Literature DB >> 32203058

Modeling and comparing central and room air conditioning ownership and cold-season in-home thermal comfort using the American Housing Survey.

Carina J Gronlund1, Veronica J Berrocal2.   

Abstract

Household-level information on central air conditioning (cenAC) and room air conditioning (rmAC) air conditioning and cold-weather thermal comfort are often missing from publicly available housing databases hindering research and action on climate adaptation and air pollution exposure reduction. We modeled these using information from the American Housing Survey for 2003-2013 and 140 US core-based statistical areas employing variables that would be present in publicly available parcel records. We present random-intercept logistic regression models with either cenAC, rmAC or "home was uncomfortably cold for 24 h or more" (tooCold) as outcome variables and housing value, rented vs. owned, age, and multi- vs. single-family, each interacted with cooling- or heating-degree days as predictors. The out-of-sample predicted probabilities for years 2015-2017 were compared with corresponding American Housing Survey values (0 or 1). Using a 0.5 probability threshold, the model had 63% specificity (true negative rate), and 91% sensitivity (true positive rate) for cenAC, while specificity and sensitivity for rmAC were 94% and 34%, respectively. Area-specific sensitivities and specificities varied widely. For tooCold, the overall sensitivity was effectively 0%. Future epidemiologic studies, heat vulnerability maps, and intervention screenings may reliably use these or similar AC models with parcel-level data to improve understanding of health risk and the spatial patterning of homes without AC.

Entities:  

Keywords:  Air conditioning; Climate change; Vulnerability

Mesh:

Year:  2020        PMID: 32203058      PMCID: PMC7483423          DOI: 10.1038/s41370-020-0220-8

Source DB:  PubMed          Journal:  J Expo Sci Environ Epidemiol        ISSN: 1559-0631            Impact factor:   5.563


INTRODUCTION

The primary function of housing is to protect us from “the elements,” and therefore housing quality is likely a critical mediator in the documented associations between weather, air quality, and health. In many key studies of the health effects of temperature and air pollution, large administrative databases of healthcare billing records or vital records have been linked to outdoor environmental exposure data with increasing spatial and temporal resolution (1–3). However, these studies usually lack information on housing quality or characteristics, or such information is available only at an ecologic scale (4, 5). Central air conditioning is likely a particularly important mediator of associations between ambient exposures and health, given its capacity to filter and cool air. This absence of housing information may lead to exposure misclassification and mis-estimation of the environmental health effects, given the imperfect, though moderate, correlations between outdoor and indoor exposures (6, 7). To understand how housing characteristics affect vulnerability to these ambient exposures, there has been increased interest in linking these data sets to tax assessor’s records. Available at the parcel level, these records include characteristics of the home relevant to establishing its value for taxation purposes. These characteristics usually include the year the home was built, occupation by a renter or owner (tenure), and the resulting assessed value. Sometimes, these records also include information about the number of stories, siding, basement type, and heating and cooling systems. However, the recorded characteristics vary widely between municipalities, and these more detailed characteristics, including central air conditioning, are often not available. City health officials, particularly in temperate or cold climates, are also interested in the magnitude and variability of cold health effects. In many cities, in the present climate at least, cold-associated mortality and morbidity are greater than heat-associated mortality and morbidity (8–10). Though some evidence suggests that these burdens are borne disproportionately by homeless individuals, other lines of evidence suggest that individuals in homes with inadequate heating and cooling or even dangerous heating methods are also particularly vulnerable to increased morbidity or mortality during extreme heat and/or cold (11). Therefore, having models to predict central air conditioning ownership and uncomfortably cold indoor temperature in residential homes could further our understanding of the mediating and modifying effects of these characteristics on health in the warm and cold seasons in epidemiologic studies. In turn, this information could be used to screen households for allocation of weatherization resources, with potential prioritization of 1) homes that lack central air conditioning, 2) homes that are deemed too cold in the winter, 3) homes that use energy inefficiently, which can also be predicted from housing characteristics (12), and 4) households that can’t afford to pay for utilities (13–18). These homes and households could also be prioritized in policies addressing health through improving housing conditions. The American Housing Survey, started in 1973, originally represented two longitudinal surveys: a biennial national sample and a biennial metropolitan sample, consisting of a rotating subset of 67 U.S. core-based statistical areas (CBSAs). In 2015, the sampling strategy was altered, questions were revised, and an entirely new sample of participants was recruited (19). The surveys include a wide variety of questions about housing type and condition. Among the questions asked in the 2003–2013 surveys are “Does this housing unit have central air conditioning,” “Does the housing unit have any room air conditioners,” and “Last winter, for any reason, was your housing unit so cold for 24 hours or more that it was uncomfortable?”. Using data from the 2003–2013 American Housing Survey, we first tested whether homes that lacked central air conditioning were the same homes that were reported as being uncomfortably cold for 24 hours or longer in the winter, to understand how strongly correlated these two temperature-related vulnerabilities were. Then, we constructed predictive models of central air conditioning ownership and cold indoor temperatures using commonly available parcel characteristics, hypothesizing that we could predict central AC ownership using year in time, year built, market value, and tenure in 140 U.S. CBSAs. We validated the out-of-sample predictions of our models using 2015–2017 American Housing Survey data. For central air conditioning ownership, we also tested the validity of the model using parcel data from Wayne County, Michigan, and, to illustrate a potential usage of our model predictions, we mapped the probability of air conditioning ownership at the parcel level in Wayne County, Michigan.

