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Article

Objectively Measured Built Environments and Cardiovascular Diseases in Middle-Aged and Older Korean Adults

1
Department of Nursing, Kkottongnae University, Cheongju 28211, Korea
2
Department of Mathematics, Hanyang University, Seoul 04763, Korea
3
Research Institute for Natural Sciences, Hanyang University, Seoul 04763, Korea
4
Department of Urban Planning and Engineering, Hanyang University, Seoul 04763, Korea
5
Department of Preventive Medicine, College of Medicine, Hanyang University, Seoul 04763, Korea
*
Author to whom correspondence should be addressed.
Int. J. Environ. Res. Public Health 2021, 18(4), 1861; https://doi.org/10.3390/ijerph18041861
Submission received: 18 January 2021 / Revised: 9 February 2021 / Accepted: 10 February 2021 / Published: 14 February 2021

Abstract

:
This study assesses the association between the objectively measured built environment and cardiovascular diseases (CVDs) in 50,741 adults from the Korean Community Health Survey. The CVD outcomes of hypertension, diabetes, dyslipidemia, stroke, and myocardial infarction (MI) or angina were derived from self-reported histories of physician diagnoses. Using ArcGIS software and Korean government databases, this study measured the built environment variables for the 546 administrative areas of Gyeonggi province. A Bayesian spatial multilevel model was performed independently in two age groups (i.e., 40–59 years or ≥60 years). After adjusting for statistical significant individual- and community-level factors with the spatial associations, living far from public transit was associated with an increase in the odds of MI or angina in middle-aged adults, while living in neighborhoods in which fast-food restaurants were concentrated was associated with a decrease in the odds of hypertension and stroke. For adults 60 or older, living farther from public physical-activity (PA) facilities was associated with a 15% increased odds for dyslipidemia, compared with living in neighborhoods nearer to PA facilities. These findings suggest that creating a built environment that provides more opportunities to engage in PA in everyday life should be considered a strategy to reduce the prevalence of CVD.

1. Introduction

Cardiovascular disease (CVD) has remained the leading cause of death worldwide, including in the Republic of Korea, despite a marked decrease in incidence rates in recent decades [1]. In 2016, CVD accounted for 31% of all deaths globally [2] and for 15% of all-age, all-cause, disability-adjusted life-years (DALYs) in 2017 [1]. A total of 61,009 Koreans died from CVD in 2018 and it accounted for 20.4% of all deaths [3]. Moreover, DALYs per 100,000 Korean population for CVD were 3475 (11.8%) in 2015 [4].
Although individual-level risk factors for CVD have been addressed, neighborhood-level risk factors that can reduce CVD and cardiovascular health disparities are now attracting attention [5]. Because previous studies of neighborhood-level risk factors focused largely on socioeconomic deprivation, social cohesion, air pollution, and traffic noise, little is known about the relationship between the built environment and cardiovascular health [5,6,7]. A systematic review of 18 studies revealed that density of food outlets (restaurants, supermarkets, or grocery stores) and highly walkable environments were associated with blood pressure of neighborhood residents [8]. Additionally, the influence of neighborhood walkability on hypertension and diabetes was confirmed in a meta-analysis of longitudinal studies [9]. Neighborhood walkability as measured by population density, street connectivity, and land-use mix (LUM) can encourage physical activity (PA) and reduce the risk of obesity, diabetes, hypertension, and dyslipidemia [8,9,10,11]. High volume of traffic, road proximity, and dense fast-food restaurants were associated with CVD, including coronary heart disease, stroke, myocardial infarction (MI), and angina [12,13]. Thus, previous studies indicate that PA-favorable neighborhood environment and food environment are related to CVD.
Although multiple studies have investigated the association between the built environment and cardiovascular health, the effects on hypertension, diabetes, dyslipidemia, stroke, MI, and angina have received much less attention than obesity [5,8,9]. Diverse research on the relationship between built environment and CVD beyond obesity is needed to develop more effective CVD prevention strategies for the population. Additionally, few studies have used specific environmental attributes such as street connectivity, population density, and land-used mix. Most assessed combined environmental measures such as walkability and urban sprawl [8,9]. More research is therefore required on whether specific attributes of the built environment are related to CVD.
A lack of knowledge on the relationship between the built environment and CVD prompted this study of the relationship between objective measures of built environment and various CVDs including hypertension, diabetes, dyslipidemia, stroke, MI, and angina.

2. Methods

Study Participants

Participants in this study were part of the Korean Community Health Survey (KCHS) in 2013 and 2014 [14], an annual nationwide and community-based cross-sectional survey of 230,000 adults aged ≥19 years old. The protocols of the KCHS were approved by the Institutional Review Board of the Korea Centers for Disease Control and Prevention (2013-06EXP-01-3C and 2014-08EXP-09-4C-A) before data collection. Written informed consent was obtained from all participants. Trained interviewers conducted face-to-face computer-assisted individual interviews using a standardized questionnaire in the participants’ homes [14]. The present study used data drawn from the KCHS in Gyeonggi province in 2013 and 2014. The province, which surrounds the South Korean capital of Seoul, represents approximately 10.2% of the total land area and approximately 24% of the total population. Gyeonggi province is a mix of urban and rural areas, consisting of 546 administrative districts in 2013, with an average population of approximately 28,000 residents living in each administrative district. In the current study, we excluded data with incomplete information (n = 4387), participants under 40 years of age (n = 27,074), and those who were in bed all day and therefore had little involvement in social activities (n = 217). A total of 50,741 participants aged 40 years or older were analyzed.

