Introduction
Air pollution exposure is an important risk factor for both cognitive decline and dementia [
1]. Fine particulate matter air pollution (PM
2.5) is ubiquitous in the air we breathe and is particularly harmful to the aging brain [
2]. Older adults living in areas with higher concentrations of PM
2.5, for example, perform worse on assessments of cognitive function [
3–
7] and experience more rapid cognitive decline [
8,
9] than older adults living in areas with lower concentrations of PM
2.5. This may be due to changes in brain structure, including white matter loss, which neuroimaging data has linked to PM
2.5 exposure [
10,
11]. These findings are consistent with evidence that air pollution increases risk of both brain inflammation and accumulation of amyloid-β, which are implicated in the pathogenesis of Alzheimer’s disease [
12,
13]. Older adults experiencing air pollutant-induced inflammation and neurodegeneration may therefore be more likely to develop cognitive deficits [
14]. Research to-date, however, has not found strong evidence for an association between PM
2.5 and incident cognitive impairment [
15].
Individuals with low levels of education may be particularly vulnerable to the negative impacts of air pollution on brain health. Prior research shows that less educated older adults report lower cognitive function [
16–
18] and are at increased risk for cognitive decline [
19] and the onset of dementia and Alzheimer’s disease [
20]. Less educated individuals are also more likely to live in more polluted neighborhoods [
21,
22]; however, even when similarly exposed to air pollution, individuals with less education often do not have the cognitive, economic, and health resources that more educated people have to mitigate the potential damage of air pollution to the brain.
Highly educated individuals may have a greater reserve against, or ability to compensate for, damage to the structure and functions of the brain that can arise from exposure to toxins such as air pollution. The cognitive decline that would typically accompany damage to brain function caused by air pollution exposure may be mitigated either through a reserve of pre-existing brain networks that have higher capacity (i.e., are more efficient) and are, therefore, less susceptible to damage, or through an ability to compensate against damage by activating alternate networks [
23,
24]. Research has found, for instance, that among individuals whose brains had pathology consistent with Alzheimer’s disease in postmortem examination, the more educated individuals were less likely to have exhibited clinical symptoms of dementia during their lifetimes compared to those with less education [
25].
Education also confers socioeconomic and health advantages that may reduce susceptibility to the adverse cognitive effects of air pollution [
26]. Highly educated individuals earn more money and accumulate more wealth, and these economic resources increase one’s ability to engage in healthier behaviors, including eating more nutritious food and smoking less, which have been shown to mitigate the effects of air pollution on health [
27–
29]. Having access to greater economic resources may also decrease co-exposure to other pollutants (e.g., indoor pollutants and second-hand smoke) that could exacerbate the adverse effects of ambient air pollution. Finally, less educated individuals are more likely to have pre-existing medical conditions, such as diabetes and cardiorespiratory disease, which are known to increase susceptibility to air pollution [
30,
31].
Thus, education may play a key role in buffering the effect of air pollution on cognitive impairment. The current study tests the hypothesis that the association between PM
2.5 and incident cognitive impairment is stronger among those with less educational attainment. Two major societal changes related to education and air pollution could, however, alter the relationship between air pollution, education, and cognitive impairment among successive cohorts of older adults. First, educational attainment and access to quality education increased markedly in the first half of the 20th century [
32,
33]. As a result, individuals who completed less than a high school education comprise a smaller proportion of the older adult population today than they did merely a decade ago and also represent a much more disadvantaged group. Second, in the past 20 years the EPA began regulating PM
2.5, which resulted in a 43% decline in the national average PM
2.5 concentration [
34]. Therefore, this study examines the role of education in the association between PM
2.5 and cognitive impairment in two cohorts of older adults assessed 10 years apart.