METHODS

The process for developing, validating, and applying models predicting central air conditioning (cenAC), room air conditioning (rmAC), and the home being too cold in the winter (tooCold) for a given parcel is outlined in Figure 1 and described in detail below.
Figure 1.

Process for developing and applying models predicting central air conditioning (cenAC), room air conditioning (rmAC), and uncomfortably cold indoor winter temperatures (tooCold) for a given parcel.

Data

We downloaded publicly available American Housing Survey microdata for 2003–2017, for which the CBSA of the household is provided. Over 75% of respondents provided responses in only one survey year, so in instances where participation occurred in multiple years, only the most recent year of data was retained for that household. We retained variables for: year of survey, year the home was built, housing value, monthly rent, multi- vs. single-family, tenure (rented or owned by resident), central air conditioning ownership (cenAC), and “home was uncomfortably cold for 24 hours or more” (tooCold). To convert monthly rent values to a housing value, we assumed a 10% annual rent-to-value ratio (20). Regional heating and cooling needs were estimated as average annual cooling-degree days (CDDs, cumulative number of degree days above 18 C per year) and heating-degree days (HDDs, cumulative number of degree days below 18 C per year), each averaged over a 30-year period. In R 3.5.0, CBSAs, from the tigris package, were superimposed using the gIntersection function (rgeos package) over state-specific climate divisions, 2–10 per state, using the definition from the Climate Prediction Center, and area-weighted averages of each climate division’s 30-year (1981–2010) CDDs and HDDs (21) were extracted for each CBSA.