3. Measures

3.1. Cardiovascular Disease

A self-reported history of a physician’s diagnosis of hypertension, diabetes, dyslipidemia, stroke, MI, or angina constituted CVD for the purposes of this study. KCHS collects data using a standardized questionnaire developed by Korea Centers for Disease Control and Prevention [14]. Quality control of the data is conducted every year [14], and reliability and validity of self-reports were assessed [15,16]. Participants who responded “yes” to the item “Have you ever been diagnosed with hypertension by a doctor?” were assigned to the hypertension group. Diabetes was identified by a response of “yes” to the item “Have you ever been diagnosed with diabetes by a doctor?” Dyslipidemia was identified by a response of “yes” to the item “Have you ever been diagnosed with dyslipidemia, including hyperlipidemia, by a doctor?” Stroke was identified by a response of “yes” to the item “Have you ever been diagnosed with stroke by a doctor?” Participants who responded “yes” to “Have you ever been diagnosed with MI or angina?” were assigned to the MI or angina group.

3.2. Built Environment

This study measured built environment variables using a geographic information system. Metrics included population; density of public physical-activity (PA) facilities, public parks, and fast-food restaurants; proximity to public PA facilities (e.g., athletic or football fields, tennis courts, or swimming pools), parks, and public transit (e.g., subway stations or bus stops); street connectivity; residential density; commercial density; industrial density; and land-use mix (Table 1). Korean government databases (i.e., Population Census 2013, National Public Physical-Activity Facility Database 2013, National Building Database 2013, and Korean Transport Database 2013) and ArcGIS software were used to measure the built environments of the 546 administrative districts (the smallest administrative spatial unit) of Gyeonggi province.
First, population density was calculated by dividing the total population by the area of urbanized land. This study classified the urbanized areas of each administrative district excluding highland and watershed areas and natural open spaces. The density of PA facilities was the area of PA facilities divided by the population. The density of public parks was expressed as the area of public parks divided by the population. The density of fast-food restaurants was calculated as the number of fast-food restaurants divided by the urbanized area. After forming 100 × 100 m grids in the urbanized areas, proximity to public PA facilities, parks, and public transit was calculated as the average Euclidean distance between the centers of each grid and the nearest destination. Street connectivity was calculated as the number of three- or four-way intersections divided by the urbanized area. Next, this study calculated land-use density measures of residential, commercial, and industrial uses. Residential density was calculated as the residential building floor areas divided by the urbanized area excluding mountains, watershed, and natural open spaces. Commercial and industrial density measures were calculated as the building floor area of each land-use category divided by the urbanized area. This study calculated the land-use mix (LUM) based on floor area of residential, commercial, and industrial buildings [17]. As an entropy index, LUM values close to 1 indicated the highest heterogeneity of land-use. Due to the non-linear effects of the built environment on CVDs, all built-environment variables were categorized into three groups according to tertile distribution.

3.3. Covariates

Covariates included individual factors such as socio-demographic characteristics, health behaviors, and health status that were obtained from the KCHS. Sex (male or female), age (40–59 years or ≥60 years), education (≤high school diploma or ≥college), household income (<3 million won per month or ≥3 million won per month), job (non-manual job, manual job, or other), living alone, one-person household (no or yes), and residence period (<20 years or ≥20 years) were assessed as the socio-demographic characteristics. Smoking (never, former smoker), alcohol drinking (never, former, or current), sleeping duration (<7 h per day or ≥7 h per day), participation in moderate or vigorous physical activity (no or yes), and level of dietary sodium (high, middle, or low) were assessed. Subjective health (poor or good), perception of stress (no or yes), symptoms of depression (no or yes), and obesity (<25.0 kg/m2 or ≥25.0 kg/m2) were assessed as health status variables.

4. Statistical Analyses

Statistical analyses were conducted independently in two age groups (40–59 years and ≥ 60 years). We examined the effects of the individual factors on CVD. Conditioning the significant individual factors, we examined the effects of the built environmental factors on CVD. Univariable analyses were performed by using logistic regression models. Multivariable logistic regression models were performed to identify significant individual and built-environment factors [18].
A Bayesian spatial multilevel model was considered to investigate the relationship between the built environment and CVD [18,19,20]. The model was designed to account for complex spatially dependent structures, which mean spatial associations between adjacent geographical areas. The series of models is described in full in Appendix A. Model 1 contained only the intercept; Model 2 contained statistically significant individual factors; Model 3 contained statistically significant built-environmental factors as well as significant individual factors; and Model 4 contained spatially dependent structures, along with significant individual and built-environmental factors, to explain the additional spatial-dependent random variation not captured by neighborhood- and individual-level factors. The spatially dependent component followed a conditional autoregressive distribution [21] that assumed that the random component at a specific area correlated with those in the adjacent neighborhoods. All models included spatially independent random components to account for the spatially independent variation.
In fitting these models, integrated nest Laplace approximation (INLA) as Bayesian estimation methods was performed using the R-INLA package [22] for the computational efficiency. Non-informative priors were considered for all the parameters. The best model was Model 4 based on a deviance information criterion (DIC) [23], which is the goodness-of-fit measure in the Bayesian model comparison (Appendix A). In Model 4, the spatial fraction was computed to determine the extent to which the unexplained spatial variation was associated with geographical location (Appendix A). A spatial fraction close to 1 indicated dominance of the spatial effect [24].