Methods
Study population
We used data from the Health and Retirement Study (HRS), a nationally representative, longitudinal study of U.S. adults over age 50 [
35]. Our sample includes HRS respondents ages 60 and older, living in the community or a nursing home in 2004 or 2014. We excluded respondents who lived in a nursing home in the prior wave, and thus were potentially exposed to a different pollution environment, as well as those who were classified as having cognitive impairment in the prior wave. The 2004 cohort included 9,970 respondents and the 2014 cohort included 9,185 respondents after we excluded 41 and 192 respondents in 2004 and 2014, respectively, due to missing data on analytic variables. HRS employs a steady-state design, replenishing the sample with younger cohorts every 6 years to ensure it remains representative of the older adult population over time. Our analytic sample includes 4,334 respondents who were included in both the 2004 and 2014 cohorts, 5,636 respondents who were included only in 2004, and 4,851 respondents who were included only in 2014.
Assessment of incident cognitive impairment
Information from respondents, proxies, and interviewers is used to identify cognitive impairment. Respondents are administered the Telephone Instrument for Cognitive Status (TICS) to assess cognitive function either by phone or in face-to-face interviews. The cognitive assessment consists of tests that evaluate the respondent’s memory, using 10 word immediate and delayed recall, and attention and processing speed, using a serial 7s subtraction test of working memory and counting backwards. Scores from all items in the cognitive assessment were summed into a composite score of cognitive functioning, ranging from 0–27. Performance on the cognitive assessment is used to determine the respondent’s level of cognitive impairment. We use the Lange-Weir classification to assign respondents with a score of 12–27 as having normal cognition, scores of 7–11 as having cognitive impairment with no dementia, and scores of 0–6 as having impairment consistent with dementia [
36].
Cognitive impairment can also be measured in respondents who did not take the cognitive assessment by utilizing information from the interviewer and proxy assessments of respondent functioning. Proxy reports of limitations in instrumental activities of daily living (IADLs) and assessment of respondent’s memory, as well as the interviewer’s assessment of respondent’s cognition were scored and summed to create a total cognition score, ranging from 0–11. Using the Langa-Weir classification, respondents with scores of 6–11 are categorized as having normal cognitive function, while scores of 3–5 and 0–2 are categorized as having cognitive impairment with no dementia and dementia, respectively. Thus, we are able to determine cognitive impairment in both self and non-self respondents. It has previously been established that this approach to differentiating among respondents with normal functioning versus cognitive impairment has good predictive ability when compared with classification from a consensus panel of experts in neuropsychiatric assessments of dementia [
37,
38].
The dependent variable for this study is incident cognitive impairment, which includes respondents classified as having cognitive impairment with or without dementia. In order to measure incident cognitive impairment, we excluded any respondents who were classified as having any cognitive impairment in the previous wave; respondents with cognitive impairment in 2002 were excluded from the 2004 cohort and respondents with cognitive impairment in 2012 were excluded from the 2014 cohort.
Fine particulate matter air pollution (PM2.5)
HRS respondent addresses have been geocoded and assigned census tract identifiers that can be used to link to other geographic data. Data on PM
2.5 come from the HRS Contextual Data Resource (HRS-CDR), which provides annual average PM
2.5 linked to the census tract in which respondents resided at the time of interview [
39]. The HRS-CDR consisted of monthly and annual measures aggregated from data provided by the U.S. the Environmental Protection Agency’s Downscaler Model (DS) [
40–
42]. The DS model leverages the accuracy of air quality monitors with the spatial and temporal coverage of modeled data to provide gridded (12 km) prediction surfaces of daily air pollution concentrations for the contiguous U.S. that are aggregated to create daily averages at the census tract level. We average across measures from the two years prior to the determination of incident cognitive impairment. For 2004, the measure of PM
2.5 reflects the average of years 2002–2003 and, for 2014, the average of years 2012–2013. Although we use a linear term for PM
2.5 in our analyses, we also examined potential non-linear associations between PM
2.5 and cognitive impairment. Examination of both linear and quadratic associations with PM
2.5 showed no evidence of non-linearity in either 2004 or 2014. To facilitate interpretation, we report PM
2.5 in 5-unit increments.
Educational attainment
We used self-reported years of schooling to assess educational attainment and classified respondents into four categories: 0–8, 9–11, 12, and 13 or more years of education.
