Research Article Volume 122 | Issue 1 | January 2014
Environ Health Perspect; DOI:10.1289/ehp.1306670
Estimation and Uncertainty Analysis of Impacts of Future Heat Waves on Mortality in the Eastern United States
Jianyong Wu,1 Ying Zhou,1 Yang Gao,2,3 Joshua S. Fu,2 Brent A. Johnson,4 Cheng Huang,5 Young-Min Kim,1 and Yang Liu1
Background: Climate change is anticipated to influence heat-related mortality in the future. However, estimates of excess mortality attributable to future heat waves are subject to large uncertainties and have not been projected under the latest greenhouse gas emission scenarios.
Objectives: We estimated future heat wave mortality in the eastern United States (approximately 1,700 counties) under two Representative Concentration Pathways (RCPs) and investigated sources of uncertainty.
Methods: Using dynamically downscaled hourly temperature projections for 2057–2059, we projected heat wave days that were defined using four heat wave metrics and estimated the excess mortality attributable to them. We apportioned the sources of uncertainty in excess mortality estimates using a variance-decomposition method.
Results: Estimates suggest that excess mortality attributable to heat waves in the eastern United States would result in 200–7,807 deaths/year (mean 2,379 deaths/year) in 2057–2059. Average excess mortality projections under RCP4.5 and RCP8.5 scenarios were 1,403 and 3,556 deaths/year, respectively. Excess mortality would be relatively high in the southern states and eastern coastal areas (excluding Maine). The major sources of uncertainty were the relative risk estimates for mortality on heat wave versus non–heat wave days, the RCP scenarios, and the heat wave definitions.
Conclusions: Mortality risks from future heat waves may be an order of magnitude higher than the mortality risks reported in 2002–2004, with thousands of heat wave–related deaths per year in the study area projected under the RCP8.5 scenario. Substantial spatial variability in county-level heat mortality estimates suggests that effective mitigation and adaptation measures should be developed based on spatially resolved data.
Citation: Wu J, Zhou Y, Gao Y, Fu JS, Johnson BA, Huang C, Kim YM, Liu Y. 2014. Estimation and uncertainty analysis of impacts of future heat waves on mortality in the eastern United States. Environ Health Perspect 122:10–16; http://dx.doi.org/10.1289/ehp.1306670
Address correspondence to Y. Liu, Department of Environmental Health, Rollins School of Public Health, Emory University, 1518 Clifton Rd. NE, Atlanta, GA 30322 USA. Telephone: (404) 727-2131. E-mail: firstname.lastname@example.org
The study was supported mainly by the Climate and Health Program at the Centers for Disease Control and Prevention (CDC; grant 5 U01 EH000405 managed by G. Luber) and by the National Institutes of Health (grant 1R21ES020225). The climate model simulations were supported in part by the National Science Foundation through TeraGrid resources provided by National Institute for Computational Sciences (grants TG-ATM110009 and UT-TENN0006). The data simulations used resources of the Oak Ridge Leadership Computing Facility at the Oak Ridge National Laboratory, which is supported by the Office of Science of the U.S. Department of Energy (DOE) (contract DE-AC05-00OR22725). Y.G. was supported in part by the Office of Science of the U.S. Department of Energy as part of the Regional and Global Climate Modeling Program. The Pacific Northwest National Laboratory is operated for DOE by Battelle Memorial Institute (contract DE-AC05-76RL01830).
The authors declare they have no actual or potential competing financial interests.
Received: 19 February 2013
Accepted: 1 November 2013
Advance Publication: 6 November 2013
Final Publication: 1 January 2014
- Supplemental Material (7.5 MB) PDF
Heat is a well-known natural hazard. During the summer, high temperatures may result in heat exhaustion, heat syncope, heat stroke, and heat cramps in susceptible individuals, leading to excess mortality at the population level (Gasparrini and Armstrong 2011; Kovats and Hajat 2008). Heat waves, commonly defined as a few consecutive days with high temperature above a certain threshold, are the leading cause of weather-related mortality in the United States (Davis et al. 2003). For example, the severe heat wave in Chicago, Illinois, in July 1995 resulted in approximately 700 deaths (Semenza et al. 1996). In California, the estimated excess mortality attributable to heat waves in July 2006 ranged from 160 to 333 deaths (Ostro et al. 2009).