5. Results

Table 2 shows the prevalence of CVDs and the general characteristics of the study participants. More than half were female (53.6%), 40–59 years old (65.9%), and had more than a high school diploma (70.2%). Approximately 28.5% of participants had hypertension and approximately 17% had dyslipidemia, followed by 11.3% for diabetes. The prevalence of stroke and MI/angina were approximately 2% and 3.2%, respectively. Figure 1 provides the spatial variations of CVDs by age group (i.e., 40–59 years and ≥60 years). Hypertension, diabetes, and dyslipidemia were more prevalent among those 40–59 years old than among those 60 or older, while stroke and MI/angina were more common in participants 60 years or older.
The association between CVD and the built environment in adults aged 40–59 years is provided in Table 3. Hypertension was negatively associated with fast-food restaurant density (odds ratio (OR) = 0.91, 95% confidence interval (CI) = 0.84–0.99 for T2 vs. T1). Diabetes was associated with population density, proximity to public park, and residential density, while dyslipidemia was associated with population density, fast-food restaurant density, and proximity to public PA facilities in univariable analysis. However, no built-environment factors significantly influenced diabetes or dyslipidemia in multivariable analysis. Stroke in participants 40–59 years old was negatively associated with fast-food restaurant density (OR = 0.58, 95% CI = 0.41–0.83 for T2 vs. T1; OR = 0.64, 95% CI = 0.44–0.92 for T3 vs. T1). In addition, living in a neighborhood with middle-level distances to public transit was associated with a 36% increase in the odds of diagnosis of MI or angina in adults aged 40–59 compared with those living in a neighborhood with close access to public transit (OR = 1.36, 95% CI = 1.07–1.74 for T2 vs. T1).
The association between CVDs and the built environment in adults ≥60 years is provided in Table 4. Hypertension, stroke, and MI/angina for those 60 and older were not associated with built-environment factors, while diabetes was associated with LUM (OR = 1.11, 95% CI = 1.01–1.23 for T2 vs. T1; OR = 1.13, 95% CI = 1.02–1.24 for T3 vs. T1). Although dyslipidemia was associated with most of built-environment factors in univariable analysis, the association was statistically significant only for the influence of distance to PA facilities. Living in a neighborhood farther from public PA facilities was associated with a 15% increased odds for dyslipidemia diagnosis in adults 60 or older compared with those living in a neighborhood with close access to public PA facilities (OR = 1.15, 95% CI = 1.01–1.30 for T2 vs. T1)

6. Discussion

The current study assessed the relationship between the objectively measured built environment and various CVDs, including hypertension, diabetes, dyslipidemia, stroke, and MI or angina among middle-aged and older Korean adults. The main finding of this study was that the proximity to public transit was positively associated with MI/angina in adults aged 40–59, while the density of fast-food restaurants was inversely associated with hypertension and stroke. For adults 60 and older, distance to public PA facilities and LUM were significantly associated with dyslipidemia and diabetes, respectively.
These results build on previous findings regarding the relationship between built environments favorable for PA and CVD. The current study found that the proximity to public transit was associated with MI/angina in adults aged 40–59 who actively engaged in social activities. A lack of previous studies on the relationship between public transit and MI/angina precluded any firm conclusions. However, one possible explanation is that the proximity to public transportation encouraged residents to walk to such transport locales [25], which could lead to reduced adiposity and MI/angina. A recent study on the association between public transportation and cardiometabolic health reported that public transportation was associated with modestly lower adiposity rates, because it provided an opportunity to incorporate PA into a journey [26]. A study of commuting modes and CVD mortality involving 394,746 participants who were followed for more than 25 years reported that rail commuters had a 21% lower rate of CVD mortality compared with motor-vehicle commuters [27]. In line with previous studies, our findings support that the proximity to public transit options promotes physically active lifestyles and protects against the development of adiposity and MI/angina in adults aged 40–59. The proximity of PA facilities was significantly associated with dyslipidemia in people aged 60 or older who tend to remain in their neighborhood due to presence of other retirees. Two previous studies of Australian adults reported no association between the built environment and dyslipidemia [28,29]. One study of 78,023 Toronto, Canada residents reported significant differences in the mean high-density lipoprotein levels between the highest and lowest walkability quartiles in adults older than 40; the difference was attributed to a PA effect [10]. The findings in this study expand on previous evidence by adding age-specific associations between the PA-favorable built environments (i.e., proximity of public transit and PA facilities) and certain CVDs (i.e., dyslipidemia and MI/angina).
The reason why a high density of fast-food restaurants was negatively associated with hypertension and stroke is unclear. Very little is known about the association between the density of fast-food restaurants and hypertension or stroke. A study of more than four million Swedes between 35 and 80 years of age reported a statistically significant association between fast-food restaurants and stroke, although the ORs of the association were not large [12]. In addition, a study from the United States showed a significantly positive association between fast-food restaurants and mortalities related to CVD and stroke [30]. However, a longitudinal study from Australia found no association between the food environment and hypertension [28]. Even a study of 40,398 residents in a rural state in the United States reported an inverse association between fast-food restaurants and CVD health behaviors [31]. Our findings can be explained by a lack of association between proximity to fast-food restaurant and actual fast-food consumption, particularly among middle-aged Asians. Increased age was associated with less frequent consumption of fast-food even considering proximity to and coverage of fast-food restaurants [32]. In addition, spatial distribution data suggest that the prevalence of hypertension and stroke were high in remote areas, which are less urbanized. As a substitute for urbanization, therefore, fast-food restaurants may be related to hypertension and stroke. This unexpected finding raises the need for future replicated studies and longitudinal studies of the association between fast-food restaurants and CVDs.
The present study found that higher LUM was associated with greater prevalence of diabetes in adults aged 60 or over. Previous studies have supported that high-level LUM encourages participation in physical activity due to better access to local destinations that help reduce obesity and diabetes [33,34,35]. The elderly, who are more sensitive to stress from their residence environments, might be exposed to higher levels of stresses when living in areas with mixed residential, commercial, and industrial land-use, usually located in urban centers [36,37]. In addition, there might confounding factors that were not measured in this study, such as noise and traffic volume [6]. Explanations for the present findings warrant further study on the potential positive and negative effects of LUM on elderly health.
A major strength of the current study is that it assessed the relationship between the objectively measured built environment and various CVDs. It adjusted for sufficient individual-level covariates in the multilevel framework and considered spatial associations between adjacent geographical areas. The current study has some limitations. First, this study did not allow for a definition of causality association between the built environment and CVD due to a cross-sectional design. Second, although the current study adjusted for the residence period, residents may choose the neighborhoods they live in based on health-related characteristics. Third, because the data on health behaviors and CVDs were limited to self-reported responses in the 2013–2014 KCHS, recall bias cannot be ignored. Further study using medical records is needed. Fourth, although individual-level income was considered in the current study, neighborhood deprivation should be included in the future studies. Finally, various built-environment attributes were including in the current study, but the availability of healthcare facilities were not.