Statistical Analysis

Summary statistics were computed as follows. The weighted means or proportions of each housing characteristic were computed within each CBSA using the survey weights provided by the AHS. Then, means, interquartile ranges, minima, maxima, and 25th, 50th, and 75th percentile values were calculated across the 140 CBSAs. Separately, annual weighted means were computed using the national survey results only because different CBSAs are sampled in the metropolitan surveys on different years. To predict whether a house does or does not have central air conditioning, we constructed the following logistic random intercept model using the lme4 package in R: with defined as = 1 + 2CDD, for x = 1 to 11. In the model above, we used the following notation: for household h in CBSA m, PcenAC denotes the probability of cenAC, YRBLT indicates the year the home was built, RENTAL is an indicator for whether the home was rented or owned by the resident, YEAR indicates the year of the survey, LNMARKVAL denotes the natural log of the market value, MULTIFAM is an indicator for whether the home was multi-family or single-family, MOBILEHOME is an indicator for whether the home was a mobile home or not, and γm and εhm represent random effects for CBSA and households, respectively, each following normal distributions. In addition, CDD indicates cooling-degree days, and, assuming a modifying effect for this term, we interacted it with each of the household-level terms. The rmAC and tooCold models were similar, except heating degree-days were used in place of cooling degree-days. To examine for residual spatial dependence in PcenAC, rmAC and tooCold not accounted for by the covariates we constructed and inspected semivariograms of the Pearson residuals using R’s gstat package. To validate the predictive power of the model, we used a hold-out validation procedure (22), comparing the out-of-sample predicted probabilities obtained using the logistic regression model fit using 2003–2013 AHS data with the AHS values for 2015–2017 data. The 2015 sampling year provided a natural cut-point for dividing the data into training and test data sets because of the substantial revisions to the survey in 2015 described above and the inclusion in 2015–2017 of only 35 of the 140 core-based-statistical areas available in the 2003–2013 sample. We calculated accuracy, sensitivity (true positive rate), and specificity (true negative rate), overall and by city using R’s pROC package. To compare cenAC, rmAC, and tooCold, we cross-tabulated each of the AC variables with tooCold in our entire set of the 2003–2017 AHS and calculated prevalence ratios and Wald confidence intervals using the epiR package in R. To demonstrate the utility of these models, we created maps of the predicted probabilities in the City of Detroit by linking the cenAC and anyAC (cenAC or rmAC) with residential parcel data (23). Such records are commonly publicly available in the U.S. These records, based on tax assessor’s records, do not indicate in Detroit whether a home has air conditioning but do include year built, rental (based on whether the owner’s address matches the property address), assessed value, and whether the unit was multifamily. There are no mobile home parks within Detroit city limits, so we assumed that none of the parcels contained a mobile home.

Code Availability

the R code is available from Dr. Gronlund on request.

RESULTS

Across 140 CBSAs from 2003–2013, an average of 68% of homes in a CBSA had central AC, with central AC prevalence as low as 5% (Utica-Rome, NY) and as high as 99% (El Paso, TX). Housing units with room AC ranged from 0–72% by CBSA with a mean of 25%, while homes reported as having been uncomfortably cold for 24 hours or more in the winter in a CBSA ranged from 0–24%, with a mean of 8.7%. None of the homes in the sample had been built prior to 1910, and average year built ranged from 1937 to 1983. Mean housing value ranged widely, from $48,000 to $344,000, with a median of $107,000 that was similar to the housing values geometric mean of $114,000. Climatic conditions ranged widely as well, with annual degree-days ranging between 150–3,800 CDDs and 300–9,200 HDDs (Figure 2, Table 1). In addition to wide spatial variability in the selected housing characteristics, temporal trends were evident for some of the housing characteristics. The proportion of homes with central air conditioning rose from 0.50 in 2003 to 0.64 in 2013. Likewise, mean year built and mean housing value also rose over time (Table 2).
Figure 2.

Average annual cooling-degree days (CDDs, cumulative number of degree days above 18 C per year), for the 1981–2010 climatological period, in each of the 140 available core-based statistical areas (CBSAs), American Housing Survey, 2003–2013.

Table 1.

Summary statistics of climate and housing characteristics across 140 U.S. core-based statistical areas (CBSAs), 2003–2013.

CharacteristicMeanMinimum25th PercentileMedian75th PercentileMaximum
Number of households sampled[1]1,30619521052,6988,042
Proportion of households with central air conditioning (cenAC)[1]0.670.0460.500.730.890.99
Proportion of households with room air conditioning (rmAC)[1]0.250.000.130.200.340.72
Proportion of households uncomfortably cold for 24 hours or more (tooCold)[1]0.0850.000.0590.0850.110.24
Annual cooling degree-days (CDDs)[2]1,3001505609101,9003,800
Annual heating degree-days (HDDs)[2]4,5003002,7004,6006,4009,200
Mean year built[1]196319371957196419711983
Mean year of survey[1]201020052010201120112011
Proportion of rental homes[1]0.380.210.320.370.450.61
Proportion of multi-family homes[1]0.290.040.220.270.350.64
Proportion of mobile homes[1]0.0260.0000.0000.0180.0390.187
Geometric mean housing value (dollars)[1,3]112,00048,00085,800107,000140,000344,000

American Housing Survey

National Weather Service Climate Prediction Center

Dollar values were not discounted across years.

