Skip to main content

Author: Julia Shipman

Weathering the Impact: ENSO-Driven Disasters, Power Disruption, and Health Outcomes in Medicare Populations

Weathering the Impact: ENSO-Driven Disasters, Power Disruption, and Health Outcomes in Medicare Populations

 

Investigators:

Sara Curran, Jeff Stanaway, Luanne Thompson, June Yang, Emmanuela Gakidou

Data sources:

ENSO indices from the National Oceanic and Atmospheric Administration Climate Prediction Center from 1980-2025.

SHELDUS: Special hazard events and losses database for the United States 1970 – 2023. Available by County and day.

Center for Medicare & Medicaid Services claim and beneficiary data from 1990-2023. Available by County and day.

HHS emPOWER: Count of medicare beneficiaries who rely on electricity-dependent durable medical and assistive equipment and devices from 2016-2025. Available by County and month.

DOE-417 archive data: Electric Emergency Incident and Disturbance Report from 2000 to 2023. Available by County and Day.

Spatial Coverage: United States

Temporal Coverage: 2016 – 2023.

Measures:

  • Climate Measurements:

    • ENSO Indices (NOAA): Seasonal measurements of sea surface temperature anomalies used to classify El Niño and La Niña events.
    • SHELDUS: Provides detailed records of natural disaster events (including type, date, and location), allowing alignment of local disasters with ENSO periods. It also includes loss data (e.g., property damage, crop loss, injuries) to quantify event severity.

    Power Infrastructure Measurements:

    • HHS emPOWER Dataset: Monthly, county-level counts of Medicare beneficiaries who rely on electricity-dependent durable medical equipment (DME), indicating vulnerability to power disruptions.
    • DOE OE-417 Archive: Incident-level reports on electrical disturbances, including type of event, date/time, geographic area, and population affected.

    Health Outcomes:

    • CMS Claims and Quality Measures: Data on Medicare beneficiaries covering:
      • Hospital readmission rates
      • Emergency department (ED) and inpatient utilization
      • Home health services
      • Minimum Data Set (MDS) indicators from nursing homes
      • Preventable hospitalizations (e.g., ambulatory care-sensitive conditions)

    Demographic and Socioeconomic Context:

    • County-Level Medicare Population Characteristics: Including race/ethnicity, age, sex, and dual eligibility for Medicare and Medicaid, enabling analysis of differential impacts across vulnerable groups.

Project Summary:

Disruptions driven by the El Niño-Southern Oscillation (ENSO), such as flooding, drought, and extreme temperatures, have long been implicated in public health threats across the United States. For example, during negative phases of ENSO (La Nina events) there is typically an increase in the number of hurricanes that can result in major floods. This also occurs during El Nino events in the Southwest US.  Major floods have been shown to elevate hospitalization rates among older adults for skin conditions, neurological illnesses, musculoskeletal disorders, and injuries in the weeks following exposure (Aggarwal et al. 2025). In addition, other impacts include health care disruptions due to displacement from homes and communities or through damage to health infrastructure. These might be particularly important for those requiring frequent care for chronic illnesses.

However,  mechanisms linking ENSO-related disasters with health outcomes remains poorly understood. For instance, the role of power infrastructure failure, such as prolonged outages disrupting electricity-dependent medical care is a plausible pathway for detrimental impacts on healthcare particularly for the elderly who are less mobile than the general population..

Our U.S.-based project investigates how ENSO-related disasters influence health outcomes among older adults, focusing especially on power disruptions as a critical explanatory pathway. By aligning the data sources mentioned above, we aim to trace if and how power outages amplify the health impact of ENSO-driven disasters on older adults.

We will employ a combination of panel regression models, Difference-in-Difference analysis, and causal mediation analysis to estimate the direct and indirect effects of ENSO-driven disasters, to quantify the role of infrastructure failure and identify populations at higher risk.

Comments

Papers on impacts of El Nino in the U.S. 

Outputs:

Peer-reviewed publications, grant proposals, conference presentations

References:

Aggarwal, Sarika, Jie K. Hu, Jonathan A. Sullivan, Robbie M. Parks, and Rachel C. Nethery. 2025. “Severe Flooding and Cause-Specific Hospitalisation among Older Adults in the USA: A Retrospective Matched Cohort Analysis.” The Lancet Planetary Health 9(7):101268. doi:10.1016/S2542-5196(25)00132-9.

Fussell, Elizabeth, Sara R. Curran, Matthew D. Dunbar, Michael A. Babb, Luanne Thompson, and Jacqueline Meijer-Irons. 2017. “Weather-Related Hazards and Population Change: A Study of Hurricanes and Tropical Storms in the United States, 1980–2012.” The ANNALS of the American Academy of Political and Social Science 669(1):146–67. doi:10.1177/0002716216682942.