7. Conclusions

The present study supports an age-specific association between the objectively measured built environment (e.g., proximity to public PA facilities and public transit, LUM, and density of fast-food restaurants) and CVDs (hypertension, diabetes, dyslipidemia, stroke, and MI or angina) among middle-aged and older Korean adults. The findings indicate a PA-favorable neighborhood environment with access to public transit options and PA facilities may help reduce CVDs in middle-aged and older adults. The lack of a previous study of whether specific built-environment attributes are related to CVDs implies that similar studies should be conducted. Further examination of the spatial-temporal association is needed to better understand the causality of the relationship between the built environment and CVD.

Author Contributions

Conceptualization, E.Y.L.; methodology, E.Y.L. and J.C.; formal analysis, J.C.; data curation, S.L. and B.Y.C.; writing—original draft preparation, E.Y.L. and J.C.; writing—review and editing, E.Y.L., J.C., S.L. and B.Y.C.; visualization, S.L.; funding acquisition, E.Y.L. All authors have read and agreed to the published version of the manuscript.

Funding

This work was supported by a National Research Foundation of Korea grant funded by the Korean Government (No. 2020R1A2C1014449).

Institutional Review Board Statement

The protocols of the KCHS were approved by the Institutional Review Board of the Korea Centers for Disease Control and Prevention (2013-06EXP-01-3C and 2014-08EXP-09-4C-A) before data collection.

Informed Consent Statement

Written informed consent was obtained from all participants.

Data Availability Statement

Availability of KCHS data: https://chs.cdc.go.kr/chs/index.do (accessed on 18 January 2021).

Conflicts of Interest

The authors declare no conflict of interest.

Appendix A

Bayesian spatial multilevel model
We assume y k i is the binary CVD outcome of individual i   ( = 1 , , n k ) at neighborhood k   ( = 1 , , N ) , following a Bernoulli distribution with the probability having CVDs, p k i (Equations (A1) and (A2)):
y k i ~ B e r n o u l l i ( p k i ) ,
l o g i t ( p k i ) = log ( p k i 1 p k i ) = ψ k i .
In this study, each model specified ψ k i as follows.
(Model 1) ψ k i = α + u k
(Model 2) ψ k i = α + X k i β + u k
(Model 3) ψ k i = α + X k i β + E k γ + u k
(Model 4) ψ k i = α + X k i β + E k γ + u k + v k ,
where α is an intercept, X k i are individual factors, and E k are built-environmental factors with the corresponding coefficients β and γ , respectively. The random component u k ~ N ( 0 ,   σ u 2 ) explains the spatially uncorrelated effects of spatially independent variation. The random component v k explains the spatially correlated effects based on a conditional autoregressive distribution [10] (Equation (A3)):
v k | v j , j k   ~   N ( j w k j v j w k + , σ v 2 w k + ) , j , k = 1 , 2 , ,   N .
The neighborhood information w j k is 1 when the j th and k th regions are adjacent; otherwise, w j k =0. The number of the neighboring regions for the k th region is defined by w k + = w k j . The intercept α and fixed parameters β and γ are assigned non-informative prior values, N(0,10000). For the variance parameters σ v 2 and σ u 2 , the default priors in R-INLA [11] are used as log ( 1 / σ v 2 ) , log ( 1 / σ u 2 ) ~ logGamma(1,0.0005).
For the goodness-of-fit measure, the deviance information criterion (DIC) is considered as (Equation (A4)):
D I C = p D + D ( θ ) ¯ ,
where the vector of parameters is θ . The posterior mean of deviance is D ( θ ) ¯ , D ( θ ) = 2 log ( y | θ ) , and the model complexity is p D = D ( θ ) ¯ D ( θ ^ ) , and the posterior mean is θ ,   θ ^ . A smaller DIC value indicates better model fit.
In Model 4′s spatially uncorrelated and correlated components, the spatial fraction is defined by (Equation (A5)):
S F = σ v 2 σ u 2 + σ v 2 .

