Abstract

Background

Although seasonal variations in mortality have been recognized for millennia, the role of temperature remains unclear. We aimed to assess seasonal variation in mortality and to examine the contribution of temperature.

Methods

We compiled daily data on all-cause, cardiovascular and respiratory mortality, temperature and indicators on location-specific characteristics from 719 locations in tropical, dry, temperate and continental climate zones. We fitted time-series regression models to estimate the amplitude of seasonal variation in mortality on a daily basis, defined as the peak-to-trough ratio (PTR) of maximum mortality estimates to minimum mortality estimates at day of year. Meta-analysis was used to summarize location-specific estimates for each climate zone. We estimated the PTR with and without temperature adjustment, with the differences representing the seasonal effect attributable to temperature. We also evaluated the effect of location-specific characteristics on the PTR across locations by using meta-regression models.

Results

Seasonality estimates and responses to temperature adjustment varied across locations. The unadjusted PTR for all-cause mortality was 1.05 [95% confidence interval (CI): 1.00–1.11] in the tropical zone and 1.23 (95% CI: 1.20–1.25) in the temperate zone; adjusting for temperature reduced the estimates to 1.02 (95% CI: 0.95–1.09) and 1.10 (95% CI: 1.07–1.12), respectively. Furthermore, the unadjusted PTR was positively associated with average mean temperature.

Conclusions

This study suggests that seasonality of mortality is importantly driven by temperature, most evidently in temperate/continental climate zones, and that warmer locations show stronger seasonal variations in mortality, which is related to a stronger effect of temperature.

Key Messages
  • To our knowledge, this is by far the largest study on the seasonality of mortality by including 719 locations from 34 countries in tropical, dry, temperate and continental climate zones.

  • Our study provides evidence that the generally higher mortality in cold seasons than in warm seasons is considerably explained by temperature, and this pattern is most evident in temperate and continental climate zones.

  • Seasonality estimates and responses to temperature adjustment varied across locations, and locations characterized by a warm climate experienced larger seasonal variations in mortality, which was related to the stronger effect of temperature.

  • Our investigation of this long-known complex phenomenon provides important evidence for understanding the epidemiology and ecology of seasonal variation in mortality and the role of temperature.

  • Our findings also provide a basis for developing hypotheses about the potential impact of climate change on the seasonality of mortality for future investigations.

Introduction

Seasonal variation in mortality as a broad phenomenon has been recognized since Hippocrates.1 During certain times of the year, mortality increases substantially, which consequently increases the demand for healthcare services and may exert intense pressure on healthcare systems.2–10 The most plausible underlying mechanisms include seasonal fluctuations in the environment, human behaviours and infectious diseases.

Although consensus exists among researchers that the ambient temperature is a key driver, the extent to which temperature is actually the proximal cause of seasonal variation in mortality is a matter of long-standing debate.11,12 Few studies have attempted to address this topic.6 More importantly, previous investigations focused on a small number of locations within a limited geographical scope, which makes it difficult to draw comprehensive conclusions across different climate zones. To better understand the epidemiology and ecology of seasonal variation in mortality and the role of temperature, a systematic and comprehensive investigation on highly diverse populations including multiple locations from multiple climate zones is crucial. Such an investigation should further help us to develop hypothesis about the impact of the warming climate on seasonal dynamics of mortality for future investigations.

Moreover, the magnitude of seasonal variation in mortality varies substantially among different locations, possibly due to the differences in location-specific characteristics, e.g. socio-economic development. To date, some studies have explored this issue but were limited in geographical locations and climate zones.5,9,10,13–16 A comprehensive evaluation across multiple locations with various characteristics is warranted, as it will aid in identifying more vulnerable locations with a greater need for intervention.

In this research, we investigated the seasonality of mortality, with a particular focus on its magnitude, by analysing daily time-series data of mortality and temperature from 719 locations (i.e. city/province/prefecture) in 34 countries from tropical, dry, temperate and continental climate zones. Our primary focus in this study was to estimate the magnitude of the seasonal variation in mortality (i.e. seasonal amplitude) and to examine the extent to which temperature explains the seasonality of mortality. We also evaluated the modifying effects of location-specific characteristics on the seasonal variation of mortality. To our knowledge, this is by far the largest multi-country study on the seasonality of mortality.

Methods

Data collection

We collected daily time series of mortality and mean temperature from 719 locations in 34 countries in largely overlapping periods ranging from January 1969 to December 2016. The data were obtained through the Multi-Country Multi-City (MCC) Collaborative Research Network (http://mccstudy.lshtm.ac.uk/).17 Mortality was represented by daily counts of death from all causes or, where not available, non-external causes [International Classification of Diseases (ICD)-9 0–799, ICD-10 A00-R99] and cardiovascular (ICD-8 390–458, ICD-9 390–459, ICD-10 I00-I99) and respiratory diseases (ICD-8 and ICD-9 460–519, ICD-10 J00-J99). We also obtained information on Köppen–Geiger climate groups for each location, including tropical, dry, temperate and continental climate zones.18

We collected data on the indicators of location-specific characteristics for each location, including environmental factors, demographics and socio-economic factors. For environmental indicators, we considered the multi-year average value of daily mean temperature, daily mean temperature range, daily mean relative humidity and annual PM2.5 levels. For demographic and socio-economic factors, we collected from the Organisation for Economic Co-operation and Development Regional and Metropolitan Database, including the proportion of population aged ≥65 years old, gross domestic product, gross value added (GVA, a measure of labour productivity), education level, unemployment rate and Gini index (a measure of wealth inequality). The details for the indicators are included in the Supplementary Material (Page 5, Supplementary Material, available as Supplementary data at IJE online).