Table 2.

Means or proportions of selected housing characteristics by survey year, American Housing Survey National Survey, 2003–2013.

200320052007200920112013
Proportion of households with central air conditioning (cenAC)0.500.540.600.590.650.64

Proportion of households with room air conditioning (rmAC)0.320.300.280.300.280.28

Proportion of households uncomfortably cold for 24 hours or more (tooCold)0.100.080.100.100.100.09

Mean year built195719571959195919641960
Proportion of rental homes0.400.490.540.490.360.41
Proportion of multi-family homes0.350.420.460.430.300.33
Proportion of mobile homes0.060.020.020.010.020.01
Geometric mean housing value (dollars)117,000110,000112,000125,000143,000140,000
In models of central AC, room AC and uncomfortably cold indoor winter temperatures, the semivariograms of the residuals from each of the three models did not reveal any residual spatial dependence. All of the characteristics included in the central AC and room AC models were statistically significant predictors of AC status, either alone or in interactions. When the continuous variables representing housing characteristics were scaled to an IQR increase, the housing characteristics most strongly associated with central AC ownership were year built, CDDs, and housing value, all of which predicted increased likelihood of central AC. In rental housing units, central AC was less likely, although this was attenuated in homes of higher value and in homes in CBSAs with more CDDs, i.e., warmer CBSAs. Year built, CDDs and housing value were also strong predictors of room AC. In contrast to central AC, these characteristics predicted a decreased likelihood of room AC. Being in a multi-family housing unit in a warmer climate was also associated with decreased likelihood of room AC. Indeed, central AC and room AC were strongly inversely associated, with a 0.04 (95% CI: 0.03, 0.04) odds of lacking room AC among individuals lacking central AC vs. those not lacking central AC. For uncomfortably cold indoor winter temperatures, being in a rental unit, a home in a cooler climate (more HDDs), and a mobile home were the strongest predictors. Newer homes were associated with a lower likelihood of uncomfortably cold indoor winter temperatures. In contrast to the AC models, many of the interaction terms between the characteristics were not significant. For both the uncomfortably cold and the AC models, the likelihood of uncomfortably cold indoor winter temperatures or AC increased in later years of the survey indicating increasing trends in all three housing characteristics, holding other characteristics constant. For central AC in particular, we observed a 0.23 increase in the log-odds (i.e., a 1.26 times higher odds) of central AC for each 5-year increase in time (Table 3).
Table 3.

Change in the log-odds of central air conditioning ownership (cenAC), room air conditioner ownership (rmAC) and “home was uncomfortably cold for 24 hours or more” (tooCold) for presence vs. absence or interquartile-range (IQR) increase[1] in each characteristic in 140 U.S. core-based statistical areas, 2003–2013.

cenACrmACtooCold
CoefficientStandard ErrorCoefficientStandard ErrorCoefficientStandard Error
Intercept1.510.11***−1.600.07***−2.500.04***
Year built1.120.01***−0.870.01***−0.230.01***
Rental−0.520.02***0.310.02***0.360.02***
DDs1.160.12***−0.420.07***0.350.06***
Year of survey0.230.01***0.030.01***0.200.01***
ln(Housing value)0.620.01***−0.420.01***−0.140.01***
ln(Housing value)20.090.00***−0.070.00***0.000.00
Multi-family0.030.02−0.080.02***−0.200.02***
Mobile home−0.560.04***0.740.03***0.410.04***
Year built x rental0.040.02*0.260.01***−0.090.02***
Year built x DDs0.270.01***−0.160.01***0.150.02***
Rental x DDs0.160.03***−0.230.02***−0.060.04
Year of survey x rental−0.200.02***0.070.02***−0.200.02***
Year of survey x DDs−0.160.01***0.040.01***0.090.02***
ln(Housing value) x rental0.360.02***−0.140.02***0.040.02
ln(Housing value) x DDs0.240.01***−0.150.01***0.110.02***
ln(Housing value)2 x rental0.120.01***−0.060.01***−0.020.01*
ln(Housing value)2 x DDs0.010.00***−0.010.00**0.020.01***
Multi-family x DDs0.330.02***−0.430.02***0.160.04***
Year built x rental x DDs−0.200.02***−0.180.02***−0.020.03
Year of survey x rental x DDs0.190.02***−0.060.02***−0.090.04**
ln(Housing value) x rental x DDs0.060.03*−0.130.03***−0.060.04
ln(Housing value)2 x rental x DDs0.030.01***−0.020.01*−0.010.01