Salas, Renee N., Laura G. Burke, Jessica Phelan, Gregory A. Wellenius, E. John Orav, and Ashish K. Jha. 2024. “Impact of Extreme Weather Events on Healthcare Utilization and Mortality in the United States.” Nature Medicine 30(4):1118–26. doi:10.1038/s41591-024-02833-x.

Continue reading

What Am I Reading: Disasters and Aging in Place

What am I reading? Disasters and Aging in Place

Link to article

If you’re interested in contributing a short What Am I Reading post, we’d love to hear from you! Email us at cache@colorado.edu

Written by Jenna Tipaldo, CUNY School of Public Health and CUNY Institute for Demographic Research, jenna.tipaldo09@sphmail.cuny.edu

A new report from Winkler & Mockrin (2025) entitled “Aging and wildfire risk to communities” explores the exposure of older populations to wildfires. A main findings is that “Nearly all (87 percent) of the population growth in higher wildfire risk locations between 2010 and 2020 was among people over the age of 60, many of whom had been living in higher risk places for years and are growing older (i.e., aging in place).” Each is relevant when thinking about older adults and exposure, vulnerability, and resilience to disasters.  Wildfires are just one of type of disaster to consider: recent evidence also suggests that coastal zones – areas at risk of storms and other seaward hazards such as flooding and tsunamis – are also aging faster than areas farther inland (Bukvic et al., 2018; Hauer et al., 2020; Tagtachian and Balk, 2023). 

No relocation: Forsyth & Molinsky (2020) note that to some, aging in place signifies remaining in their home while to others it may mean moving but within the same community, such as downsizing. Based on recent shifts in age distribution in Census blocks with “moderate-to-high” wildfire risk, Winkler & Mockrin (2025) conclude that the increase in older adult populations in fire-prone regions is likely attributable to populations aging in place rather than in-migration (Figure 4). They also note important spatial variation and also uncertainty about the relative contributions of migration and death. They also note that aging in place seems to be the “primary mechanism” in higher risk rural areas (Winkler & Mockrin, 2025). 

Source: Winkler & Mockrin (2025)

Health and Health Care : Winkler & Mockrin (2025) summarize the various ways in which older adults can be at higher risk due to wildfires including 1) physical limitations that are barriers to preparation or response, 2) factors like social isolation which can impact access to information and resources, and 3) higher rates of chronic diseases which are risk factors for adverse health outcomes due to fires and smoke. Furthermore, disasters can be disruptive to healthcare, not only by damaging facilities and displacing people from their homes but also by disrupting care which relies on movement. Examples include when patients are unable to travel to hospitals or medical providers, or if healthcare workers can‘t get to a patient’s home due to inaccessible roads (Tarabochia‐Gast et al., 2022) or suspended public transit systems. Rural areas face additional challenges with longer travel times for healthcare access, especially with high levels of hospital closures (Miler et al., 2020; McCarthy et al., 2021). Such patterns negatively impact health care access, emergency medical response, and transport times (GAO, 2021; Kaufman et al., 2016). On average, rural residents must travel about 20 miles farther for typical health care services – in non-disaster times (GAO 2021). While those miles may seem trivial, in emergencies they can mean loss of access to care and treatment. 

Personal choice: Aging in place can be a personal choice in support of maintaining one’s agency and independence by staying in one’s own home and community (Forsyth & Molinsky, 2020). Even so, staying in one’s home can also result from lack of choice due to limited resources and/or few desirable and affordable options. Modifications are expensive too. Even older adults who are relatively better off can struggle to pay for downsizing or modifying a new dwelling for care needs (Forsyth & Molinsky, 2020).  

From research to policy 

To help support healthy aging in place, Winkler & Mockrin (2025) suggest that existing programs that support older adults could be expanded to include wildfire risk reduction. An example is the USDA’s Section 504 Home Repair program which supports older low-income homeowners. In addition, organizations such as the AARP provide useful material for aging in place such as a checklist for people who are prepping their home. Such resources should be expanded to include disaster risk as a consideration.  

 

References:  