References

  1. GBD 2017 DALYs and HALE Collaborators. Global, regional, and national disability-adjusted life-years (DALYs) for 359 diseases and injuries and healthy life expectancy (HALE) for 195 countries and territories, 1990–2017: A systematic analysis for the Global Burden of Disease Study 2017. Lancet 2018, 392, 1859–1922. [Google Scholar] [CrossRef] [Green Version]
  2. World Health Organination. Cardiovascular Diseases (CVDs). 2017. Available online: https://www.who.int/news-room/fact-sheets/detail/cardiovascular-diseases-(cvds) (accessed on 13 August 2020).
  3. Statistics Korea. Cause of Death in 2018; Statistics Korea: Daejeon, Korea, 2018.
  4. Kim, Y.E.; Park, H.; Jo, M.W.; Oh, I.H.; Go, D.S.; Jung, J.; Yoon, S.J. Trends and patterns of burden of disease and injuries in Korea using disability-adjusted life years. J. Korean Med. Sci. 2019, 34, e75. [Google Scholar] [CrossRef]
  5. Diez Roux, A.V.; Mujahid, M.S.; Hirsch, J.A.; Moore, K.; Moore, L.V. The impact of neighborhoods on CV Risk. Glob. Heart 2016, 11, 353–363. [Google Scholar] [CrossRef] [Green Version]
  6. Clark, C.; Sbihi, H.; Tamburic, L.; Brauer, M.; Frank, L.D.; Davies, H.W. Association of Long-Term Exposure to Transportation Noise and Traffic-Related Air Pollution with the Incidence of Diabetes: A Prospective Cohort Study. Environ. Health Perspect. 2017, 125, 087025. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  7. Leal, C.; Chaix, B. The influence of geographic life environments on cardiometabolic risk factors: A systematic review, a mehtodological assessment and a research agenda. Obes. Rev. 2011, 12, 217–230. [Google Scholar] [CrossRef] [PubMed]
  8. Malambo, P.; Kengne, A.P.; De Villiers, A.; Lambert, E.V.; Puoane, T. Built Environment, Selected Risk Factors and Major Cardiovascular Disease Outcomes: A Systematic Review. PLoS ONE 2016, 11, e0166846. [Google Scholar] [CrossRef]
  9. Chandrabose, M.; Chandrabose, M.; Rachele, J.N.; Gunn, L.; Kavanagh, A.; Owen, N.; Turrell, G.; Giles-Corti, B.; Sugiyama, T. Built environment and cardio-metabolic health: Systematic review and meta-analysis of longitudinal studies. Obes. Rev. 2019, 20, 41–54. [Google Scholar] [CrossRef] [Green Version]
  10. Loo, C.K.; Greiver, M.; Aliarzadeh, B.; Lewis, D. Association between neighbourhood walkability and metabolic risk factors influenced by physical activity: A cross-sectional study of adults in Toronto, Canada. BMJ Open 2017, 7, e013889. [Google Scholar] [CrossRef]
  11. Dendup, T.; Feng, X.; Clingan, S.; Astell-Burt, T. Environmental Risk Factors for Developing Type 2 Diabetes Mellitus: A Systematic Review. Int. J. Environ. Res. Public Health 2018, 15, 78. [Google Scholar] [CrossRef] [Green Version]
  12. Hamano, T.; Kawakami, N.; Li, X.; Sundquist, K. Neighborhood environment and stroke: A follow-up study in Sweden. PLoS ONE 2013, 8, e56680. [Google Scholar] [CrossRef]
  13. Chum, A.; O’Campo, P. Cross-sectional associations between residential environmental exposures and cardiovascular diseases. BMC Public Health 2015, 15, 438. [Google Scholar] [CrossRef] [Green Version]
  14. Kang, Y.W.; Ko, Y.S.; Kim, Y.J.; Sung, K.M.; Kim, H.J.; Choi, H.Y.; Sung, C.; Jeong, E. Korea Community Health Survey Data Profiles. Osong Public Health Res. Perspect. 2015, 6, 211–217. [Google Scholar] [CrossRef] [Green Version]
  15. Choe, S.; Lee, J.; Lee, J.; Kang, D.; Lee, J.; Shin, A. Validity of self-reported stroke and myocardial infarction in Korea: The Health Examinees study. J. Prev. Med. Public Health 2019, 52, 377–383. [Google Scholar] [CrossRef]
  16. Kehoe, R.; Wu, S.; Leske, M.; Chylack, L. Comparing self-reported and physician-reported medical history. Am. J. Epidemiol. 1994, 139, 813–818. [Google Scholar] [CrossRef]
  17. Frank, L.D.; Pivo, G. Relationship Between Land Use and Travel Behavior in the Puget Sound Region; Washington State Department of Transportation: Olympia, WA, USA, 1994.
  18. Lee, E.Y.; Lee, S.; Choi, B.Y.; Choi, J. Influence of Neighborhood Environment on Korean Adult Obesity Using a Bayesian Spatial Multilevel Model. Int. J. Environ. Res. Public Health 2019, 16, 3991. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  19. Eastwood, J.G.; Jalaludin, B.B.; Kemp, L.A.; Phung, H.N.; Barnett, B.E.W. Immigrant maternal depression and social networks. A multilevel Bayesian spatial logistic regression in South Western Sydney, Australia. Spat. Spatio Temporal Epidemiol. 2013, 6, 49–58. [Google Scholar] [CrossRef]