P-value < 0.05

P-value < 0.01

P-value < 0.001

Note that the odds ratios for presence vs. absence or an interquartile-range increase can be found by taking exp(coefficient).

DDs = mean annual cooling degree-days (CDDs, in air conditioning models) or mean annual heating degree-days (HDDs, in tooCold model).

The value of the random effect for each core-based statistical area is provided in Supplemental Material Table 1 as well as instructions for computing parcel-level probabilities.

The standard deviations of the random effects were 1.18, 0.69, and 0.34 for the cenAC, rmAC, and tooCold models, respectively.

The IQR increases for year built, CDDs, HDDs, year of survey, and ln(Housing value) were calculated on the raw data rather than the CBSA means (as in Table 1) and therefore differ from those in Table 1. They are 30 years, 1000 CDDs, 3000 HDDs, 5 years, and 1 log-dollar, respectively.

In comparing predicted central AC values to true central AC values in the 2015–2017 AHS hold-out data, the central AC model performed reasonably well (Table 4). If we use a probability threshold of 0.5 to declare a home as having central AC if the predicted probability is above it and not having central AC if the predicted probability is below it, the model has a 63% specificity. That means that the model correctly identified homes without central AC 63% of the time. On the other hand, the model has a 91% sensitivity, that is, it correctly identifies homes with central AC 91% of the time. Finally, the overall area under the receiver operating characteristic (ROC) curve, e.g. AUC, is 89%. By choosing a higher threshold of 0.9 at which to consider a home to have central AC, the model achieves a higher specificity (95%) at the cost of sensitivity, which drops to 59%. The thresholds at which sensitivity and specificity were maximized are close to 0.5 for both the central AC and the room AC models. At this threshold, the room AC model has a higher specificity of 94% but a lower sensitivity of 34%, and an overall area under the ROC curve of 80%. ROC curves for these two models suggested good model utility for many of the CBSAs (Figure 3). However, the room AC models failed in Seattle-Tacoma-Bellevue, WA and San Francisco-Oakland-Hayward, CA where the areas under the ROC curve are close to 0.5.
Table 4.

Model sensitivity and specificity for logistic regression models of central air conditioning (cenAC), room air conditioning (rmAC) and “home was uncomfortably cold for 24 hours or more” (tooCold). Sensitivity and specificity are obtained by comparing predicted probabilities for the 2015–2017 period to the 2015–2017 American Housing Survey data.

Model Threshold[1] = 0.1Model Threshold[1] = 0.5Model Threshold[1] = 0.9
cenACSpecificity[2]63%95%
Sensitivity[3]91%59%
Accuracy[4]84%68%
rmACSpecificity[2]94%100%
Sensitivity[3]34%1%
Accuracy[4]82%80%
tooColdSpecificity[2]57%100%
Sensitivity[3]62%0%
Accuracy[4]57%93%

Model threshold refers to the modeled probability above which a housing unit is considered to have AC or be tooCold.

True negative rate, i.e., the rate at which homes without AC were predicted to lack AC or homes that were not tooCold were predicted to be not tooCold.

True positive rate, i.e., the rate at which homes with AC were predicted to have AC or homes that were tooCold were predicted to be tooCold.

Percent of the values predicted correctly by the model.

See Supplemental Material Table 2 for city-specific cenAC results, including results for a model threshold of 0.95

Figure 3.

Receiver operating curves (ROCs) for each of the 35 core-based statistical areas (CBSAs) with data available during the training period of 2003–2013 and the out-of-sample prediction period 2015–2017. The ROC refers to predicted probabilities of central air conditioning (A), room air conditioning (B), and home was uncomfortably cold (C). CDDs = cooling-degree days and HDDs = heating-degree days.