  • Bukvic, A., Gohlke, J., Borate, A., and Suggs, J. 2018. “Aging in Flood-Prone Coastal Areas: Discerning the Health and Well-Being Risk for Older Residents.” International Journal of Environmental Research and Public Health 15(12):2900. https://doi.org/10.3390/ijerph15122900.   
  • Hauer, Mathew E., Elizabeth Fussell, Valerie Mueller, Maxine Burkett, Maia Call, Kali Abel, Robert McLeman, and David Wrathall. 2020. “Sea-Level Rise and Human Migration.” Nature Reviews Earth & Environment 1(1):28–39. https://doi.org/10.1038/s43017-019-0002-9 
  • Kaufman, B.G., Thomas, S.R., Randolph, R.K., et al. The rising rate of rural hospital closures. The Journal of Rural Health. 2016;32(1):35-43. https://doi.org/10.1111/jrh.12128  
  • McCarthy, S., Moore, D., Smedley, W. A., Crowley, B. M., Stephens, S. W., Griffin, R. L., Tanner, L. C., & Jansen, J. O. (2021). Impact of Rural Hospital Closures on Health-Care Access. Journal of Surgical Research, 258, 170–178. https://doi.org/10.1016/j.jss.2020.08.055 
  • Miller, K.E.M., James, H.J., Holmes, G.M., Van Houtven, C.H. The effect of rural hospital closures on emergency medical service response and transport times. Health Serv Res. 2020;55(2):288-300. https://doi.org/10.1111/1475-6773.13254  
  • Tagtachian, D. and Balk, D., 2023. Uneven vulnerability: characterizing population composition and change in the low elevation coastal zone in the United States with a climate justice lens, 1990–2020. Frontiers in Environmental Science, 11, p.1111856. 
  • Tarabochia‐Gast, A. T., Michanowicz, D. R., & Bernstein, A. S. (2022). Flood Risk to Hospitals on the United States Atlantic and Gulf Coasts From Hurricanes and Sea Level Rise. GeoHealth, 6(10), e2022GH000651. https://doi.org/10.1029/2022GH000651 
  • Winkler, R. L., & Mockrin, M. H. (2025). Aging and wildfire risk to communities (Report No. EIB-284). U.S. Department of Agriculture, Economic Research Service. https://doi.org/10.32747/2025.9015828.ers 

 

Continue reading

Severe Heat Days using the Universal Thermal Comfort Index

Severe Heat Days using the Universal Thermal Comfort Index

Link to code

Click here

Date: September 2025


Authors/Creators/ Team Members: Marcial Yangali (marcialy@colmex.mx)

Reviewers: Landy Sánchez and Emerson Baptista

Specific purpose of code: It demonstrates how to construct severe heat measures using the UTCI data (ERA5-HEAT ). It starts by showing data manipulation from raster (grid data) to a tabular dataset that obtains UTCI values for each municipality in Mexico. Then, it presents how to map and analyze such data. Finally, it shows how to count the number of days of severe heat (32°C UTCI and above). This script is part of the demonstration CACHE project “Heat, Disability in older adults and Care” from El Colegio de Mexico.

General Application: This develops familiarity with heat data and fundamental skills to construct an environmental dataset that can be easily integrate with demographic information.

How does or could this code allow researchers to assess research questions related  to aging or life course?: This code help to analyze exposure to severe heat days by age structure at a subnational level. Particularly, to understand how aging realtes to higher exposure to extreme weather. Historical UTCI measures could be employ to assess cumulative heat impacts across the life course.

Data sets used: 

  • Two publicy available datasets are used:

    • Universal Thermal Climate Index (UTCI). Copernicous ERA5-HEAT
    • 2020 Mexican Municipalities and States boundaries. INEGI (Census Bureau office)

Coding Language:  R 

Tools and Packages used: R packages for data manipulation (mainly dplyr but also janitor, stringr, tidyr and forcats), visualization (ggplot2, patchwork), and geospatial operations (sf).

Output(s): Analysis results, maps and graphs

Spatial extent:Mexico (33.0°N (North), -118.5°E (East), 14.0°N (South), and -86.0°E (West)

Temporal extent: May 2019

Key words: heat, severe weather, thermal index, Mexico

Continue reading

Aging and disability in the Mexican Population

Aging and disability in the Mexican Population

Link to code

Click here

Date: September 2025


Authors/Creators/ Team Members: Marcial Yangali (marcialy@colmex.mx) and Mariana Ramos

Reviewers: Emerson Baptista and Landy Sánchez

Specific purpose of code: To show how to construct disability measures using the international recommendation of the Washington Group. It also demonstrates how to evaluate age and sex composition of the population with disability and their territorial distribution.

General Application: This demonstrates basic manipulation of demographic data with R, particularly useful for those with limited familiarity with population measures.

How does or could this code allow researchers to assess research questions related  to aging or life course?: This code examines age structure in census data. Specifically, explores how the prevalence of disability condition increases with age.

Data sets used: 

  • All are publicy available datasets:

    • 2020 Mexican Housing and Population Data (IPUMS International)

Coding Language:  R 

Tools and Packages used: R packages for data manipulation (mainly dplyr but also stringr, ipumsr, tidyr, srvyr, gtsummary, purr, and labelled), visualization (ggplot2, patchwork, geofacet, scales and plotly), and geospatial operations (sf, biscale, ggtern).