  20. Wang, X.; Shao, C.; Yin, C.; Zhuge, C. Exploring the Influence of Built Environment on Car Ownership and Use with a Spatial Multilevel Model: A Case Study of Changchun, China. Int. J. Environ. Res. Public Health 2018, 15, 1868. [Google Scholar] [CrossRef] [Green Version]
  21. Besag, J. Spatial Interaction and the Statistical Analysis of Lattice Systems. J. R. Stat. Soc. 1974, 36, 192–236. [Google Scholar] [CrossRef]
  22. Rue, H.; Martino, S.; Lindgren, F.; Simpson, D.; Riebler, A.; Krainski, E. INLA: Functions Which Allow to Perform Full Bayesian Analysis of Latent Gaussian Models Using Integrated Nested Laplace Approximation. 2014. Available online: http://www.r-inla.org (accessed on 19 March 2020).
  23. Spiegelhalter, D.J.; Best, N.G.; Carlin, B.P.; Van Der Linde, A. Bayesian measures of model complexity and fit. J. R. Stat. Soc. 2002, 64, 583–639. [Google Scholar] [CrossRef] [Green Version]
  24. Dasgupta, P.; Cramb, S.M.; Aitken, J.F.; Turrell, G.; Baade, P.D. Comparing multilevel and Bayesian spatial random effects survival models to assess geographical inequalities in colorectal cancer survival: A case study. Int. J. Health Geogr. 2014, 13, 36. [Google Scholar] [CrossRef] [Green Version]
  25. Djurhuus, S.; Hansen, H.S.; Aadahl, M.; Glümer, C. The Association between Access to Public Transportation and Self-Reported Active Commuting. Int. J. Environ. Res. Public Health 2014, 11, 12632–12651. [Google Scholar] [CrossRef] [Green Version]
  26. Patterson, R.; Webb, E.; Hone, T.; Millett, C.; Laverty, A.A. Associations of public transportation use with cardiometabolic health: A systematic review and meta-analysis. Am. J. Epidemiol. 2019, 188, 785–795. [Google Scholar] [CrossRef]
  27. Patterson, R.; Panter, J.; Vamos, E.P.; Cummins, S.; Millett, C.; Laverty, A.A. Associations between commute mode and cardiovascular disease, cancer, and all-cause mortality, and cancer incidence, using linked Census data over 25 years in England and Wales: A cohort study. Lancet Planet. Health 2020, 4, e186–e194. [Google Scholar] [CrossRef]
  28. Paquet, C.; Coffee, N.T.; Haren, M.T.; Howard, N.J.; Adams, R.J.; Taylor, A.W.; Daniel, M. Food environment, walkability, and public open spaces are associated with incident development of cardio-metabolic risk factors in a biomedical cohort. Health Place 2014, 28, 173–176. [Google Scholar] [CrossRef]
  29. Muller-Riemenschneider, F.; Pereira, G.; Villanueva, K.; Christian, H.; Knuiman, M.; Giles-Corti, B.; Bull, F.C. Neighborhood walkability and cardiometabolic risk factors in Australian adults: An observational study. BMC Public Health 2013, 13, 755. [Google Scholar] [CrossRef] [Green Version]
  30. Mazidi, M.; Speakman, J.R. Association of fast-food and full-service restaurant densities with mortality from cardiovascular disease and stroke, and the prevalence of diabetes mellitus. J. Am. Heart Assoc. 2018, 7, e007651. [Google Scholar] [CrossRef] [Green Version]
  31. Briggs, A.C.; Black, A.W.; Lucas, F.L.; Siewers, A.E.; Fairfield, K.M. Association between the food and physical activity environment, obesity, and cardiovascular health across Maine counties. BMC Public Health 2019, 19, 374. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  32. Sharkey, J.R.; Johnson, C.M.; Dean, W.R.; Horel, S.A. Association between proximity to and coverage of traditional fast-food restaurants and non-traditional fast-food outlets and fast-food consumption among rural adults. Int. J. Health Geogr. 2011, 10, 37. [Google Scholar] [CrossRef] [Green Version]
  33. Amuda, A.T.; Berkowitz, S.A. Diabetes and the built environment: Evidence and policies. Curr. Diabetes Rep. 2019, 19, 35. [Google Scholar] [CrossRef]
  34. Kärmeniemi, M.; Lankila, T.; Ikäheimo, T.; Puhakka, S.; Niemelä, M.; Jämsä, T.; Koivumaa-Honkanen, H.; Korpelainen, R. Residential relocation trajectories and neighborhood density, mixed land use and access networks as predictors of walking and bicycling in the Northern Finland Birth Cohort 1966. Int. J. Behav. Nutr. Phys. Act. 2019, 16, 88. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  35. Bonaccorsi, G.; Manzi, F.; Del Riccio, M.; Setola, N.; Naldi, E.; Milani, C.; Giorgetti, D.; Dellisanti, C.; Lorini, C. Impact of the Built Environment and the Neighborhood in Promoting the Physical Activity and the Healthy Aging in Older People: An Umbrella Review. Int. J. Environ. Res. Public Health 2020, 17, 6127. [Google Scholar] [CrossRef] [PubMed]
