaohsiung City, in Taiwan. The temperatures with the lowest ambulance services ranged from 18 to 28 °C for various cause-specific ambulance services. Increased call helps of chest pain and OHCA were associated with both extreme high and low temperatures. In addition, risk of ambulance services of lying at public significantly associated with PM2.5 concentration ranged from 20 to 60 μg/m3, and the risk of ambulance services of respiratory distress was significant as the PM2.5 concentration exceeded 60 μg/m3. After adjusting the cumulative 6-day effects of temperature and total PM2.5 level, this study observed that ambulance services of headache/dizziness/vertigo/fainting/syncope significantly increased with increased daily OC and EC concentrations. Meanwhile, the risk of ambulance services of lying at public was significantly associated with daily sulfate and EC concentrations. This study provides health risk in association with PM2.5 constituents in an industrialized city located in Southeast Asia. Health effects from exposure to hot and humid climate and PM2.5 with high toxicity potential were revealed in this study of a simulated scenario for Western industrialized cities in the future.