Statistical analysis

Estimating location-specific seasonality

In the first step, we performed location-specific time-series analyses to assess the seasonality of mortality using quasi-Poisson regression models19 throughout the study period available in each location. Day of year was considered as the exposure indicator for seasonality. This is different from previous studies,2–10 which used monthly aggregated data to compare winter mortality with other times of the year. In this study, we took values from 1 to 366 to represent the day of year, corresponding to 1 January through to 31 December for locations in the northern hemisphere and 1 July to 30 June of the following year for locations in the southern hemisphere. To model seasonality, we used a cyclic spline with 4 degrees of freedom (df) for the day of year. The days of year with maximum and minimum mortality predictions were identified as the peak and trough, respectively, of the seasonality of mortality. We then took the ratio of the mortality predicted at the peak to the mortality prediction at the trough (peak-to-trough ratio, PTR) to summarize seasonality. A stratum defined by year, day of week and their interaction was used to control for long-term trends and the effect of the day of week.

We then added temperature to the model described above for each location, by using a distributed lag non-linear model (DLNM)20 to estimate seasonality adjusting for temperature effect. We modelled the non-linear and non-linearly delayed effect of temperature on mortality using a cross-basis with natural cubic spline for temperature with three internal knots at the 25th, 50th and 75th percentiles of temperature, and another natural cubic spline for lag with 3 df. The lag was extended up to 21 days.17 From this model, we also calculated the PTR to represent temperature-adjusted seasonality.

Pooling the location-specific seasonality by country and climate zone

In the second step, location-specific estimates of the seasonal curve (i.e. coefficients of knot points) with and without temperature adjustment were pooled separately by climate zone through two-level (locations nested within country/region) random-effects multivariate meta-analysis techniques.21 We also pooled the estimates by each of 34 countries/regions with location considered as the random-effect factor. Using the pooled coefficients, the seasonal curve and the corresponding PTR were estimated for each country and each climate zone.

Modification of seasonality by location-specific characteristics

In the final step, we first explored the between-location heterogeneity of the seasonal curve by including the location-specific average temperature, temperature range, indicator for country and indicator for Köppen–Geiger climate zone as meta-predictors in the random-effects meta-regression.22 The heterogeneity was tested for location-specific seasonality estimates before and after adjusting for temperature separately. Next, we evaluated the association of the unadjusted and adjusted PTR with each indicator in separate meta-regression models including indicators for countries and climate zones. For each indicator, the original value was scaled by the average value of the country to remove the between-countries effects from the correlation. Results were expressed as log (PTR) variation for a standard deviation increase in the indicator.

Sensitivity analysis

We performed several sensitivity analyses. First, we evaluated how results changed with 5 and 6 df for the cyclic spline included in the location-specific time-series regression model. Second, we conducted seasonality assessment by using the subset of data since the year 2000. Finally, we investigated the sensitivity by changing the types of splines, lag days and df for the cross-basis function for temperature adjustment in the location-specific regression model.

We investigated the seasonality of all-cause, cardiovascular and respiratory mortality in separate analyses using R software, version 3.6.0 (R Development Core Team) using dlnm and mixmeta packages.

Results

The final analysis included 138 868 448 deaths from all or non-external causes in 719 locations in 34 countries, 39 777 149 deaths from cardiovascular diseases and 12 805 050 deaths from respiratory mortality in 519 locations in 22 countries. The country-specific average mean temperature ranged from 4.7°C in Norway to 27.6°C in Thailand. These temperatures are illustrative of locations characterized by four Köppen–Geiger climate zones18 (Figure 1), including 94 locations in the tropical climate zone (e.g. Ho Chi Minh City, Vietnam), 57 locations in the dry climate zone (e.g. Mashhad, Iran), 440 locations in the temperate climate zone (e.g. London, UK) and 128 locations in the continental climate zone (e.g. Hokkaido, Japan). Table 1 shows a summary of daily data for each climate zone. Supplementary Table S1 (available as Supplementary data at IJE online) summarizes the mortality in each season for each country/region.

Spatial distribution of location-specific averaged annual mean temperature of 719 locations in four Köppen–Geiger climate zones
Figure 1

Spatial distribution of location-specific averaged annual mean temperature of 719 locations in four Köppen–Geiger climate zones

(A) Tropical, (B) dry, (C) temperate and (D) continental.