According to the Intergovernmental Panel on Climate Change (IPCC), air temperature is projected to rise by 1.8–6.4°C by 2100 (IPCC 2007). The frequency, intensity, and duration of heat waves will likely increase in the future, thus aggravating heat-related mortality unless population adaptation occurs. Consequently, preparedness for adverse outcomes of future heat waves is necessary. However, accurately estimating the health impact of heat waves is challenging because of the uncertainties related to future temperature projections, heat wave metrics, population growth patterns, population susceptibility to heat waves, and spatial heterogeneity of heat waves. A recent study that considered several different climate change scenarios and seven global climate models estimated that future heat waves in Chicago would cause 166–2,217 deaths/year during 2081–2100 (Peng et al. 2011). However, Peng et al. (2011) projected future heat wave mortality in only one city and did not consider spatially resolved temperature data. Because the health impacts of heat waves can have significant spatial variability, mitigation strategies are unlikely to be universally effective. To take local needs into account, spatially resolved estimates of health outcomes due to heat waves are very important.
In the present study, we estimated county-level excess mortality attributable to heat waves across the eastern United States during 2057–2059 using spatially and temporally resolved regional climate model simulation results and also examined factors that contributed to uncertainty. First, we used state-of-the-art high-resolution climate projections to estimate future heat waves at the county level. Next, we estimated the future excess mortality related to heat waves considering several population growth patterns. Finally, we attributed the uncertainties in the excess mortality estimates to various factors using a variance-decomposition method.
Study area. We focused on the eastern United States (east of 95° longitude), an area that covers approximately 1,700 counties, has a large population (> 180 million), and has diverse weather conditions and geography.
Climate model simulation data. Developed at the National Center for Atmospheric Research (NCAR), the Community Earth System Model (CESM1.0) is a coupled climate model that simultaneously simulates the Earth’s atmosphere, ocean, land surface, and sea ice (Gent et al. 2011). For the present study, we used CESM-projected coarse-resolution temperature data for 2057–2059 under two Representative Concentration Pathway (RCP) emissions scenarios. RCPs, the most recent approach to emissions trajectories used by the IPCC (Inman 2011; Moss et al. 2010), include four emissions scenarios (RCP8.5, RCP6.0, RCP4.5, and RCP2.6), representing the radiative forcing levels of greenhouse gases (GHGs) and other forcing agents in 2100. To capture the range of the possible future climate conditions for the present analysis, we used the RCP4.5 scenario, a low-medium scenario of climate change that assumes moderate emissions and the use of a range of technologies and strategies for reducing GHG emissions (Thomson et al. 2011), and the more extreme RCP8.5 scenario, which assumes fossil fuel–intensive energy consumption, with increasing GHG emissions (van Vuuren et al. 2011). The 2050s are generally regarded as the mid-range of climate projection and can potentially be used to capture enough climate change signal while avoiding excessive uncertainties associated with projecting too far into the future (Nolte et al. 2008). We selected the last 3 years of the 2050s (2057–2059) in order to capture signals and heat wave impacts for far enough into the decade.
We used the Weather Research and Forecasting (WRF) model to dynamically downscale the CESM projections. Daily temperature data in 2001–2004, including daily average temperature (Tavg), daily maximum temperature (Tmax), daily minimum temperature (Tmin), and dew point, were generated by WRF on a 4-km × 4-km grid in the study area. A detailed description of the CESM/WRF modeling was reported previously by Gao et al. (2012). We aggregated 251,262 4-km × 4-km grid cells to 1,703 counties to match population projection data and reduce computational demands. We determined the population-weighted centroid for each county and then averaged the data in the nine grid cells closest to the centroid. To reduce the bias of the WRF temperature simulation results, we used the weather station observations collected in the Meteorological Assimilation Data Ingest System (MADIS) (see Supplemental Material, Figure S1) as the reference to calibrate the WRF temperature data. Specifically, we first calculated the difference between the MADIS and WRF data at each station each day, and then excluded the data points beyond the 99th percentile of the daily temperature data in the MADIS stations. For counties with more than one MADIS station, we averaged the MADIS and WRF data and then obtained the ratios of WRF to MADIS data in each county. We interpolated the calibration ratios from 625 counties with MADIS stations to the 1,703-county study area using either a fixed search radius or flexible search radii. For estimates based on a fixed search radius, we derived county-level calibration ratios based on the average of all calibration ratios in a 150-km radius centered on the population-weighted centroid of each county. The 150-km search radius was selected to ensure that there would be at least one calibration ratio in every search radius. For the second method, we identified the five calibration ratios closest to the county centroid and used the average of these ratios as the calibration ratio for each county.