Covariates
Demographic covariates included age (in years), gender (female or male), race/ethnicity (non-Hispanic White, non-Hispanic Black, Hispanic, or Other), and region (Northeast, Midwest, South, and West). Socio-economic status was measured using continuous indicators of annual household income (includes earnings, investments, pensions, and Social Security income) and household net worth (the difference between assets, such as from home values and investments, and debts) in the previous year, measured in nominal US dollars. For easier interpretation of coefficients, income and wealth are divided by 10,000 when included in multivariable models. Health conditions included respondent reported doctor diagnosed diseases and conditions (stroke, diabetes, heart disease, hypertension, lung disease), and current smoking status (current smoker, former smoker, never smoker). Finally, we include a measure of the percent of residents in the census tract with income below the poverty line.
Statistical analyses
We used mixed-effects logistic regression models to account for statistical dependence among respondents living in the same census tract. We first examined the association between PM2.5 and incident cognitive impairment. We then adjusted for individual sociodemographic characteristics, including education. Next, we added interaction terms between PM2.5 and education categories. In the final model, we further adjusted for socioeconomic characteristics, health status, and smoking. We present results from mixed effects regression models separately for the 2004 and 2014 cohorts. All descriptive and multivariable analyses are weighted to represent both older adults living in the community and in nursing homes. All analyses were conducted in Stata/SE 16.
Results
Characteristics of the 2004 and 2014 samples are shown in
Table 1. In 2004, 13.9% of respondents had incident cognitive impairment. Most respondents had completed at least 12 years of education, with 6.4% completing 8 or fewer years of school and 11.8% completing 9–11 years of education. In 2014, incident cognitive impairment was found in only 10.5% of respondents. Over 90% had completed at least 12 years of education, with 3.5% completing 8 or fewer years of school, and 6.8% completing 9–11 years of education. In both 2004 and 2014, the sample was about 70 years old on average, just over half were women, and the majority were white.
We plot the distribution of PM
2.5 for both 2004 and 2014 in
Fig. 1. The mean 2004 concentration of PM
2.5 was 12.4, with a standard deviation of 2.8. Thus, just over half of the sample lived in areas with PM
2.5 concentrations above the EPA regulatory threshold of 12
μg/m
3. By 2014, the distribution of PM
2.5 had changed considerably. The mean concentration was 9.2, with a standard deviation of 1.7. In 2014, most respondents lived in areas with PM
2.5 concentrations below the threshold at which the EPA considers harmful to human health.
Table 2 shows the main effects and interactions for PM
2.5 and education from mixed-effects models of incident cognitive impairment. Results showing all model covariates are provided in Supplementary Tables 1 and 2. Log odds and standard errors for 2004 are shown in
Table 2A. In Model 1, a 5
μg/m
3 increase in PM
2.5 concentration was associated with a 12% increase in the odds of incident cognitive impairment (
b = 0.12,
p < 0.05). This relationship was no longer statistically significant with adjustment for individual sociodemographic characteristics in Model 2, in particular race/ethnicity. In addition, compared to older adults with 8 or fewer years of education, those with 12 years of education had lower log odds of cognitive impairment (
b = –0.900,
p < 0.001), as did those with 13 or more years of education (
b = –1.558,
p < 0.001). Interactions between PM
2.5 and education included in Model 3 indicate that a 5
μg/m
3 increase in PM
2.5 concentration was associated with an increase in the log odds of incident cognitive impairment among those with 8 or fewer years of education (
b = 0.314,
p < 0.05). There was also a statistically significant interaction between PM
2.5 and 13 or more years of education (
b = –0.436,
p < 0.05), indicating no association between PM
2.5 and incident cognitive impairment among the most educated. These associations were largely unchanged with further adjustments for socioeconomic factors, health status, and health behaviors in Model 4. We found nearly identical results in models using a 1-year average for PM
2.5 in 2003.