Table 1

Summary (mean ± standard deviation) of daily mean temperature (°C) and daily mortalities (counts) by climate zone

Climate zoneNo. of locationsaMean temperatureAll-cause mortalitybCardiovascular mortalityRespiratory mortality
Tropical94/1826.68 ± 2.8614.91 ± 14.318.82 ± 6.052.44 ± 2.26
Dry57/5017.61 ± 8.1713.82 ± 12.873.81 ± 4.551.68 ± 2.19
Temperate440/35014.51 ± 8.4323.82 ± 36.968.44 ± 15.192.58 ± 5.34
Continental128/1188.85 ± 10.8711.58 ± 17.864.24 ± 6.410.96 ± 1.37
Climate zoneNo. of locationsaMean temperatureAll-cause mortalitybCardiovascular mortalityRespiratory mortality
Tropical94/1826.68 ± 2.8614.91 ± 14.318.82 ± 6.052.44 ± 2.26
Dry57/5017.61 ± 8.1713.82 ± 12.873.81 ± 4.551.68 ± 2.19
Temperate440/35014.51 ± 8.4323.82 ± 36.968.44 ± 15.192.58 ± 5.34
Continental128/1188.85 ± 10.8711.58 ± 17.864.24 ± 6.410.96 ± 1.37
a

No. of locations where all-cause/non-external mortality data were available/no. of locations where cause-specific mortality data were available.

b

Data on non-external mortality were used when data on all-cause mortality were not available for some locations.

Table 1

Summary (mean ± standard deviation) of daily mean temperature (°C) and daily mortalities (counts) by climate zone

Climate zoneNo. of locationsaMean temperatureAll-cause mortalitybCardiovascular mortalityRespiratory mortality
Tropical94/1826.68 ± 2.8614.91 ± 14.318.82 ± 6.052.44 ± 2.26
Dry57/5017.61 ± 8.1713.82 ± 12.873.81 ± 4.551.68 ± 2.19
Temperate440/35014.51 ± 8.4323.82 ± 36.968.44 ± 15.192.58 ± 5.34
Continental128/1188.85 ± 10.8711.58 ± 17.864.24 ± 6.410.96 ± 1.37
Climate zoneNo. of locationsaMean temperatureAll-cause mortalitybCardiovascular mortalityRespiratory mortality
Tropical94/1826.68 ± 2.8614.91 ± 14.318.82 ± 6.052.44 ± 2.26
Dry57/5017.61 ± 8.1713.82 ± 12.873.81 ± 4.551.68 ± 2.19
Temperate440/35014.51 ± 8.4323.82 ± 36.968.44 ± 15.192.58 ± 5.34
Continental128/1188.85 ± 10.8711.58 ± 17.864.24 ± 6.410.96 ± 1.37
a

No. of locations where all-cause/non-external mortality data were available/no. of locations where cause-specific mortality data were available.

b

Data on non-external mortality were used when data on all-cause mortality were not available for some locations.

A descriptive summary of location-specific indicators is shown in Supplementary Table S2 (available as Supplementary data at IJE online). Unemployment rates and PM2.5 concentrations showed a large variation between locations. Socio-economic indicators included in the analysis were correlated, and the averaged mean temperature was correlated with the other indicators (Supplementary Figure S1, available as Supplementary data at IJE online).

Before adjustment for temperature, a seasonal pattern was observed in all climate zones with a high mortality in cold seasons and a low mortality in warm seasons (Figure 2). When the temperature was adjusted, the seasonality of mortality remained higher in cold seasons in most climate zones, except for the seasonality of all-cause mortality in the tropical climate zone, where the adjusted seasonality became almost flat with a large confidence interval (Figure 2). The unadjusted PTR varied between climate zones, with the lowest estimate observed in the tropical zone (Table 2). The unadjusted PTRs for all-cause mortality were 1.05 [95% confidence interval (CI) 1.00–1.11] in the tropical climate zone and 1.23 (95% CI: 1.20–1.25) in the temperate climate zone, respectively (Table 2). Adjusting for temperature reduced the PTRs to different degrees, from a slight reduction observed in the tropical climate zone to a large reduction in the temperate climate zone: the pooled unadjusted PTR for all-cause mortality was reduced to 1.02 (95% CI: 0.95–1.09) in tropical climate zone and 1.10 (95% CI: 1.07–1.12) in temperate climate, respectively (Table 2).

Seasonality of mortality without (black) and with (red) temperature adjustment in four Köppen–Geiger climate zones
Figure 2

Seasonality of mortality without (black) and with (red) temperature adjustment in four Köppen–Geiger climate zones

(A) Tropical, (B) dry, (C) temperate and (D) continental. The seasonality is computed as the relative risk of mortality estimates at each day of year to daily minimum mortality estimates at the trough day with 95% confidence intervals (95% CIs) for four Köppen–Geiger climate zones: 

These estimates are obtained by pooling location-specific estimates for each climate zone. We took values from 1 to 366 to represent the day of year, corresponding to 1 January through 31 December for locations in the northern hemisphere and 1 July to 30 June of the following year for locations in the southern hemisphere (for common years, values were taken from 61 to 366 from the 60th day to the 365th day).