We were able to apply this model to City of Detroit residential parcel data, for which information about central or room AC is entirely absent, but other model variables are present. The predicted probability of central AC varies widely across the city (Figure 4A), with mean probabilities of central AC less than 0.4 in 14 of the 349 census tracts (Figure 5A). For any AC, low probabilities are more dispersed throughout the city than are the low probabilities of central AC (Figure 4B). If we consider census tracts as our administrative area of interest, four of the 349 census tracts have mean any AC probabilities less than 0.7 (Figure 5B).
Figure 4.

Model-predicted probability (Prob) of central air conditioning (AC) (A) or any (central or room) AC (B) by parcel (N = 390,668), Detroit, MI, 2016.

Figure 5.

Model-predicted probability (Prob) of central air conditioning (AC) (A) or any (central or room) AC (B) by tract, Detroit, MI, 2016.

DISCUSSION

Using American Housing Survey housing data, we successfully created predictive models of central and room AC that yielded predictions of central and room AC status in the hold-out sample better than if one was randomly assigning central and room AC status to parcels. For applications such as epidemiologic studies, where correctly identifying both AC and lack of AC are equally valuable, accuracy should be maximized. For these applications, a threshold of 0.5 for separating homes with AC from those without is appropriate. At this threshold, homes without central AC were correctly identified in approximately 63% of the parcels without central AC (specificity) and homes with central AC were correctly identified in 91% of the parcels with central AC (sensitivity). In contrast, for room AC, at a threshold maximizing accuracy, specificity was high (94%), but sensitivity was low. For applications where specificity may be more important, i.e., in screening parcels for lack of AC, a model threshold of 0.9 resulted in a specificity of 95% for central AC and a specificity of 100% for room AC, that is, perfect identification of homes without room AC among the homes that were indeed without room AC. However, at this threshold of 0.9, sensitivity for room AC was only 1%. Characteristics predicting central AC were often predictive of room AC but with opposite effect. For example, housing value and CDDs predicted a higher odds of central AC ownership but a lower odds of room AC ownership while the opposite was true for rental and mobile home units. Central AC and room AC ownership were inversely related, and it’s likely that households that lack central AC purchase room AC units to compensate for a lack of central AC. However, our room AC variable did not include information on the number, use or effectiveness of the room AC units, and room AC has been shown to be less effective than central AC at lowering indoor temperatures in prior research (24). Therefore, central AC may be a more useful predictor of heat vulnerability than room AC. In contrast to the models for central and room AC, the model for uncomfortably cold indoor winter temperatures did not provide good validation summary statistics in the hold-out sample, and we would not recommend using the model based on 2003–2013 housing characteristics to attempt to predict uncomfortably cold indoor winter temperatures in subsequent years. The uncomfortably cold model may not have validated well because of stark changes over time in the relationships between the independent variables and self-reported perceptions of uncomfortably cold indoor winter temperatures. Given that the construct of primary interest is housing with chronic under-heating problems, data sets using actual indoor temperatures and information on weatherization and utility usage rather than self-reported discomfort may be better suited to predicting under-heating in the winter. Despite better-than-random performance of the central and room AC models, neither central nor room AC are perfectly predicted on the basis of the age of the home, market value or tenure. These models are suitable to be used in studies estimating the effects of AC ownership when other options for assigning AC exposure are not available, but the respective central and room AC uncertainties should be taken into account. When additional characteristics that may predict AC ownership beyond those used in our models are available in parcel records, we recommend that users construct and validate new predictive models with these additional characteristics. Other statistical techniques, including multiple imputation, may be more appropriate depending on the quantity and missingness of the housing data available to the analyst. Another limitation is that although AC ownership is predicted by these models, AC use is not. Lacking the financial resources to operate an air conditioner is likely a substantial barrier to home cooling (13–18, 25). Cognitive impairment, having medical conditions aggravated by AC use, concerns about energy efficiency, and additional barriers to resources related to racial discrimination and neighborhood of residence (13, 18) may also limit home cooling. Further research and action is needed to quantify socio-economic drivers of air conditioning usage and reduce racial disparities in access to cool spaces. Additionally, we did not have information on indoor “uncomfortably warm temperatures” from the American Housing Survey. The U.S. Energy Information Administration’s Residential Energy Consumption Survey (RECS) does include responses on summer indoor temperatures when someone is and is not home as well as air conditioning usage (26), although information on the respondent’s comfort level is not available and sample sizes are smaller (the total number of responding households nationally was 5,686 in the 2015 RECS (27)). In future research, air conditioning usage and indoor temperatures could be modeled using household occupant and building characteristics from RECS or other surveys, as new years of data become available. Such research could advance our ability to predict indoor summer heat exposure for epidemiologic research and heat vulnerability screening. To demonstrate the utility of the AC models, we applied the models to City of Detroit parcel data, from which information on AC ownership is entirely lacking. Room AC appeared fairly evenly dispersed across the city, but central AC ownership by census tract was more heterogeneous. Several of the census tracts with low central AC prevalence are in Southwest Detroit in an area of the city known for high levels of ambient air pollution given the presence of an oil refinery, steel mills, a wastewater treatment facility, a coal burning power plant, and truck traffic across the nearby international U.S.-Canadian border (28). That these homes also lack the air filtration offered by AC units (7) may increase personal exposure to these air pollutants. Furthermore, these areas of the county experience high outdoor and land-surface temperatures due in part to high levels of heat-retaining surfaces (29–31), thereby also increasing personal exposure to high summer temperatures. Efforts to reduce heat and air pollution exposures, such as green roofs (32) or weatherization interventions (33), may be particularly impactful in these areas of the city. In general, both heat and air pollution exposures disproportionately affect communities of color and the economically disadvantaged (34, 35), further motivating research and action addressing the independent and cumulative effects of these exposures to reduce disparities in heat- and air pollution-related health effects (13, 36). In examining the AHS sample as a whole, we did see that uncomfortably cold indoor winter temperature was associated with central AC and, to a lesser extent, any AC, confirming that homes that are uncomfortably cold may also lack AC and may require weatherization measures for both summer and winter temperatures (Table 5). In cities such as Detroit, where weatherization measures currently focus on keeping indoor temperatures warmer in winter, additional measures, such as education on keeping homes cool in the summer or AC installation, may also be appropriate to help these same residents adapt to a warming climate.
Table 5.