Heat wave definitions. Because there is no universally accepted definition of a heat wave, we used slightly modified versions of four frequently used heat wave definitions (HWDs) (Table 1) to project the frequency and duration (in days) of heat waves from 1 May through 31 September of each year at baseline (2001–2004) and in the future (2057–2059). Specific criteria vary among the definitions, but in brief, the first heat wave definition (HWD_HI) is based on daily low and high heat index values (Robinson 2001), the second (HWD_Tavg) is based on the number of days with a Tavg above the 95th percentile (Anderson and Bell 2011), the third (HWD_Tmax) is based on Tmax values (Meehl and Tebaldi 2004; Peng et al. 2011), and the fourth (HWD_Tmin) is based on the number of days with a Tmin above the 95th percentile.
According to HWD_Tavg, some days with relatively mild temperatures might be counted as heat wave days in counties with a low Tavg during May through September. Therefore, we modified the original definition used by Anderson and Bell (2011) by setting 26.7°C (80°F) as the minimum threshold of Tavg used to define a heat wave. For the same reason, we set 21.3°C (70.8°F) as the Tmin threshold, and 32.7°C (90.9°F) as the Tmax threshold, when defining heat waves based on HWD_Tmin or HWD_Tmax, respectively. These thresholds were selected because the average Tmin and Tmax differ from the average Tavg from 1 May–31 September by 5.4°C and 6°C in our data set, respectively (see Supplemental Material, Figure S2).
Future population projections. We based our estimates of county-level populations for 2057–2059 on state-level projections conducted by the U.S. Census Bureau using the cohort-component method (U.S. Census Bureau 2009), in which the components of population change (births, deaths, and net international migration) were projected from the 2000 base population to the year 2050 for each birth cohort (Preston et al. 2001). To conduct this projection, the Census Bureau used multiple data sources to generate information about fertility, mortality, and migration. In addition, the Census 2009 projection incorporated four net international migration assumptions: a) high migration, b) constant/medium migration, c) low migration, and d) zero migration. For the present analysis, we projected future populations at the county level using the constant ratio method (Shryock et al. 1973). Specifically, for each county, we multiplied the census-projected state population in 2050 by the ratio of the county population to the state population at baseline in 2000. The approach assumes that each county’s share of the state population remains constant over time.
Estimation of heat wave mortality. The expected number of excess deaths attributable to heat waves (EDhw) in each county was calculated using Equation 1 (Peng et al. 2011):
EDhw = N × (RR – 1) × L, 
where N is the expected number of deaths on non–heat wave days in each county, which is equal to the expected daily mortality rate on non–heat wave days multiplied by county population, and RR is the relative risk of death on heat wave days compared with non–heat wave days. RR – 1 is the attributable risk (AR) to heat waves (i.e., the increase in the risk of nonaccidental mortality on heat wave days compared with non–heat wave days), and L is the length of the heat wave in days.
Because nearly 99% of counties had no heat waves in 2001 by our definitions, we used the county-level nonaccidental daily mortality rate in 2001 as the expected daily mortality rate on non–heat wave days during the 2002–2004 baseline period. Similar to Peng et al. (2011), we assumed that the nonaccidental mortality rate on non–heat wave days in 2057–2059 was unchanged from the baseline rate. We used the 95% confidence interval (CI) estimated by Anderson and Bell (2011) for the percentage increase in nonaccidental mortality on heat wave days compared with non–heat waves days during 1987–2005 to define the ranges of possible AR values for counties in the Northeast (1.79–11.98%), the Midwest (3.36–7.93%), and the South (–0.11 to 3.84%). These estimates reflect estimated excess risks of mortality on heat wave days defined using HWD_Tavg (Table 1). Based on the geographic location of each state, the Northeast region includes Connecticut, Maine, Massachusetts, New Hampshire, New Jersey, New York, Pennsylvania, Rhode Island, and Vermont. The Midwest region includes Illinois, Indiana, Iowa, Kansas, Michigan, Minnesota, Missouri, Nebraska, Ohio, and Wisconsin. The South region includes Alabama, Arkansas, Delaware, Florida, Georgia, Kentucky, Louisiana, Maryland, Mississippi, Oklahoma, North Carolina, South Carolina, Tennessee, Texas, Virginia, Washington, DC, and West Virginia. We generated 100 random samples of AR values from uniform distributions based on the ranges for each region using Latin hypercube sampling, a modified Monte Carlo simulation method (Helton and Davis 2003) and randomly selected nine of the sampled sets of values (each of which included three AR values, one for each region—the counties in each region have the same AR values) to use in our final calculations.