These estimates are obtained by pooling location-specific estimates for each climate zone. We took values from 1 to 366 to represent the day of year, corresponding to 1 January through toe 31 December for locations in the northern hemisphere and 1 July to 30 June of the following year for locations in the southern hemisphere (for common years, values were taken from 61 to 366 from the 60th day to the 365th day).

These estimates are obtained by pooling location-specific estimates for each climate zone. We took values from 1 to 366 to represent the day of year, corresponding to 1 January through toe 31 December for locations in the northern hemisphere and 1 July to 30 June of the following year for locations in the southern hemisphere (for common years, values were taken from 61 to 366 from the 60th day to the 365th day).

Table 2

Pooled peak-to-rough ratio (95% confidence intervals) for each climate zone

TemperatureTropicalDryTemperateContinental
All-cause mortalityUnadjusted1.05 (1.00, 1.11)1.23 (1.18, 1.30)1.23 (1.20, 1.25)1.20 (1.17, 1.23)
Adjusteda1.02 (0.95, 1.09)1.16 (1.14, 1.19)1.10 (1.07, 1.12)1.08 (1.06, 1.10)
Cardiovascular mortalityUnadjusted1.16 (1.08,1.24)1.34 (1.27,1.41)1.32 (1.27,1.36)1.27 (1.22,1.32)
Adjusteda1.07 (1.01, 1.13)1.20 (1.16, 1.23)1.11 (1.10, 1.13)1.08 (1.07, 1.10)
Respiratory mortalityUnadjusted1.19 (1.01, 1.33)1.53 (1.19, 1.95)1.61 (1.42, 1.73)1.55 (1.46, 1.66)
Adjusteda1.08 (0.99, 1.17)1.72 (1.25, 2.37)1.36 (1.24, 1.49)1.39 (1.31, 1.46)
TemperatureTropicalDryTemperateContinental
All-cause mortalityUnadjusted1.05 (1.00, 1.11)1.23 (1.18, 1.30)1.23 (1.20, 1.25)1.20 (1.17, 1.23)
Adjusteda1.02 (0.95, 1.09)1.16 (1.14, 1.19)1.10 (1.07, 1.12)1.08 (1.06, 1.10)
Cardiovascular mortalityUnadjusted1.16 (1.08,1.24)1.34 (1.27,1.41)1.32 (1.27,1.36)1.27 (1.22,1.32)
Adjusteda1.07 (1.01, 1.13)1.20 (1.16, 1.23)1.11 (1.10, 1.13)1.08 (1.07, 1.10)
Respiratory mortalityUnadjusted1.19 (1.01, 1.33)1.53 (1.19, 1.95)1.61 (1.42, 1.73)1.55 (1.46, 1.66)
Adjusteda1.08 (0.99, 1.17)1.72 (1.25, 2.37)1.36 (1.24, 1.49)1.39 (1.31, 1.46)
a

Temperature was adjusted for each location by using a distributed lag non-linear model (DLNM): the non-linear exposure–response association was modelled by a natural cubic spline function with three internal knots at the 25th, 50th and 75th percentiles of temperature, and the lag–response curve was fit by another natural cubic spline function with 3 df with extended lag up to 21 days.

Table 2

Pooled peak-to-rough ratio (95% confidence intervals) for each climate zone

TemperatureTropicalDryTemperateContinental
All-cause mortalityUnadjusted1.05 (1.00, 1.11)1.23 (1.18, 1.30)1.23 (1.20, 1.25)1.20 (1.17, 1.23)
Adjusteda1.02 (0.95, 1.09)1.16 (1.14, 1.19)1.10 (1.07, 1.12)1.08 (1.06, 1.10)
Cardiovascular mortalityUnadjusted1.16 (1.08,1.24)1.34 (1.27,1.41)1.32 (1.27,1.36)1.27 (1.22,1.32)
Adjusteda1.07 (1.01, 1.13)1.20 (1.16, 1.23)1.11 (1.10, 1.13)1.08 (1.07, 1.10)
Respiratory mortalityUnadjusted1.19 (1.01, 1.33)1.53 (1.19, 1.95)1.61 (1.42, 1.73)1.55 (1.46, 1.66)
Adjusteda1.08 (0.99, 1.17)1.72 (1.25, 2.37)1.36 (1.24, 1.49)1.39 (1.31, 1.46)
TemperatureTropicalDryTemperateContinental
All-cause mortalityUnadjusted1.05 (1.00, 1.11)1.23 (1.18, 1.30)1.23 (1.20, 1.25)1.20 (1.17, 1.23)
Adjusteda1.02 (0.95, 1.09)1.16 (1.14, 1.19)1.10 (1.07, 1.12)1.08 (1.06, 1.10)
Cardiovascular mortalityUnadjusted1.16 (1.08,1.24)1.34 (1.27,1.41)1.32 (1.27,1.36)1.27 (1.22,1.32)
Adjusteda1.07 (1.01, 1.13)1.20 (1.16, 1.23)1.11 (1.10, 1.13)1.08 (1.07, 1.10)
Respiratory mortalityUnadjusted1.19 (1.01, 1.33)1.53 (1.19, 1.95)1.61 (1.42, 1.73)1.55 (1.46, 1.66)
Adjusteda1.08 (0.99, 1.17)1.72 (1.25, 2.37)1.36 (1.24, 1.49)1.39 (1.31, 1.46)
a

Temperature was adjusted for each location by using a distributed lag non-linear model (DLNM): the non-linear exposure–response association was modelled by a natural cubic spline function with three internal knots at the 25th, 50th and 75th percentiles of temperature, and the lag–response curve was fit by another natural cubic spline function with 3 df with extended lag up to 21 days.