Output(s): Analysis results, maps and graphs

Spatial extent: Mexico (33.0°N (North), -118.5°E (East), 14.0°N (South), and -86.0°E (West)

Temporal extent: 2022

Key words: disability, Mexico, age structure, sex composition, aging

Continue reading

Joining ACAG Annual Estimates of PM2.5 with Social Determinants of Health (SDOH) data

Joining ACAG Annual Estimates of PM2.5 with Social Determinants of Health (SDOH) data

Link to code

Click here

Date: July 2025


Authors/Creators/Team Members: Zoé Haskell-Craig and Priyanka deSouza

Specific purpose of code: This code aggregates gridded annual average PM2.5 concentration estimates produced by the Atmospheric Composition Analysis Group (ACAG) to the census tract level, producing a variable containing the average PM2.5 exposure for each tract. This is then combined with socioeconomic and demographic data available at the tract level from the social determinants of health (SDOH) database produced by the Agency for Healthcare Research and Quality (AHRQ).

General Application: This code takes advantage of the `tigris` package to aggregate high resolution (fine spatial scale) modelled estimates of PM2.5 pollution to the administrative boundaries at which demographic and SDOH data are available. As an example, here we demonstrate computing the annual average PM2.5 concentrations in 2020 for census tracts and combining this with SDOH data on race/ethnicity and income. With minor changes, this code can be used for other years and temporal resolutions (i.e. monthly estimates of PM2.5) and for other administrative units (ZCTAs, blockgroups, counties, etc).

How does or could this code allow researchers to assess research questions related to aging or life course?: While the dataset output from this code does not contain variables on age, the raw SDOH dataset contains census information on age which could be included with minor edits to the code. Also, the aggregation of PM2.5 exposure to the census tract (or other administrative units) allows researchers to combine this exposure with other information available from the census, such as income by age breakdowns.

Data sets used: 

Are all the data publicly available or are some restricted-access? Publicly available 

Coding Language:  R 

Tools and Packages used: tidyverse, readxl, sf, raster, ncdf4, exactextractr, tigris, viridis

Output(s): Dataset with census tracts as unit of analysis and a map of the average PM2.5 per census tract in 2020. 

Spatial extent: Continental US

Temporal extent: Single-year, 2020 (code can be modified to produce data for any year from 1998 – 2023, or monthly for any month in that period). 

Additional Comments: Journal article using this code is forthcoming. 

Published papers that use this code: Zoé Haskell-Craig, Kevin P. Josey, Patrick L. Kinney, and Priyanka deSouza. (2025). Equity in the Distribution of Regulatory PM2.5 Monitors. Environmental Science & Technology. DOI: 10.1021/acs.est.4c12915

Continue reading

What am I Reading? Disentangling the Impacts of Extreme Heat on Biological Aging: Measuring the Hidden Toll on Our Body

What am I reading? Disentangling the Impacts of Extreme Heat on Biological Aging: Measuring the Hidden Toll on Our Body

Link to article

If you’re interested in contributing a short What Am I Reading post, we’d love to hear from you! Email us at cache@colorado.edu.

Written by Eun Young Choi, Postdoctoral Associate, University of Southern California

High temperatures are heating not only our neighborhoods and homes, but also our very biology, as we suggested in a recent study (Choi & Ailshire, 2025). Among the many ways extreme heat threatens public health, its subtle yet significant impact on the body’s aging processes has begun to draw attention. I’ve been exploring how we can quantify the biological consequences of extreme heat, and why these hidden impacts matter for aging research.

Why Focus on Biological Aging?

Much of the climate-health literature has understandably focused on observable health outcomes: hospitalizations, respiratory and cardiovascular diseases, and death (Bunker et al., 2016; Hajat et al., 2010). These are essential indicators, but the effects of extreme heat might not immediately manifest as diagnosable conditions; instead, they may exert a silent toll at the cellular and molecular level. Over time, this biological strain can accumulate, increasing the risk of disability and disease. Biological age, measured using biomarkers that reflect physiological wear and tear, offers a promising way to identify early signs of changes in the body before chronic conditions are formally diagnosed. These include measures based on clinical biomarkers, cellular markers, and, more recently, molecular signatures such as DNA methylation (Chen et al., 2023 for review). Each of these tools provides a useful lens into how the aging process may advance more rapidly than expected based on chronological age, and how it may be shaped by external stressors like heat. Recent studies show that accelerated biological aging is associated with elevated risk of cardiovascular disease, cognitive decline, and mortality (Emami et al., 2022; Fransquet et al., 2019; Zhou et al., 2022). As such, these clocks provide a useful intermediate endpoint that can be particularly valuable when studying environmental exposures, which often unfold gradually and exert diffuse effects across multiple body systems. In this context, biological age can help us understand not just whether heat is harmful, but how it does its damage.

How Do We Measure Heat?

Measuring exposure to extreme heat may appear straightforward, but it involves multiple layers of complexity. The most common metric is ambient temperature (technically, the temperature in the surrounding environment), but even this can be defined in various ways—daily maximums, minimums, or averages—and it usually refers to outdoor air temperature. Others use composite indices that better approximate heat stress on the human body. The Heat Index, for example, incorporates humidity and is used to estimate heat-related stress in shaded environments (National Weather Service). The Wet-Bulb Globe Temperature (WBGT) goes further by accounting for wind speed, cloud cover, and sun angle as well to reflect conditions in direct sunlight, making it especially relevant for outdoor or occupational settings. Each of these measures captures different aspects of thermal stress, and the choice of metric should align with the study’s research question and target population. In our study, we used the Heat Index because our sample consisted of older adults, who are generally less likely to work outdoors or spend extended time in full sun. While these metrics can technically be measured indoors, they are typically based on outdoor weather data and do not directly reflect indoor conditions.