  36. Grant, M.; Braubach, M. Evidence review on the spatial determinants of health in urban settings: Land use pattern. In Annex 2 in Urban Planning, Environment and Health: From Evidence to Policy Action; Meeting repot, 22-97; WHO Regional Office for Europe: Copenhagen, Denmark, 2010. [Google Scholar]
  37. Wu, Y.; Prina, A.M.; Jones, A.; Barnes, L.E.; Mattews, F.E.; Brayne, C.; MRC CFAS. Land use mix and five-year mortality in later life: Results from the Cognitive Function and Ageing Study. Health Place 2016, 38, 54–60. [Google Scholar] [CrossRef] [PubMed] [Green Version]
Figure 1. Spatial distribution of prevalence of cardiovascular diseases by age groups.
Figure 1. Spatial distribution of prevalence of cardiovascular diseases by age groups.
Ijerph 18 01861 g001
Table 1. The objectively measured built environment.
Table 1. The objectively measured built environment.
VariablesDefinitionsData SourcesMean (±SD)Min-Max
Population densityNumber of people per sq. km of urbanized area2013 Population Census of Statistics Korea227.6
(±398.5)
4.2–8067.8
Density of physical activity facilitiesAreas of physical activity facility per population2013 Public Physical Activity Facility Database of the Ministry of Culture, Sports, and Tourism23,145.9
(±55,203.8)
0.0–513,250.7
Density of public parksArea of public park per population451,898.2
(±3008,972.2)
0.0–76,659,160.8
Density of fast-food restaurantsNumber of fast-food restaurant per urbanized area2013 Building Database of the Ministry of Land, Infrastructure and Transport0.0
(±0.2)
0.0–3.5
Proximity to public physical activity facilitiesAverage distance between the 100 × 100 m grid center of urbanized areas and public physical activity facilities2013 Public Physical Activity Facility Database of the Ministry of Culture, Sports, and Tourism1444.6
(±1216.1)
205.3–9783.6
Proximity to public parksAverage distance between the 100 × 100 m grid center of urbanized areas and public parks709.3
(± 991.6)
39.9–6183.3
Proximity to public transitAverage distance between the 100 × 100 m grid center of urbanized areas and bus stops or subway stations2013 Transport Database of the Ministry of Land, Infrastructure and Transport282.2
(±206.4)
85.1–1751.6
Street connectivityNumber of three- or four-way intersections per urbanized area0.2
(±0.3)
0.0–2.9
Residential densityResidential building floor areas per urbanized area2013 Building Database of the Ministry of Land, Infrastructure and Transport11,734.0
(±53,103.4)
148.7–1,044,944.0
Commercial densityCommercial building floor areas per urbanized area2750.3
(±7652.3)
49.9–137,521.9
Industrial densityIndustrial building floor areas per urbanized area2305.9
(±6849.8)
49.7–128,049.5
Land-use mixResidential, commercial, and industrial building floor areas per urbanized area0.7
(±0.2)
0.0–1.0
Table 2. Characteristics of study participants.
Table 2. Characteristics of study participants.
VariablesTotalHypertensionDiabetesDyslipidemiaStrokeMI/Angina
Total, n50,741 (100)14,438 (28.5)5725 (11.3)8644 (17.0)1006 (2.0)1649 (3.2)
Male sex, n (%)23,549 (46.4)6923 (47.9)3013 (52.6)3717 (43.0)540 (53.7)906 (54.9)
40–59 years old, n (%)33,433 (65.9)5601 (38.8)2083 (36.4)4434 (51.3)186 (18.5)418 (25.3)
Education, ≤high school, n (%)35,632 (70.2)11,654 (80.7)4673 (81.6)6431 (74.4)861 (85.6)1344 (81.5)
Household income, <3 million won/month, n (%)23,482 (46.3)8672 (60.1)3580 (62.5)4649 (53.8)745 (74.1)1123 (68.1)
Job, non-manual job, n (%)10,674 (21.0)1721 (11.9)634 (11.1)1425 (16.5)45 (4.5)154 (9.3)
Job, manual job, n (%)20,264 (39.9)4977 (34.5)1865 (32.6)3043 (35.2)193 (19.2)459 (27.8)
Living alone (yes), n (%)4139 (8.2)1720 (11.9)670 (11.7)954 (11.0)133 (13.2)216 (13.1)
Residence period, <20 years, n (%)27,153 (53.5)6497 (45.0)2516 (43.9)4309 (49.8)464 (46.1)736 (44.8)
Former smokers, n (%)9693 (19.1)3417 (23.7)1448 (25.3)1874 (21.7)325 (32.3)505 (30.6)