Our findings were generally similar for cause-specific mortalities (Figure 2 and Table 2). However, the change in seasonality estimates by temperature adjustment was more evident for cardiovascular mortality whereas it was less profound for respiratory mortality.

The location-specific seasonality estimates are presented in Figure 3 (Supplementary Table S3, available as Supplementary data at IJE online) and summarized for each country/region in Figure 4 (Supplementary Figure S2, available as Supplementary data at IJE online). Although the location- and country/region-specific results are generally consistent with our findings from the climate-zone-specific assessment, PTR estimates varied between locations/countries/regions even for those within the same climate zone (Page 37, Supplementary Material, available as Supplementary data at IJE online).

Peak-to-trough ratio (PTR) without (left) and with (right) temperature adjustment for each location for all-cause/non-external (blue), cardiovascular (red) and respiratory (green) mortality
Figure 3

Peak-to-trough ratio (PTR) without (left) and with (right) temperature adjustment for each location for all-cause/non-external (blue), cardiovascular (red) and respiratory (green) mortality

The size of the points corresponds to the precision of the PTR estimate (i.e. the inverse of the standard error of the PTR).

Peak-to-trough ratio (PTR) with 95% confidence intervals (95% CIs) without (black) and with (red) temperature adjustment for each country/region (numbers of locations in each country/region for each Köppen–Geiger climate zone§)
Figure 4

Peak-to-trough ratio (PTR) with 95% confidence intervals (95% CIs) without (black) and with (red) temperature adjustment for each country/region (numbers of locations in each country/region for each Köppen–Geiger climate zone§)

These estimates are obtained by pooling location-specific estimates for each country/region. *Countries/regions that have data for all mortality causes. §Four Köppen Geiger climate zones: (A) tropical, (B) dry, (C) temperate and (D) continental. Different background colours were used to highlight the climate zone for each country (red: tropical, yellow: dry, green: temperate, blue: continental and grey: multiple climate zones).

Our meta-analysis showed substantial heterogeneity between locations for seasonality estimates both with and without temperature adjustment (Supplementary Table S4, available as Supplementary data at IJE online). Results from our multivariate meta-regression models suggest that the heterogeneity for seasonality estimates with/without temperature adjustment for all mortality types was reduced when country indicators were included (Supplementary Table S4, available as Supplementary data at IJE online). The other three predictors (i.e. the indicators for climate zones, location-specific average mean temperature and location-specific total temperature range) all significantly modify the effect of seasonality both in the single-predictor and the full models, and account for a small proportion of the heterogeneity (Supplementary Table S4, available as Supplementary data at IJE online).

Figure 5 presents the association between each of the location-specific characteristics and the PTR. The average mean temperature was positively associated with the unadjusted PTR for all-cause mortality, and adjusting for temperature in the PTR moved the estimate towards the null. The other indicators showed no associations with the PTRs for all-cause mortality. Our analysis of cause-specific mortality showed similar results, with a few additional findings: for cardiovascular mortality, the total range of daily mean temperature was negatively associated with the unadjusted PTR, which moved toward the null after adjustment for temperature in the PTR; for respiratory mortality, the averaged mean relative humidity was negatively associated with both the unadjusted and adjusted PTR.

Associations between the indicators on location-specific characteristics and peak-to-trough ratios before (black) and after (red) temperature adjustment
Figure 5

Associations between the indicators on location-specific characteristics and peak-to-trough ratios before (black) and after (red) temperature adjustment

Coefficients with 95% confidence intervals (95% CIs) were obtained from a meta-regression model adjusted by indicators for country and climate zone. Results are expressed as the changes in log(PTR) for standard deviation increase in the indicators.

Results from sensitivity analyses (Supplementary Table S5, available as Supplementary data at IJE online) suggest that the pooled seasonality curve and the PTR in each climate zone of the main analysis were generally robust to different approaches (Supplementary Figures S3 and S4, available as Supplementary data at IJE online). The country- and region-specific PTR estimates for those with most locations characterized by tropical climates seemed to be less sensitive to different modelling choices (Supplementary Tables S6 and S7, available as Supplementary data at IJE online). The unadjusted PTR for most countries/regions was reduced in the subperiod analysis by using data since the year 2000 (Supplementary Table S6, available as Supplementary data at IJE online). In addition, associations between indicators and PTRs remained similar when using different approaches (Supplementary Figure S5, available as Supplementary data at IJE online).