How Can We Conceptualize Outdoor Heat Exposure to Better Estimate Health Impacts?

Researchers have considered a variety of factors to understand the magnitude of heat-related health effects. Here, I created a conceptual cube with three axes to synthesize commonly used dimensions: exposure timing, heat intensity, and exposure context. This framework is not a modeling tool, but rather a way to clarify how different features of outdoor heat exposure interact to shape physiological burden.

  • Y-axis: What timeframe is captured?

Exposure can occur over various timeframes: a single hot day, a multi-day heatwave, or repeated seasonal exposures over years. Short-term heat events can trigger immediate physiological stress responses (e.g., inflammation), while longer-term exposure to elevated temperatures may produce cumulative biological wear and tear. Studies use various time windows to model these effects, from several day lags to multi-year averages, depending on the health outcome of interest. While short-term physiological responses to heat stress may be transient, some effects may accumulate over time and this continuous exposure may leave biological imprints detectable by biomarker-based measures. For example, our findings show consistent associations between longer-term heat exposure (e.g., 1-year and 6-year cumulative heat days) and accelerated epigenetic aging, consistent with prior studies reporting robust associations and large effect sizes for longer-term heat exposure (Chiu et al., 2024; Ni et al., 2023).

  • Z-axis. How severe is the exposure?

This axis represents the intensity of the heat experienced. Researchers use both relative and absolute metrics to define extreme heat. Relative measures, such as temperatures above the 95th percentile of the local historical distribution, are useful for identifying deviations from the norm, especially considering that long-term sublethal heat can lead to physiological adaptations and increased thermal tolerance (Carr et al., 2024; Périard et al., 2016). In contrast, absolute thresholds (e.g., >95°F or >35°C) provide a fixed reference point that can be useful for identifying biologically hazardous temperatures and facilitating comparisons across regions. For the Heat Index, for example, the National Weather Service offers a practical classification: 80°F (Caution), 90°F (Extreme Caution), and 103°F (Danger). The choice between relative and absolute measures should be guided by the study’s objective, the population’s vulnerability, and the geographic and climatic context.

  • X-axis. How is exposure experienced?

This axis reflects the context: the individual or situational factors that influence how ambient heat translates into actual personal exposure. Most studies use outdoor temperature data from weather stations or modeled products, and these measures may not fully capture personal exposure – a challenge also seen in air pollution research, where ambient data often serve as proxies for individual exposure (see related discussion). It is therefore important to interpret such data as approximating the potential for exposure rather than direct experience. Key contextual modifiers include time spent outdoors, occupational exposure, housing quality, and access to cooling resources. For instance, older adults living in poorly insulated homes without air conditioning may experience disproportionately high indoor heat, despite similar ambient temperatures. Recent work has also highlighted substantial within-neighborhood variation in heat exposure, reinforcing the need to consider behavioral and environmental mediators when interpreting ambient heat metrics (Li et al., 2023; Reid et al., 2009).

The color gradient in the figure reflects increasing physiological burden, illustrating how these dimensions can intersect to magnify biological stress. For instance, someone who works outdoors (high context), over many years (longer timing), and in areas where temperatures regularly exceed 100°F (high intensity), may experience substantially greater heat-related aging than someone briefly exposed to moderate heat while indoors.

What We Found about Heat and Epigenetic Aging

There is growing evidence from animal studies that heat stress can trigger epigenetic alterations such as DNA methylation, positioning these molecular changes as a plausible biological mechanism linking environmental exposures to long-term health outcomes (Murray et al., 2022). Epigenetic clocks—biological age estimates derived from DNA methylation levels across the genome—can capture cumulative physiological responses to stress and toxins. In our work, we’ve begun to apply these epigenetic measures to understand how outdoor heat exposure may accelerate epigenetic aging. Our findings show that outdoor heat, especially long-term, was significantly associated with greater acceleration in epigenetic age in a diverse national cohort of older adults. These associations persisted even after adjusting for individual-level socioeconomic and behavioral factors, as well as community-level characteristics. Taken together, these findings suggest that chronic heat exposure may not only increase immediate health risks but also disrupt key systems contributing to a steeper trajectory of epigenetic aging, potentially through pathways involving oxidative stress, inflammation, and metabolic reprogramming (Murray et al., 2022). Nonetheless, further evidence is needed to clarify the specific mechanisms linking heat exposure to epigenetic aging acceleration.