Uncertainty and sensitivity analysis. We considered the factors contributing to the uncertainties in projected heat wave health impacts in each analytical step. These factors include the two RCP scenarios (RCP4.5 and RCP8.5), the two methods used to calculate the temperature calibration ratios for each county (fixed search radius and flexible search radii), the four heat wave definitions (Table 1), the four population projections (assuming high, constant/medium, low, or zero net migration), and the nine sets of sampled AR values. In addition, we estimated excess mortality due to heat waves for 1,703 individual counties in each of 3 future years (2057–2059). After calculating the total excess mortality attributable to heat waves considering all the sources of variation mentioned above, we derived probability distributions, mean values, SDs, and 95% CIs for an overall estimate and for subsets of estimates according to different assumptions (e.g., according to RCP scenarios and heat wave definitions).
We used the variance-decomposition method in our sensitivity analysis of the influence of different factors on heat wave mortality estimates because it not only identifies influential factors but also apportions the sources of uncertainty (Chan et al. 1997; Saltelli et al. 2008). For a generic model, y = f(x1, x2,…xn), the total variance of y can be decomposed into the partial variance attributable to each factor (x1, x2,…xn) and their interactions. In our analysis, y is the excess mortality estimate; x1, x2,…xn are n factors related to y; and the total variance was decomposed using the following equations:
V(y) = V(y|x1) + V(y|x1, x2) +…V(y|x1, x2,…xn) 
Si = V(y|xi)/V(y), 
where V(y) is the total variance of y, V(y|x1) is the variance of y attributable to x1, and V(y|x1,x2,…xn) is the variance of y attributable to the interactions of x1, x2,…xn. Si, the first-order sensitivity index for factor i, reflects the main effect of each factor on the estimate of the heat wave mortality. A large value of S for a given factor indicates that the estimate of excess mortality is more sensitive to this factor than factors with a smaller S. We identified factors that have larger influences on the total excess mortality of the whole study area (which are the main sources of uncertainty in the estimation of heat wave mortality).
Characteristics of heat waves. After calibrating the WRF temperature simulations to observed temperatures in MADIS using the calibration method based on a fixed search radius (the distribution of calibration ratios is shown in the Supplemental Material, Figure S3), the estimated Tavg (± SD) over the entire study area during May–September over both RCP scenarios was 22.74°C (± 4.67) during 2002–2004 and 24.75°C (± 4.46) during 2057–2059 (Table 2). Average estimated numbers of heat waves per county per year were 0.38 ± 0.91 during 2002–2004 and 1.88 ± 3.11 during 2057–2059. Temperatures projected for 2057–2059 based on the RCP8.5 scenario were nearly 1°C higher than projections based on the RCP4.5 scenario, resulting in almost twice as many projected heat waves. The projected average duration of heat waves in 2057–2059 based on both RCP scenarios (4.53 ± 3.09 days) is nearly 1 day longer than the estimated average duration in 2002–2004 (Table 2).
When estimated using only one heat wave definition at a time, HWD_HI resulted in the smallest estimated numbers of future heat waves, and HWD_Tmin resulted in the largest numbers (Table 3). HWD_Tmax produced the longest estimate of average heat wave duration (4.88 ± 2.98 days), whereas projections based on the other three heat wave definitions were between 3 and 4 days. Average heat wave durations estimated under the RCP8.5 scenario were almost 1 day longer than under the RCP4.5 scenario, regardless of the heat wave definition used (Table 3).