Discussion

Our study systematically and comparatively investigated the seasonality of mortality in 719 locations of 34 countries covering a wide range of environmental conditions, population dynamics and socio-economic status. To our knowledge, this is the largest investigation on the seasonality of mortality. Our study provides evidence that the generally higher mortality in cold seasons than in warm seasons is considerably explained by temperature, and this pattern is most evident in temperate and continental climate zones. Despite a similar pattern, the amplitudes of seasonality varied between locations. Locations characterized by a warm climate experienced larger seasonal variations in mortality, which were related to a stronger effect of temperature. Our investigation of this long-known complex phenomenon provides important evidence for understanding this phenomenon and informing the ongoing discussion on future impacts of the warming climate.

Winter peaks and summer troughs in the seasonality of mortality have been broadly defined and consistently described in previous studies2–10 and we observed a similar seasonal pattern for most of the locations in our study. Although previous studies measured the magnitude of seasonality in mortality, direct comparison with our findings (i.e. the unadjusted PTR) is difficult due to the differences in modelling approaches. Where we applied time-series analysis to estimate the mortality on each day of the year and then compared the maximum mortality estimates with the minimum mortality estimates on a daily basis to measure the strength of seasonality, previous studies used mortality data aggregated to each month or, to a lesser extent, for each week and applied Fourier transforms to compare mortality estimates in peak months with those trough months. Stewart et al.2 reviewed 48 studies on the seasonality of cardiovascular mortality mostly from temperate areas in Europe and North America and reported an estimate of 1.23-fold (95% CI: 1.16–1.31) for the relative difference of cardiovascular mortality in peak-vs-trough seasons, which was lower than our estimate on the seasonality of cardiovascular mortality in temperate zones [1.32 (95% CI: 1.27–1.36)].

One highlight of our investigation is the assessment of the extent to which the seasonal variation in temperature is associated with seasonal variation in mortality. Despite the extensive literature on the effects of cold and hot temperatures on health, debate remains regarding whether temperature is the main cause of the seasonality of mortality.11,12,23 Addressing this issue is essential for understanding the epidemiology and ecology of seasonal variation in mortality. Using multi-decade data from 36 cities in the USA and 3 cities in France covering a wide range of winter temperatures from −5°C to >20°C, Kinney et al.12 observed no correlations between seasonal temperature differences (the difference in mean temperature between winter and summer) and winter excess mortality, and concluded that temperature was not a key driver of winter excess mortality. However, this conclusion can be misleading, as their findings actually answered the question of whether the spatial variation in the strengths of seasonal variation in mortality was related to the differences in seasonal temperature differences. In our study, we estimated the temperature-adjusted seasonal variation in mortality and demonstrated that temperature is an important driver of seasonal variation in mortality, especially in temperate/continental climate zones. Our findings, on the other hand, provide a basis for developing hypotheses about the potential impact of climate change on the seasonality of mortality, e.g. whether an increasing temperature and shortening winter season will reduce winter mortality, increase summer mortality and subsequently attenuate their variation between seasons. Future investigations are merited to investigate these hypotheses by taking into account the increasing extreme weathers (e.g. cold spells, snowfall or ice), other seasonal events (e.g. infectious disease outbreaks) and human adaptation, which is beyond the scope of the current study.

It should be noted that other unmeasured seasonally varying factors, e.g. sunlight, rainfalls, infectious disease incidence and human behaviour, may also contribute to the seasonality of mortality.2 For example, the increase in infectious disease-related mortality during rainy seasons may explain the seasonal variation in total mortality in the tropical climate zone13 and influenza infections may increase the risk of excess mortality in winter.23–25 Furthermore, we found that seasonal variation in respiratory mortality seems to be less explained by temperature than are all-cause and cardiovascular mortalities. This result may be explained by the fact that the increase in respiratory mortality during the winter season can be considerably attributed to seasonal respiratory infections (e.g. influenza and respiratory syncytial virus). Further research in the seasonal pattern of mortality considering various kinds of seasonally varying factors would complement the evidence provided in this study.

Our results showed a significant spatial variation in the amplitude of seasonality across locations, and climate factors at the location level contributed to this spatial variation but cannot fully characterize the differences between the locations. Before adjusting for temperature in the seasonality assessment, we found a larger seasonal variation in locations characterized by a warm climate; this modification became weak on the remaining seasonality after removing the short-term effect of temperature. Consistently, previous studies on the effects of cold temperature reported that cold-related mortality was higher in warm climates than in cold climates.10,26,27 One explanation is that populations routinely exposed to a warm climate are less adapted to or prepared for cold weather during the year (e.g. lack of proper insulation). In addition, our results in cause-specific mortality showed that populations from less humid areas may exhibit a large seasonal variation for respiratory mortality. This result may be related to the impact of humidity on respiratory-tract infections and transmissions (e.g. fomites). Low humidity in cold weather may increase the survival of influenza virus and increase its transmission,24 and a decrease in temperature and humidity can precede the onset of infections.28 Therefore, humidity can possibly modify the seasonality of respiratory mortality. Elaborating on this phenomenon could be a topic for future studies.