Moving Forward

Advancing this research requires embracing the complexity of both exposures and outcomes. On the exposure side, we must better account for co-occurring environmental stressors. Heat rarely acts alone. For instance, air pollution tends to worsen on hot days, creating compound exposures that may have synergistic effects on biological systems. We also need more attention to contextual variation, how housing, neighborhood infrastructure, and access to cooling resources shape actual heat burden experienced by older adults. This is especially pressing in low-income or racially marginalized communities, where systemic disinvestment may amplify risk. On the outcome side, biological aging is multidimensional. While epigenetic clocks help pinpoint biological responses to heat across systems, they capture only part of the picture. It remains unclear how—and to what extent—heat stress affects specific systems such as the immune, neuro, metabolic, cardiovascular, and renal systems in large human samples. Integrating additional biomarkers such as inflammatory cytokines, neurodegenerative markers, and metabolomic signatures can help build a more comprehensive understanding of how heat “ages” us biologically.

Final Reflections

Extreme heat is no longer exceptional—it is a defining feature of our climate reality. To understand its full toll on aging populations, we must look beyond acute events and capture the long-term, cumulative effects of chronic stress. Biological aging measures offer an important window into these processes, enabling earlier detection, monitoring of intervention impacts, and deeper insight into vulnerability. But how we measure exposure and aging matters. Choices about metrics and methods shape our conclusions—and our ability to act. Integrating high-resolution environmental data with multidimensional biomarkers will be key to building a fuller picture of how climate shapes the aging process.

References

Choi EY, Ailshire JA. Ambient outdoor heat and accelerated epigenetic aging among older adults in the US. Sci Adv. 2025;11(9):eadr0616. doi:10.1126/sciadv.adr0616

Bunker A, Wildenhain J, Vandenbergh A, et al. Effects of Air Temperature on Climate-Sensitive Mortality and Morbidity Outcomes in the Elderly; a Systematic Review and Meta-analysis of Epidemiological Evidence. eBioMedicine. 2016;6:258-268. doi:10.1016/j.ebiom.2016.02.034

Hajat S, O’Connor M, Kosatsky T. Health effects of hot weather: from awareness of risk factors to effective health protection. The Lancet. 2010;375(9717):856-863. doi:10.1016/S0140-6736(09)61711-6

Chen R, Wang Y, Zhang S, et al. Biomarkers of ageing: Current state-of-art, challenges, and opportunities. MedComm – Future Medicine. 2023;2(2):e50. doi:10.1002/mef2.50

Emami M, Agbaedeng TA, Thomas G, et al. Accelerated Biological Aging Secondary to Cardiometabolic Risk Factors Is a Predictor of Cardiovascular Mortality: A Systematic Review and Meta-analysis. Canadian Journal of Cardiology. 2022;38(3):365-375. doi:10.1016/j.cjca.2021.10.012

Fransquet PD, Wrigglesworth J, Woods RL, Ernst ME, Ryan J. The epigenetic clock as a predictor of disease and mortality risk: a systematic review and meta-analysis. Clin Epigenet. 2019;11(1):1-17. doi:10.1186/s13148-019-0656-7

Zhou A, Wu Z, Zaw Phyo AZ, Torres D, Vishwanath S, Ryan J. Epigenetic aging as a biomarker of dementia and related outcomes: a systematic review. Epigenomics. 2022;14(18):1125-1138. doi:10.2217/epi-2022-0209

National Weather Service, Wet Bulb Globe Temperature vs Heat Index. https://www.weather.gov/ict/WBGT.

Chiu KC, Hsieh MS, Huang YT, Liu CY. Exposure to ambient temperature and heat index in relation to DNA methylation age: A population-based study in Taiwan. Environment International. 2024;186:108581. doi:10.1016/j.envint.2024.108581

Ni W, Nikolaou N, Ward-Caviness CK, et al. Associations between medium- and long-term exposure to air temperature and epigenetic age acceleration. Environment International. 2023;178:108109. doi:10.1016/j.envint.2023.108109

Deborah Carr, Giacomo Falchetta, Ian Sue Wing, Population Aging and Heat Exposure in the 21st Century: Which U.S. Regions Are at Greatest Risk and Why?, The Gerontologist, Volume 64, Issue 3, March 2024, gnad050, https://doi.org/10.1093/geront/gnad050

Périard JD, Travers GJS, Racinais S, Sawka MN. Cardiovascular adaptations supporting human exercise-heat acclimation. Autonomic Neuroscience. 2016;196:52-62. doi:10.1016/j.autneu.2016.02.002

Li A, Toll M, Bentley R. Mapping social vulnerability indicators to understand the health impacts of climate change: a scoping review. The Lancet Planetary Health. 2023;7(11):e925-e937. doi:10.1016/s2542-5196(23)00216-4

Reid CE, O’Neill MS, Gronlund CJ, et al. Mapping Community Determinants of Heat Vulnerability. Environ Health Perspect. 2009;117(11):1730-1736. doi:10.1289/ehp.0900683

Murray KO, Clanton TL, Horowitz M. Epigenetic responses to heat: From adaptation to maladaptation. Experimental Physiology. 2022;107(10):1144-1158. doi:10.1113/EP090143

Continue reading

US Census Bureau Household Pulse Survey – Disaster Displacement

US Census Bureau Household Pulse Survey – Disaster Displacement

Link to code

Click here

Date: July 2025


Authors/Creators/ Team Members: Ther W. Aung, Ashwini R. Sehgal

Specific purpose of code: The purpose of this code is to analyze the questions regarding displacement due to disasters in US Census Bureau’s Household Pulse Survey. The code is applied to a single dataset.