Projected average values for the duration and frequency of heat waves in 2057–2059 (integrated over the four heat wave definitions) suggest that there will be considerable spatial variability at the county level (Figure 1). In particular, most counties in the northern half of the study region would not experience any heat waves under the RCP4.5 scenario (Figure 1B), whereas most counties along the southern coast would average ≥ 2/year, and Florida counties would average ≥ 4 heat waves/year. Under the RCP8.5 scenario, the number of non–heat wave counties in the Northern region would decrease, and the average frequency of heat waves in most of the counties in the southern states including Alabama, Florida, Georgia, Louisiana, and South Carolina would increase to ≥ 4/year (Figure 1C). Counties in southern Florida have the longest average heat wave durations projected for the study area under both RCP scenarios (Figure 1E,F).
Future heat wave mortality. The estimated average number of heat wave deaths in the eastern United States during 2002–2004 was 187 ± 173 deaths/year, in contrast with 2,379 ± 2,008 deaths/year projected for 2057–2059 (integrated over four population projections, four heat wave definitions, and two RCP scenarios) (Table 2). Projected numbers of deaths differ substantially between the two RCP scenarios, with a mean of 1,403 ± 1,015 deaths/year projected under RCP4.5, compared with 3,556 ± 2,265 deaths/year under RCP8.5. Projections also differ according to the heat wave definition used (Table 4), with almost 2.5 times more deaths projected based on HWD_Tavg and HWD_Tmin than estimated using the other two definitions, for both RCP scenarios. As expected, estimated numbers of heat wave deaths increase as projected populations increase in size due to migration (Table 4).
Our excess mortality estimates have substantial spatial variability (Figure 2). Under the RCP4.5 scenario (Figure 2A,C), the highest county-level excess mortality estimates (> 10 deaths/year) were projected for counties in Florida, New York, and Illinois. Under the RCP8.5 scenario (Figure 2B,D), > 10 deaths/year are projected for a larger number of counties in Florida in addition to some counties along the East Coast (e.g., in Massachusetts, New York, and New Jersey) and a few counties in inland states including Illinois and Michigan. The high numbers of projected deaths in metropolitan areas of Illinois, Massachusetts, Michigan, New Jersey, and New York might be associated with the high population density in these areas (see Supplemental Material, Figure S4).
Uncertainty and sensitivity analysis. Figure 3 shows the probability distributions of annual total excess mortality estimates in the eastern United States for 2057–2059 under RCP4.5, RCP8.5, and the two scenarios combined. All the factors that contribute to the uncertainty in estimated excess deaths were accounted for, including two temperature calibration methods, four heat wave definitions, four population projections, three model years, and nine sets of AR values. Under the RCP4.5 scenario, the estimated number of deaths is 1,403 deaths/year (95% CI: 137, 3,788). The distribution curve under this scenario peaks at around 500 deaths/year, then drops rapidly. The cumulative probabilities of < 1,000 excess deaths/year and < 2,000 excess deaths/year are 43% and 76%, respectively; we saw no probability of > 5,000 excess deaths/year. In contrast, the probability distribution of estimated excess deaths under RCP8.5 is relatively flat, with a cumulative probability of 42% for having 1,000–3,000 excess deaths/year, and 15% for having 5,000–7,000 excess deaths/year, and a very small probability for having > 10,000 excess deaths/year. When estimates are integrated over both RCP scenarios, the probabilities of different excess mortality estimates fall between those of the scenario-specific estimates.
Using the variance-decomposition method, we attributed 23.7% of the uncertainty to the two RCP scenarios, 22.2% to the four heat wave definitions, and 32.2% to the different values for the relative risk of mortality on heat wave days compared with non–heat wave days [including nine randomly sampled sets of three area-specific ARs based on previously published estimates (Anderson and Bell 2011)]. In contrast, the two methods used for the WRF data calibration, the four migration scenarios used in the population projections, and the interannual variability of temperature projections during 2057–2059 were not major sources of uncertainty, as indicated by their low Si values (Figure 4).
We estimated that heat waves will be 3.5–6.4 times more frequent in 2057–2059 than in 2002–2004 and that excess mortality attributable to heat waves would be 7.5–19.0 times higher. The major sources of uncertainty in our heat wave mortality projections were the RCP scenarios, the ARs of mortality on heat wave days compared with non–heat wave days, and the criteria used to define heat waves.