Some limitations must be acknowledged. First, our seasonality assessment was based on the assumption that the seasonal variation in mortality and the role of temperature have not changed over the study period. In our sensitivity analysis, we repeated the assessment by using the data since 2000: although the results showed a reduction in the unadjusted PTR for most countries/regions, the main findings and conclusions did not change. However, future studies are warranted to investigate this complex research topic—whether or not and how the seasonality of mortality has changed over the years. Second, we used the PTR as a numeric measure of seasonality, which may be limited as it only quantifies the amplitude of the seasonal variation in mortality. In other words, the PTR is not able to reflect the shape of the seasonal variation in mortality. Further investigations would be beneficial by improving the seasonality assessment, e.g. quantifying the area under the seasonal curve as an attributable fraction. Third, coverage of tropical and dry climate zones and less developed locations was limited in our study, especially for cardiovascular and respiratory mortality, so the results for these areas should be interpreted with caution. The country-level estimates for several countries (e.g. Sweden, China and Iran) may not be representative, as only a small number of locations from these countries were included in our analysis. Fourth, we did not explore the modifying effect of indicators by using a multivariable model, because of a high correlation between indicators. Finally, the collection (e.g. case ascertainment, codification) and processing of mortality data may vary between countries.

Despite these limitations, our study is, to our knowledge, the largest investigation of the seasonality of mortality. This multi-country study used the largest database of location-level daily time series for mortality for 719 locations from 34 countries and identified a strong seasonal variation in mortality in temperate climate zones, which was attenuated substantially after adjusting for temperature, whereas a small seasonal variation was observed in tropical climate zones. Moreover, populations consistently exposed to warm climates seem to be more susceptible to seasonal variation in mortality. Based on this large and geographically versatile data set and well-tested methods, our findings provide a better understanding of this long-known complex phenomenon and a basis for generating hypotheses about the future impact of climate change on the seasonality of mortality, which ultimately could help with the development of health systems and infrastructure planning in the future.

Members of the MCC Collaborative Research Network

Multi-Country Multi-City (MCC) Collaborative Research Network: Rosana Abrutzky,1 Fiorella Acquaotta,2 Caroline Ameling,3 Antonis Analitis,4 Christofer Åström,5 Shih-Chun Pan,6 Micheline de Sousa Zanotti Stagliorio Coelho,7 Patricia Matus Correa,8 Tran Ngoc Dang,9 Francesca de'Donato,10 Magali Hurtado Diaz,11 Do Van Dung,9 Alireza Entezari,12,13 Bertil Forsberg,5 Simona Fratianni,2† Patrick Goodman,14 Yue Leon Guo,6,15 Iulian Horia Holobâca,16 Danny Houthuijs,3 Veronika Huber,17,18 Ene Indermitte,19 Carmen Íñiguez,20 Jouni J K Jaakkola,21,22 Haidong Kan,23 Klea Katsouyanni,4,24 Ho Kim,25 Jan Kyselý,26,27 Eric Lavigne,28,29 Whanhee Lee,25 Shanshan Li,12 Fatemeh Mayvaneh,13 Paola Michelozzi,10 Baltazar Nunes,30,31 Hans Orru,19 Nicolás Valdés Ortega,32 Samuel Osorio,33 Ala Overcenco,34 Mathilde Pascal,35 Martina S. Ragettli,36,37 Shilpa Rao,38 Niilo R I Ryti,21 Paulo Hilario Nascimento Saldiva,7 Alexandra Schneider,39 Joel Schwartz,40 Noah Scovronick,41 João Paulo Teixeira,42 Shilu Tong,43–46 Aleš Urban,26,27 César De la Cruz Valencia,11 Ana Maria Vicedo-Cabrera,47,48 Antonella Zanobetti40 and Ariana Zeka49

Deceased.