Cross tabulations of central air conditioning presence (cenAC) or any air conditioning (central or room, anyAC) and “home was uncomfortably cold for 24 hours or more” (tooCold) and the odds of tooCold among those without vs. with AC e(or, identically, the odds of no cenAC among those tooCold vs. not tooCold) from the 2003–2017 American Housing Survey.

tooColdnot tooColdOdds Ratio (95% Confidence Interval)
no cenAC4.2%27.7%2.13 (2.07, 2.18)
cenAC4.5%63.7%
no anyAC1.4%10.1%1.57 (1.52, 1.63)
anyAC7.2%81.3%
In conclusion, central AC and room AC were reasonably predicted by housing value, year built, climate, and tenure. Future U.S. epidemiologic studies and heat vulnerability maps may reliably use the central or room AC models, or similar models, with readily available parcel-level data to predict AC ownership when AC ownership information is not available from other sources. However, users should validate or amend this model or use alternative modeling strategies when additional housing information is available. Outside of the U.S., where AC prevalence is often lower (37), we recommend the development of region-specific models by adding air conditioning ownership and/or usage questions to national or regional surveys, particularly as air conditioning ownership increases (37). These efforts will improve understanding of mortality and morbidity risk and the spatial patterning of homes without AC to prioritize weatherization or utility assistance and heat-wave preparedness measures.
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Authors:  Kazuhiko Ito; Kathryn Lane; Carolyn Olson
Journal:  Epidemiology       Date:  2018-11       Impact factor: 4.822