In contrast with previous studies that only focused on one or a few cities (Peng et al. 2011; Sheridan et al. 2012), we estimated the impacts of future heat waves over a wide geographic area. Our estimates suggest that there will be high spatial variability in future heat wave mortality and that estimates of climate change health impacts based on a single geographic area will have limited value for estimating health impacts in other areas. In addition, we performed a comprehensive examination of six factors that may contribute to uncertainty in heat wave mortality projections, whereas previous studies explored a relatively limited set of factors [e.g., GHG emission scenarios (Peng et al. 2011)]. Furthermore, we used recently developed RCPs (Inman 2011; Moss et al. 2010) for temperature projections at a high spatial resolution, whereas most previous studies (Kolstad and Johansson 2011; Peng et al. 2011) were based on older emission scenarios described in the IPCC Special Report on Emissions Scenarios (IPCC 2000).
We estimated that there would be an average of 1.88 (95% CI: 0, 11) heat wave episodes per year per county in 2057–2059. The projected geographic distribution of heat waves has considerable spatial variability, with 35.7% of counties expected not to experience any heat waves, whereas 10.4% of counties would experience > 4 heat waves/year under the RCP4.5 scenario, and corresponding estimates of 11.6% and 26.5% under the RCP8.5 scenario, respectively. Heat waves would be expected to occur most often in the southern coastal states, including Florida, Georgia, and Louisiana, with Florida counties having the highest numbers of deaths attributable to heat waves. In addition, our projections suggest that despite relatively low frequencies of heat waves, heat wave mortality will be high in densely populated counties located in several northeastern coastal states (e.g., Massachusetts, New Jersey, and New York).
Increases in future temperatures will depend largely on GHG emissions. Therefore, GHG emission scenarios may have a substantial influence on estimates of the frequency and duration of future heat waves. We estimated future heat waves under two scenarios representing moderate and high GHG emissions. Under the high-emission RCP8.5 scenario, excess mortality was estimated to be almost 2.5 times higher than that estimated under the moderate RCP4.5 scenario, suggesting that curtailing GHG emission will have a great impact on the reduction of heat wave mortality in the future.
Our findings also indicate that heat wave definitions have a strong influence on heat wave mortality projections, with the fewest days per year being classified as heat wave days when the HDW_HI definition was used, and the largest numbers of heat wave days when heat waves were defined using HDW_Tavg or HDW_Tmin. Our results are consistent with recent studies that reported substantial inconsistencies among heat wave mortality estimates when using different heat wave definitions (Hajat et al. 2010; Zhang et al. 2012).
Estimates of the relative risk of mortality on heat wave days compared with non–heat wave days have varied among previous studies and may at least partly reflect regional differences in susceptibility to adverse effects of heat at the population level as well as individual-level differences in susceptibility according to race, age, occupation, or other factors (O’Neill et al. 2005). Currently, there is little information about regional variation in the relative risk of heat wave mortality; therefore, we used a Monte Carlo simulation to sample AR from values previously reported by Anderson and Bell (2011) for different regions of the United States. Although this allowed us to estimate excess mortality based on an appropriately wide range of excess relative risk estimates, it also contributed substantial uncertainty to our estimates. In addition, we considered AR estimates reported by Bobb et al. (2011) for heat waves defined based on a Tmax, in contrast with estimates reported by Anderson and Bell (2011), who defined heat waves based on a Tavg. In general, AR values estimated by the two groups were similar except for the Midwest region, where the estimates reported by Anderson and Bell (2011) were slightly higher. We sampled the values of excess relative risks for the three regions of our study area from values spanning the 95% CIs of corresponding ARs reported by Anderson and Bell (2011) because their estimates had wider ranges, thus representing more conservative uncertainty estimates in the calculated excess deaths due to heat waves.
Our study has several limitations. Our estimates of heat wave impacts on mortality are primarily based on temperatures in urban areas, where the majority of eastern U.S. residents live. However, heat stress responses may differ between urban and rural populations (Fischer et al. 2012). Urban temperatures are generally higher than temperatures in surrounding rural areas, especially at night, because of the urban heat island effect. Therefore, the relative risk of heat-related mortality may be much higher in urban areas than in surrounding rural areas (Clarke 1972). If lower impacts of heat waves on rural populations had been accounted for in our analysis, our estimates of annual mortality due to heat waves would have been slightly smaller.