1Universidad de Buenos Aires, Facultad de Ciencias Sociales, Instituto de Investigaciones Gino Germani, Buenos Aires, Argentina, 2Department of Earth Sciences, University of Turin, Italy, 3National Institute for Public Health and the Environment (RIVM), Centre for Sustainability and Environmental Health, Bilthoven, Netherlands, 4Department of Hygiene, Epidemiology and Medical Statistics, National and Kapodistrian University of Athens, Greece, 5Department of Public Health and Clinical Medicine, Umeå University, Sweden, 6National Institute of Environmental Health Science, National Health Research Institutes, Zhunan, Taiwan, 7Institute of Advanced Studies, University of São Paulo, São Paulo, Brazil, 8Department of Public Health, Universidad de los Andes, Santiago, Chile, 9Department of Environmental Health, Faculty of Public Health, University of Medicine and Pharmacy at Ho Chi Minh City, Vietnam, 10Department of Epidemiology, Lazio Regional Health Service, Rome, Italy, 11Department of Environmental Health, National Institute of Public Health, Cuernavaca, Morelos, Mexico, 12Climate, Air Quality Research Unit, School of Public Health and Preventive Medicine, Monash University, Melbourne, Australia, 13Faculty of Geography and Environmental Sciences, Hakim Sabzevari University, Sabzevar, Khorasan Razavi, Iran, 14Technological University, Dublin, Ireland, 15Environmental and Occupational Medicine, and Institute of Environmental and Occupational Health Sciences, National Taiwan University (NTU) and NTU Hospital, Taipei, Taiwan, 16Faculty of Geography, Babes-Bolyai University, Cluj-Napoca, Romania, 17Potsdam Institute for Climate Impact Research, Potsdam, Germany, 18Department of Physical, Chemical and Natural Systems, Universidad Pablo de Olavide, Sevilla, Spain, 19Department of Family Medicine and Public Health, University of Tartu, Tartu, Estonia, 20Department of Statistics and Computational Research, University of València, València, Spain, 21Center for Environmental and Respiratory Health Research, and Biocenter Oulu, University of Oulu, Oulu, Finland, 22Finnish Meteorological Institute, Helsinki, Finland, 23Department of Environmental Health, School of Public Health, Fudan University, Shanghai, China, 24School of Population Health and Environmental Sciences, King's College, London, UK, 25Department of Public Health Science, Graduate School of Public Health, Seoul National University, Seoul, Republic of Korea, 26Institute of Atmospheric Physics of the Czech Academy of Sciences, Prague, Czech Republic, 27Faculty of Environmental Sciences, Czech University of Life Sciences, Prague, Czech Republic, 28School of Epidemiology and Public Health, Faculty of Medicine, University of Ottawa, Ottawa, Canada, 29Air Health Science Division, Health Canada, Ottawa, Canada, 30Department of Epidemiology, Instituto Nacional de Saúde Dr Ricardo Jorge, Lisboa, Portugal, 31Centro de Investigação em Saúde Pública, Escola Nacional de Saúde Pública, Universidade NOVA de Lisboa, Portugal, 32Facultad de Enfermería y Obstetricia, Universidad de los Andes, Chile, 33Department of Environmental Health, University of São Paulo, São Paulo, Brazil, 34Laboratory of Management in Science and Public Health, National Agency for Public Health of the Ministry of Health, Chisinau, Republic of Moldova, 35Santé Publique France, Department of Environmental Health, French National Public Health Agency, Saint Maurice, France, 36Swiss Tropical and Public Health Institute, Basel, Switzerland, 37University of Basel, Basel, Switzerland, 38Norwegian Institute of Public Health, Oslo, Norway, 39Institute of Epidemiology, Helmholtz Zentrum München—German Research Center for Environmental Health (GmbH), Neuherberg, Germany, 40Department of Environmental Health, Harvard T.H. Chan School of Public Health, Boston, MA, USA, 41Department of Environmental Health. Rollins School of Public Health, Emory University, Atlanta, USA, 42Department of Environmental Health, Instituto Nacional de Saúde Dr Ricardo Jorge, Porto, Portugal, 43Shanghai Children’s Medical Centre, Shanghai Jiao-Tong University, Shanghai, China, 44School of Public Health and Institute of Environment and Human Health, Anhui Medical University, Hefei, China, 45School of Public Health and Social Work, Queensland University of Technology, Brisbane, Australia, 46Center for Global Health, School of Public Health, Nanjing Medical University, Nanjing, China, 47Institute of Social and Preventive Medicine, University of Bern, Bern, Switzerland, 48Oeschger Center for Climate Change Research, University of Bern, Bern, Switzerland and 49Institute of Environment, Health and Societies, Brunel University London, London, UK.

Supplementary data

Supplementary data are available at IJE online.

Ethics approval

Not required.

Funding

This work was primarily supported by the Japan Society for the Promotion of Science (JSPS) KAKENHI [Grant Number 19K19461]. Y.C. was supported by a Senior Research grant [2019R1A2C1086194] from the National Research Foundation of Korea (NRF), funded by the Ministry of Science, ICT (Information and Communication Technologies). V.H. received support from the Spanish Ministry of Economy, Industry and Competitiveness [Grant ID: PCIN-2017-046]. J.K. and A.U. were supported by the Czech Science Foundation [project 18-22125S]. A.S. acknowledged funding from European Union’s Horizon 2020 research and innovation programme under grant agreement No 820655 (EXHAUSTION). A.G. was supported by the Medical Research Council-UK [Grant ID: MR/R013349/1], the Natural Environment Research Council UK [Grant ID: NE/R009384/1] and the European Union’s Horizon 2020 Project Exhaustion [Grant ID: 820655]. M.H. was supported by the Japan Science and Technology Agency (JST) as part of SICORP [Grant Number JPMJSC20E4].

Data availability

Data have been collected within the MCC (Multi-Country Multi-City) Collaborative Research Network (https://mccstudy.lshtm.ac.uk) under a data-sharing agreement and cannot be made publicly available. The R code for the analysis is available from the first author.

Conflict of interest

None declared.

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Author notes

A full list of the authors from MCC network is provided at the end of the manuscript

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Supplementary data