We plot the predicted probability of cognitive impairment in 2004 in
Fig. 2 based on estimates from Model 4 across PM
2.5 concentrations for each education group. Predicted probabilities and associated 95% confidence intervals are provided in Supplementary Table 3. To avoid out-of-sample predictions, we plotted data over values of PM
2.5 with cell sizes of 100 or greater. The flat line found for those with 13 years or more of education indicates no association between PM
2.5 and cognitive impairment for this group. We only find a statistically positive association between PM
2.5 and incident cognitive impairment among those with 8 or fewer years of education, indicating that it is the least educated that are at increased risk of cognitive impairment from living in more polluted environments.
Next, we examined these associations in 2014 and present those results in
Table 2B. Model 1 shows that a 5
μg/m
3 increase in PM
2.5 concentration was associated with a 32% increase in the odds of incident cognitive impairment (
b = 0.323,
p < 0.05). This relationship was no longer statistically significant with adjustment for individual sociodemographic characteristics in Model 2. Similar to the results for 2004, the association was reduced primarily due to the inclusion of race/ethnicity. Compared to older adults with 8 or fewer years of education, we found lower log odds of cognitive impairment among those with 9–11 years of education (
b = –0.539,
p < 0.05), 12 years of education (
b = –1.206,
p < 0.001), and 13 or more years of education (
b = –2.074,
p < 0.001). We did not find any evidence for an interaction between education and PM
2.5 in 2014.
As shown in
Fig. 1, the distribution of PM
2.5 substantially shifted from 2004 to 2014 resulting in fewer older adults living in high pollution environments in 2014. Furthermore, this shift in PM
2.5 occurred throughout the distribution of education (Supplementary Table 4), including among those with cognitive impairment (Supplementary Table 5). This may explain the lack of an association between education and PM
2.5 on incident cognitive impairment in 2014. To determine whether the difference in findings between the 2004 and 2014 samples was due to differences in the pollution environment, we conducted additional analysis of the 2004 sample living in areas with PM
2.5 less than 12
μg/m
3. There was no association between education and PM
2.5 on cognitive impairment among older adults in less polluted environments in 2004.
Discussion
Lower educational attainment and greater exposure to air pollution are both associated with poor cognitive function among older adults, and theory and evidence suggests education may moderate the relationship between air pollution and brain health. But no studies to our knowledge have examined whether the association between air pollution and cognitive impairment varies according to level of education. Our study aimed to address this gap by determining if the relationship between PM2.5 and incident cognitive impairment differed according to older adults’ educational attainment. We found some evidence that education serves as a buffer against the adverse impact of air pollution on cognitive impairment, but that this may only be true in populations exposed to high pollution environments.
We found that a 5
μg/m
3 increase in PM
2.5 concentration was associated with a 15% increase in the odds of incident cognitive impairment in 2004, but that with adjustment for individual characteristics, particularly race/ethnicity, the association was no longer statistically significant. The lack of an association between PM
2.5 and incident impairment, and the confounding role of race, has also been reported in other studies of older U.S. adults [
15]. We think race/ethnicity confounds the association between PM
2.5 and cognitive impairment because race/ethnic minorities have higher risk of cognitive impairment and also live in more polluted areas due to a history of racial residential segregation and environmental injustices in these communities. We did, however, find evidence of an association between PM
2.5 and incident impairment among the least educated. While the likelihood of incident cognitive impairment was unrelated to PM
2.5 among those with 13 or more years of education, it increased with increasing concentrations of PM
2.5 among those with 8 or fewer years of education. Similar interactions between PM
2.5 and education have been found in research on mental health [
43]. Accounting for socioeconomic and health-related risk factors did not explain the greater impact of PM
2.5 on incident cognitive impairment among those with less education, suggesting education operates via other resources such as cognitive reserve. Air pollution-induced damage to the brain may have a weaker impact on cognitive function for those with higher levels of education because education itself is associated with greater cognitive processing efficiency and increased ability to mobilize alternative neural pathways necessary for maintaining cognitive function [
23].