Our estimates did not include heat-related deaths on hot days that were not identified as heat wave days according to our heat wave definitions. In addition, our estimates did not account for higher temperatures during future heat waves, which will be hotter than those during heat waves in 2002–2004, even under the RCP4.5 scenario (Table 2). To better account for the temperature effect, a national-scale epidemiological study is needed to provide region-specific, parametric exposure-response functions between temperature and mortality.
We also did not consider effects of human adaptation or heat mitigation measures on future heat wave mortality. Similar to Peng et al. (2011), we assumed that excess mortality from future heat waves will be the same as heat wave mortality at baseline. However, if mitigation measures to prevent heat-related mortality are adopted as heat waves become more frequent, excess mortality would decrease, and our projections would overestimate future heat-related mortality in some areas. Heat warning systems and air conditioning have been reported to reduce heat wave impacts (Anderson and Bell 2009; Fouillet et al. 2008; O’Neill et al. 2009). Other measures such as planting trees can also reduce temperatures, thus reducing heat-related mortality (Akbari 2002). Finally, our population projections did not consider demographic changes (e.g., changes according to race/ethnicity, sex, and age) that might have considerable impacts on heat wave mortality (Hajat and Kosatky 2010; O’Neill et al. 2005).
Our results suggest that numbers of heat wave–related deaths are likely to be an order of magnitude higher in 2057–2059 than in 2002–2004. Under the fossil-fuel–intensive RCP8.5 scenario, the probability of thousands of heat wave–related deaths per year in the eastern United States is much higher than under the RCP4.5 scenario. Effective mitigation and adaptation measures will be crucial to reduce the potential for catastrophic outcomes, particularly in the most vulnerable geographic regions. In addition, we found that heat wave definitions, GHG emission scenarios, and estimates of the relative risk of mortality on heat wave days compared with non–heat wave days account for a large proportion of the total variation in projected mortality estimates and are major sources of uncertainty.
Anderson GB, Bell ML. 2011. Heat waves in the United States: mortality risk during heat waves and effect modification by heat wave characteristics in 43 U.S. communities. Environ Health Perspect 119:210–218; doi: 10.1289/ehp.1002313.
Chan K, Saltelli A, Tarantola S. 1997. Sensitivity analysis of model output: variance-based methods make the difference. In: Proceedings of the 1997 Winter Simulation Conference, Atlanta, GA, 7–10 December 1997 (Andradóttir S, Healy KJ, Withers DH, Nelson BL, eds). New York:Association for Computing Machinery, 261–268.
Davis RE, Knappenberger PC, Michaels PJ, Novicoff WM. 2003. Changing heat-related mortality in the United States. Environ Health Perspect 111:1712–1718; doi: 10.1289/ehp.6336.
Fischer EM, Oleson KW, Lawrence DM. 2012. Contrasting urban and rural heat stress responses to climate change. Geophys Res Lett 39:L03705; doi: 10.1029/2011GL050576.
Fouillet A, Rey G, Wagner V, Laaidi K, Empereur-Bissonnet P, Le Tertre A, et al. 2008. Has the impact of heat waves on mortality changed in France since the European heat wave of summer 2003? A study of the 2006 heat wave. Int J Epidemiol 37:309–317.
Gao Y, Fu JS, Drake JB, Liu Y, Lamarque JF. 2012. Projected changes of extreme weather events in the eastern United States based on a high resolution climate modeling system. Environ Res Lett 7:044025; doi: 10.1088/1748-9326/7/4/044025.
Hajat S, Sheridan SC, Allen MJ, Pascal M, Laaidi K, Yagouti A, et al. 2010. Heat-health warning systems: a comparison of the predictive capacity of different approaches to identifying dangerously hot days. Am J Public Health 100:1137–1144.
IPCC (Intergovernmental Panel on Climate Change). 2000. IPCC Special Report on Emissions Scenarios. 2000. Available: http://www.ipcc.ch/ipccreports/sres/emission/index.php?idp=0 [accessed 14 November 2013].