General Application: This code is an example of analyzing nationally-representative survey data using weights and replicate weights.

How does or could this code allow researchers to assess research questions related  to aging or life course?: This code could be used or applied to analyze nationally-representative survey data, which tend to have age as a variable and may either span the entire population or target a particular demographic. The Household Pulse Survey has participants aged 18 and above, with age top-coded at 88 (age is calculated by subtracting year of birth from the survey year).

Data sets used: 

Coding Language: Stata

Tools and Packages used: svyset, svy

Output(s): Dataset, tables, multivariate covariates of displacement and collinearity assessment

Spatial extent: US

Temporal extent: 2022-2023

Published papers that use this code: Aung, T. W., & Sehgal, A. R. (2025). Prevalence, Correlates, and Impacts of Displacement Because of Natural Disasters in the United States From 2022 to 2023. American Journal of Public Health, 115(1), 55–65. https://doi.org/10.2105/AJPH.2024.307854

Related Papers: Depression and Anxiety Symptoms in Adults Displaced by Natural Disasters

Continue reading

Code linking the American Community Survey (ACS) microdata with the Spatial Hazards Events and Losses Database for the United States (SHELDUS)

Code linking the American Community Survey (ACS) microdata with the Spatial Hazards  Events and Losses Database for the United States (SHELDUS).

Authors: Deborah Balk, Kytt MacManus, Hieu Tran, Camilla Greene, Shemontee Chowdhury

Specific purpose of code: This  code links the American Community Survey (ACS) microdata with the Spatial Hazards  Events and Losses Database for the United States (SHELDUS).] 

Integration of Python programming with ArcGIS API, IPUMS API to pull Decennial Census data, create interactive maps, find insights about the changes in population and how badly the disabilities seniors’ indicators in Community Resilience Estimates (CRE) layer exposed to the Low Elevation Coastal Zone (LECZ) in Puerto Rico.

Link to code:  https://github.com/hieutrn1205/CACHED_estimate_social_vulnerability/blob/master/estimate_social_vulnerability.ipynb

General Application:

This is a lesson on linking Census data with LECZ Merit-DEM dataset on housing vacancies and population changes. In the lesson, we disseminate the regional and local data (county-level and tract level) on overlaying with the CRE layer to show how vulnerability of seniors who are currently living in the LECZ’s zones. The code will give the audience ability to estimate of many percentages’ social vulnerabilities people in the exposed zone also. The margin of error and statistical tests are 90 percent in CRE which gives us a solid statistically belief to the social vulnerabilities’ population.

How does or could this code allow researchers to assess research questions related  to aging or life course?:  This code could be used with the Decennial data to asses any 5 year age groups from under 5 to 85+ years of age, I had gathered the visualization on the 5 year-age groups in the pyramid chart for 2010 and 2020 to assess the mean of each Age/Sex group at admin level 0 (national).

Data sets used:

  • Population, socioeconomic, or health data: Decennial Census Data on Age/Sex, Occupancy Status (Vacancy), Social Vulnerabilities in Community Resilience Estimates (CRE).
  • Climate, weather, disaster or environment data: Low Elevation Coastal Zone (LECZ)

• Are all the data publicly available or are some restricted-access [choose one]:

• Which are restricted access? : Community Resilience Estimates (CRE). I have talked with the personnels at U.S Census regarding the restrictions. Please refer the users to the first question Community Resilience Estimates Frequently Asked Questions and “if the person is a potential researcher, they are able to access the data with an approved project through the Federal Statistical Research Data Centers. If they would like to go that route, please share my email address (sehsd.cre@census.gov). I’d be happy to get them started, or they can go here: Federal Statistical Research Data Centers.”

Coding Language:  Python

Tools and Packages used:  Pandas, Numpy, Matplotlib, ipumspy, arcgis

Output(s):  Maps, Graphs

Spatial extent: Puerto Rico

Temporal extent: 2010-2020

Continue reading

Code linking SHELDUS with ACS data

Code linking SHELDUS with ACS data 

Link to code

Click here

Date: June 2025


Authors/Creators/ Team Members:  Jenna Tipaldo, Deborah Balk, Dylan Connor, Helen Wilson Burns, Lori Hunter, Melanie Gall 

Specific purpose of code: This code links the American Community Survey (ACS) microdata with the Spatial Hazards Events and Losses Database for the United States (SHELDUS). 