In 2014, a 5
μg/m
3 increase in PM
2.5 concentration was associated with a 37% increase in the odds of incident cognitive impairment. But the association was not statistically significant after adjusting for individual characteristics. Although there was an education gradient in incident cognitive impairment, we did not find any interactions between PM
2.5 and education. Research has shown that education is becoming a stronger predictor of health and mortality among older adults [
44–
46], due in part to compositional changes in who completes and does not complete higher education [
33] as well as socio-historical changes occurring within the U.S. education system that changed the meaning of education across successive cohorts [
32]. Dementia prevalence has been declining in the U.S. population, and globally, attributed primarily to increased educational attainment in younger cohorts of older adults, and the resulting improvements in health [
47–
51]. At the same time, PM
2.5 has been declining across the U.S. and may be a less important predictor of cognitive impairment at lower concentrations. Studies examining the association of PM
2.5 with mortality, for instance, have found that the human health burden from PM
2.5 declined from 2000 to 2010 [
52,
53]. Thus, while education may protect against the adverse impact of PM
2.5 at the higher levels of pollution observed in 2004, it may not confer any additional protection under conditions of improved air quality.
Our findings provide preliminary evidence that environmental policy should be considered in approaches to reduce or delay cognitive impairment and dementia in the older adult population. Much of the focus in dementia research has been on reducing risk from individual-level factors such as poor health and behaviors [
54,
55]. The current study adds to the growing literature showing that environmental factors are also key determinants of cognitive health and highlights the importance of considering the interaction between individual and environmental risks. In addition, we identified a potentially vulnerable group, those with the least education, who had the greatest risk of cognitive impairment with increasing PM
2.5 in 2004. However, though PM
2.5 has declined since 2000, data from the past few years indicate a return to higher concentrations, with potentially negative implications for human health [
52]. A return to prior PM
2.5 levels could result in increasing rates of onset and progression of cognitive impairment and dementia in the population.
Strengths of this study include the use of a large, nationally representative and socioeconomically and geographically diverse cohort of U.S. older adults that allowed us to examine incident cognitive impairment across a wide distribution of educational attainment and PM2.5. In addition, by examining two different time periods we were able to show that the impact of PM2.5 on incident impairment, and the potentially modifying role of education, are highly dependent on cohort-specific levels of educational attainment and exposure to high pollution environments.
This study also has some limitations. The assessments on which we base our classification of cognitive impairment come from survey-based measures rather than physician’s diagnosis. However, classification of cognitive impairment in the HRS demonstrates very high agreement with that based on a consensus panel of experts in neuropsychiatric assessments of dementia [
37]. In addition, our measure of outdoor PM
2.5 concentrations may not completely capture total individual exposure. Although outdoor pollution is an important contributor to total exposure, exposure can also occur in other contexts, such as in the workplace or during daily road travel. As the sample was aged 60 and older, most of the sample was not employed, so pollution concentrations at their place of residence may be a good approximation of their total exposure. Due to the relatively small spatial variability in PM
2.5 within urban areas, there is a high correlation between concentrations of outdoor and both indoor and personal PM
2.5 [
56]. Moreover, we use a tract-specific measure of PM
2.5 concentrations because we do not have access to respondent addresses. However, because there is relatively little micro-scale spatial variability in PM
2.5 across small areas like a census tract, we expect the tract-level measures we used closely match concentrations at the respondent’s address. Importantly, we do not capture long-term, or lifetime, pollution exposure. Our measure may, however, reflect some degree of longer-term air pollution because pollution concentrations are highly correlated over time [
56], and many respondents reported living in the same neighborhood for at least a decade.
Conclusion
The current study highlights the importance of accounting for differential susceptibility in examination of risk factors for cognitive health and in assessing the health impacts of air pollution. The cognitive harms of pollution exposure may, for instance, be offset by educational attainment, suggesting that the health impacts of air pollution are not uniform. Less educated older adults are more likely to live in polluted areas [
21,
22], and our findings suggest they may also be more susceptible to the adverse cognitive effects of air pollution. This study, therefore, identifies a particularly vulnerable population both with respect to the adverse health consequences of air pollution and the increased risk for cognitive aging. Unlike other modifiable risk factors for cognitive decline and dementia, air pollution can be modified at the population level through environmental regulation and technological innovation. Given its ubiquity, if exposure to air pollution is causally related to dementia, population-level reductions in exposure may significantly alter the population-level burden of dementia, even if the effects are modest.