IPCC (Intergovernmental Panel on Climate Change). 2007. Summary for Policymakers. In: Climate Change 2007: The Physical Science Basis. Contribution of Working Group I to the Fourth Assessment Report of the Intergovernmental Panel on Climate Change. Cambridge, UK:Cambridge University Press. Available: http://www.ipcc.ch/publications_and_data/publications_ipcc_fourth_assessment_report_wg1_report_the_physical_science_basis.htm [accessed 14 November 2013].
Kolstad EW, Johansson KA. 2011. Uncertainties associated with quantifying climate change impacts on human health: a case study for diarrhea. Environ Health Perspect 119:299–305; doi: 10.1289/ehp.1002060.
Nolte CG, Gilliland AB, Hogrefe C, Mickley LJ. 2008. Linking global to regional models to assess future climate impacts on surface ozone levels in the United States. J Geophys Res-Atmos 113:D14307; doi: 10.1029/2007JD008497.
Peng RD, Bobb JF, Tebaldi C, McDaniel L, Bell ML, Dominici F. 2011. Toward a quantitative estimate of future heat wave mortality under global climate change. Environ Health Perspect 119:701–706; doi: 10.1289/ehp.1002430.
U.S. Census Bureau. 2009. United States Population Projections by Age, Sex, Race and Hispanic Origin: July 1, 2000–2050. Available: http://www.census.gov/population/projections/files/methodstatement.pdf [accessed 14 November 2013].
Zhang K, Rood RB, Michailidis G, Oswald EM, Schwartz JD, Zanobetti A, et al. 2012. Comparing exposure metrics for classifying ‘dangerous heat’ in heat wave and health warning systems. Environ Int 46:23–29.
New Search FunctionWe're pleased to present our improved search page. Try it, and let us know what you think!
CEHN September 2014 Article of the Month“Prenatal Polybrominated Diphenyl Ether Exposures and Neurodevelopment in U.S. Children through 5 Years of Age: The HOME Study” (Environ Health Perspect; DOI:10.1289/ehp.1307562) has been selected by the Children’s Environmental Health Network (CEHN) as its September 2014 Article of the Month. These CEHN summaries discuss the potential policy implications of current children’s environmental health research.
Register Today for PPTOX IVEnvironmental Stressors in Disease and Implications for Human Health
October 26–29, 2014
Boston Marriott Long Wharf Hotel
Join the Endocrine Society for the fourth international summit of Prenatal Programming and Toxicity (PPTOX), a premiere conference series dedicated to cutting-edge discussion of environmental hazards during early life and long-term consequences.* Housing deadline: Monday, October 6
For more information, visit the Endocrine Society website.
Sign Up to Receive E-mail Alerts
Recent Advance Publications
- Asthma in Inner-City Children at 5-11 Years of Age and Prenatal Exposure to Phthalates: The Columbia Center for Children’s Environmental Health Cohort
- Comparative Assessment of the Effects of Climate Change on Heat- and Cold-Related Mortality in the United Kingdom and Australia
- Proximity to Natural Gas Wells and Reported Health Status: Results of a Household Survey in Washington County, Pennsylvania
- Green and Blue Spaces and Behavioral Development in Barcelona Schoolchildren: The BREATHE Project
- Aerial Application of Mancozeb and Urinary Ethylene Thiourea (ETU) Concentrations among Pregnant Women in Costa Rica: The Infants’ Environmental Health Study (ISA)
- Pyrethroid Pesticide Exposure and Parental Report of Learning Disability and Attention Deficit/Hyperactivity Disorder in U.S. Children: NHANES 1999–2002
- Household Cooking with Solid Fuels Contributes to Ambient PM2.5 Air Pollution and the Burden of Disease
- AdvPubl: Prenatal phthalates and child asthma http://t.co/SDGhtmwyO5
- CareerOpp: Postdoc research assoc, Institute for the Study of Env and Society, Brown Univ, Providence, RI http://t.co/xJPAL0YMBw
- EHPNoonNews: Indoor solid fuel use: the deadliest environmental problem today? http://t.co/4POfkTy3M7 @voxdotcom
- EHPNoonNews: Hog farm workers take resistant bacteria home http://t.co/lWDRULLHSZ @nytimes
- EHPNoonNews: China to end high ash or sulfur coal imports http://t.co/mVS1V4WsVf @cnbc