General Application: This is an example of linking county-level data on disaster events with PUMA-level micro-data (that is, data on individuals or households) on sociodemographic characteristics. The code could be used with other PUMA-level survey data, or with other county-level environmental data. 

How does or could this code allow researchers to assess research questions related  to aging or life course?: This code could be used with the ACS data to assess any single years of age, so any combination of age group or subsets by age is possible. 

Data sets used: 

  • Population, socioeconomic, or health data: American Community Survey (ACS) from the U.S. Census Bureau
  • Climate, weather, disaster or environment data: Spatial Hazard Events and Losses Database for the United States (SHELDUS)

Are all the data publicly available or are some restricted-access? ACS is publicly available and free to download. SHELDUS is publicly available with data for South Carolina free to download (access to entire SHELDUS dataset requires an agreement with SHELDUS, potentially with compensation).  

Links to data: SHELDUS, ACS 

Coding Language:  R 

Tools and Packages used:  tidyverse, tigris, sf, gganimate, RColorBrewer 

Output(s): Dataset, Maps (static and animated), Graphs 

Spatial extent: South Carolina (Example), United States (application) 

Temporal extent: 2012-2022 

Published papers that use this code: Balk, D., Connor, D., Gall, M., Hunter, L., Tipaldo, J.F., Wilson Burns, H. *authors listed alphabetically. (2025, April) The Changing Demography of Disaster Impact in the US, 2012-2022, Paper presented at the Annual Meeting of the Population Association of America Meeting, April 2025, Washington, DC

https://submissions.mirasmart.com/Verify/PAA2025/Submission/Temp/rad2p2wgqwq.pdf  

Continue reading

What Am I Watching? Understanding the Health Impacts of Wildfire Smoke Exposure

What am I Watching? Understanding the health impacts of wildfire smoke exposure

Link to video recording

If you’re interested in contributing a short What Am I Reading post, we’d love to hear from you! Email us at cache@colorado.edu.

Written by Elizabeth Sorensen Montoya, Ph.D. University of Colorado Boulder  www.elizabethsorensenmontoya.com

If you live in the Eastern U.S. or the Midwest, you’ve probably spent the last few days breathing in that now-familiar sign of summer: Canadian wildfire smoke. But this isn’t just a North American problem. In recent years, wildfires have become more frequent, more intense, and harder to suppress. Because wildfire smoke can travel long distances, the health impacts often reach far beyond the burn zone.  

So, what does all this smoke actually mean for our health? 
 
As part of the Climate and Health Research Coordinating Center’s (CAFÉ RCC) State of the Science webinar series, Dr. Michael Brauer, professor at the School of Population and Public Health at the University of British Columbia, delivered an excellent talk exploring just that. You can watch the full seminar here. 
 
Below is a quick, high-level overview of some key takeaways from the presentation: 

  • The “new normal”: Wildfires are becoming more frequent, larger, and harder to suppress. Not only that, but they’ve begun to extend beyond what we have traditionally thought of as “fire season”, with smoke events occurring well outside traditional summer months. 
  • Health impacts: The talk covered a wide range of health outcomes linked to wildfire smoke exposure, from respiratory and cardiovascular impacts to emerging evidence on effects like dementia, reduced cognitive performance, and ambulance dispatches. A particularly interesting piece of the talk focused on recent research into the delayed impacts of wildfire smoke. For example, one study by Landguth and colleagues shows that smoke exposure during the summer can increase the risk of flu during the following winter.  
  • Looking ahead: Dr. Brauer talked about how wildfire smoke could change in the years to come, not only as a result of climate change but also our response to it. 
  • What can be done? Dr. Brauer ended the talk by outlining several approaches for reducing exposure, from individual-level interventions to community-level planning and preemptive actions.  

The seminar is well worth watching in full. Dr. Brauer does a fantastic job of weaving together scientific evidence, real-world case studies, and forward-looking perspectives.  

As wildfires continue to affect communities around the world, it’s increasingly important to understand the health risks and how we might reduce them. Dr. Brauer’s talk is a great starting point for those curious about wildfire smoke and health and a valuable resource for those already working in that field.    

 

 

References: 

Brauer, M. (2024) Understanding the health impacts of wildfire smoke exposure. Presented as part of the CAFÉ RCC State of the Science webinar series, 15 May. Available at: https://www.youtube.com/watch?v=2CViMQ-Xjuo 

Landguth, E.L., Holden, Z.A., Graham, J., Stark, B., Mokhtari, E.B., Kaleczyc, E., Anderson, S., Urbanski, S., Jolly, M., Semmens, E.O. and Warren, D.A., 2020. The delayed effect of wildfire season particulate matter on subsequent influenza season in a mountain west region of the USA. Environment international, 139, p.105668. 

Continue reading