3.  Staying cool in a changing climate: Reaching vulnerable populations during heat events.

Authors:  Natalie R Sampson; Carina J Gronlund; Miatta A Buxton; Linda Catalano; Jalonne L White-Newsome; Kathryn C Conlon; Marie S O'Neill; Sabrina McCormick; Edith A Parker
Journal:  Glob Environ Change       Date:  2013-04       Impact factor: 9.523

4.  Adverse health effects of particulate air pollution: modification by air conditioning.

Authors:  Michelle L Bell; Keita Ebisu; Roger D Peng; Francesca Dominici
Journal:  Epidemiology       Date:  2009-09       Impact factor: 4.822

5.  MI-Environment: Geospatial patterns and inequality of relative heat stress vulnerability in Michigan.

Authors:  Patricia D Koman; Frank Romo; Peter Swinton; Graciela B Mentz; Ricardo F de Majo; Natalie R Sampson; Michael J Battaglia; Kimberly Hill-Knott; Guy O Williams; Marie S O'Neill; Amy J Schulz
Journal:  Health Place       Date:  2019-10-22       Impact factor: 4.078

6.  Modeling the residential infiltration of outdoor PM(2.5) in the Multi-Ethnic Study of Atherosclerosis and Air Pollution (MESA Air).

Authors:  Ryan W Allen; Sara D Adar; Ed Avol; Martin Cohen; Cynthia L Curl; Timothy Larson; L-J Sally Liu; Lianne Sheppard; Joel D Kaufman
Journal:  Environ Health Perspect       Date:  2012-02-22       Impact factor: 9.031

7.  Socio-cultural reflections on heat in Australia with implications for health and climate change adaptation.

Authors:  Cathy Banwell; Jane Dixon; Hilary Bambrick; Ferne Edwards; Tord Kjellström
Journal:  Glob Health Action       Date:  2012-10-16       Impact factor: 2.640

8.  Projections of temperature-attributable premature deaths in 209 U.S. cities using a cluster-based Poisson approach.

Authors:  Joel D Schwartz; Mihye Lee; Patrick L Kinney; Suijia Yang; David Mills; Marcus C Sarofim; Russell Jones; Richard Streeter; Alexis St Juliana; Jennifer Peers; Radley M Horton
Journal:  Environ Health       Date:  2015-11-04       Impact factor: 5.984

9.  Validating satellite-derived land surface temperature with in situ measurements: a public health perspective.

Authors:  Jalonne L White-Newsome; Shannon J Brines; Daniel G Brown; J Timothy Dvonch; Carina J Gronlund; Kai Zhang; Evan M Oswald; Marie S O'Neill
Journal:  Environ Health Perspect       Date:  2013-06-07       Impact factor: 9.031

10.  Air-quality-related health impacts from climate change and from adaptation of cooling demand for buildings in the eastern United States: An interdisciplinary modeling study.

Authors:  David W Abel; Tracey Holloway; Monica Harkey; Paul Meier; Doug Ahl; Vijay S Limaye; Jonathan A Patz
Journal:  PLoS Med       Date:  2018-07-03       Impact factor: 11.069

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1.  Development of a multidimensional housing and environmental quality index (HEQI): application to the American Housing Survey.

Authors:  Ami R Zota; Gary Adamkiewicz; MyDzung T Chu; Andrew Fenelon; Judith Rodriguez
Journal:  Environ Health       Date:  2022-05-24       Impact factor: 7.123

2.  Assessing the effects of disasters and their aftermath on pregnancy and infant outcomes: A conceptual model.

Authors:  Emily W Harville; Leslie Beitsch; Christopher K Uejio; Samendra Sherchan; Maureen Y Lichtveld
Journal:  Int J Disaster Risk Reduct       Date:  2021-06-24       Impact factor: 4.842

3.  Association between temperature exposure and cognition: a cross-sectional analysis of 20,687 aging adults in the United States.

Authors:  Anam M Khan; Jessica M Finlay; Philippa Clarke; Ketlyne Sol; Robert Melendez; Suzanne Judd; Carina J Gronlund
Journal:  BMC Public Health       Date:  2021-07-29       Impact factor: 3.295

  3 in total

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