Current smokers, n (%)10,509 (20.7)2414 (16.7)1123 (19.6)1479 (17.1)143 (14.2)292 (17.7)
Former drinkers, n (%)6790 (13.4)2392 (16.6)1152 (20.1)1347 (15.6)279 (27.7)379 (23.0)
Current drinkers, n (%)34,807 (68.6)8572 (59.4)3119 (54.5)5452 (63.1)442 (43.9)829 (50.3)
Sleeping duration, ≥7 h/day, n (%)24,906 (49.1)6974 (48.3)2897 (50.6)3938 (45.8)510 (50.7)783 (47.5)
Moderate or vigorous physical activity (yes), n (%)32,589 (64.2)9204 (63.7)3537 (61.8)5460 (63.2)590 (58.6)991 (60.1)
Low-sodium diet, n (%)13,583 (26.8)4012 (27.8)1670 (29.2)2398 (27.7)299 (29.7)469 (28.4)
High-sodium diet, n (%)12,054 (23.8)3890 (26.9)1488 (26.0)2209 (25.6)270 (26.8)485 (29.4)
Subjective health (good), n (%)40,841 (80.5)9535 (66.0)3108 (54.3)5926 (68.6)335 (33.3)783 (47.5)
Stress perception (yes), n (%)13,469 (26.5)3819 (26.5)1570 (27.4)2500 (28.9)314 (31.2)453 (27.5)
Depressive symptom (yes), n (%)3600 (7.1)1172 (8.1)549 (9.6)855 (9.9)132 (13.1)197 (11.9)
Obesity (≥25.0 kg/m2), n (%)13,917 (27.4)5563 (38.5)2197 (38.4)3420 (39.6)337 (33.5)565 (34.3)
Diabetes (yes), n (%)5725 (11.3)3479 (24.1) 2095 (24.2)294 (29.2)516 (31.3)
Hypertension (yes), n (%)14,438 (28.5) 712 (4.9)972 (6.7)
Dyslipidemia (yes), n (%)8644 (17.0) 331 (3.8)713 (8.2)
n (%) = numbers and percentages. MI = myocardial infarction.
Table 3. Association between cardiovascular diseases and built environments in adults aged 40–50 years.
Table 3. Association between cardiovascular diseases and built environments in adults aged 40–50 years.
Built EnvironmentsHypertension aDiabetes bDyslipidemia cStroke dMI/angina e
UnivariableMultivariableUnivariableMultivariableUnivariableMultivariableUnivariableMultivariableUnivariableMultivariable
OR
95%CI
OR
95%CI
OR
95%CI
OR
95%CI
OR
95%CI
OR
95%CI
OR
95%CI
OR
95%CI
OR
95%CI
OR
95%CI
Population density
T1 (lowest)1 11111 1
T20.97
(0.90, 1.05)
0.83
(0.74, 0.93)
0.87
(0.71, 1.06)
1.10
(1.01, 1.19)
1.03
(0.89, 1.21)
0.79
(0.55, 1.15)
0.90
(0.71, 1.16)
T3 (highest)0.97
(0.90, 1.05)
0.90
(0.80, 1.01)
0.98
(0.77, 1.26)
1.05
(0.96, 1.14)
0.96
(0.80, 1.15)
0.96
(0.67, 1.39)
0.87
(0.68, 1.12)
Density of physical activity facilities
T1 (lowest)1 1 1 1 1
T20.94
(0.87, 1.01)
0.91
(0.81, 1.03)
1.00
(0.92, 1.09)
0.97
(0.64, 1.44)
1.12
(0.87, 1.43)
T3 (highest)1.03
(0.96, 1.11)
1.01
(0.90, 1.12)
0.99
(0.91, 1.07)
1.38
(0.98, 1.96)
1.10
(0.86, 1.39)
Density of public parks
T1 (lowest)1 1 1 1 1
T20.99
(0.92, 1.07)
0.96
(0.86, 1.08)
0.99
(0.91, 1.07)
1.01
(0.71, 1.45)
1.04
(0.82, 1.33)
T3 (highest)0.99
(0.91, 1.06)
1.04
(0.93, 1.17)
1.00
(0.92, 1.09)
0.89
(0.62, 1.30)
1.05
(0.82, 1.35)
Density of fast-food restaurants
T1 (lowest)111 11111
T20.91
(0.84, 0.98)
0.91
(0.84, 0.99)
0.95
(0.84, 1.06)
1.04
(0.95, 1.13)
1.02
(0.90, 1.16)
0.58
(0.41, 0.83)
0.58
(0.41, 0.83)
1.12
(0.87, 1.44)
T3 (highest)0.92
(0.85, 1.00)
0.93
(0.86, 1.02)
0.98
(0.87, 1.11)
1.10
(1.01, 1.20)
1.08
(0.94, 1.25)
0.64
(0.44, 0.92)
0.64
(0.44, 0.92)
1.03
(0.79, 1.35)
Proximity to public physical activity facilities
T1 (nearest)1 1 111 1
T21.00
(0.93, 1.08)
1.02
(0.92, 1.14)
0.95
(0.88, 1.02)
0.96
(0.86, 1.08)
0.99
(0.70, 1.40)
0.98
(0.78, 1.24)
T3 (farthest)1.01
(0.93, 1.09)
1.08
(0.96, 1.22)
0.91
(0.84, 0.99)
0.92
(0.78, 1.08)
1.01
(0.70, 1.47)
1.03
(0.80, 1.33)
Proximity to public parks
T1 (nearest)1 111 1 1
T20.98
(0.92, 1.06)
0.99
(0.88, 1.11)
1.01
(0.89, 1.13)
0.98
(0.91, 1.06)
0.78
(0.54, 1.12)
1.11
(0.88, 1.41)
T3 (farthest)1.03
(0.95, 1.11)
1.13
(1.00, 1.26)
1.05
(0.85, 1.28)
0.93
(0.86, 1.02)
1.05
(0.74, 1.50)
1.11
(0.86, 1.43)
Proximity to public transit
T1 (nearest)1 1 1 1 11
T21.00
(0.94, 1.08)
1.00
(0.90, 1.11)
1.01
(0.94, 1.09)
0.98
(0.70, 1.39)
1.41
(1.11, 1.80)
1.36
(1.07, 1.74)
T3 (farthest)0.99
(0.92, 1.07)
1.01
(0.90, 1.14)
0.99
(0.91, 1.08)
0.95
(0.65, 1.38)
1.22
(0.94, 1.60)
1.09
(0.81, 1.46)
Street connectivity
T1 (lowest)1 1 1 1 11
T20.95
(0.88, 1.03)
1.00
(0.89, 1.12)
1.01
(0.93, 1.10)
0.91
(0.64, 1.31)
0.92
(0.72, 1.17)
0.93
(0.72, 1.20)
T3 (highest)0.95
(0.88, 1.02)
0.94
(0.83, 1.06)
1.06
(0.97, 1.15)
0.83
(0.57, 1.21)
0.75
(0.58, 0.97)
0.77
(0.58, 1.02)
Residential density
T1 (lowest)1 111 1 1
T20.98
(0.91, 1.05)
0.86
(0.77, 0.97)
0.98
(0.79, 122)
1.05
(0.97, 1.14)
0.73
(0.51, 1.05)
0.93
(0.74, 1.18)
T3 (highest)0.96
(0.89, 1.04)
0.90
(0.80, 1.01)
0.95
(0.73, 1.22)
1.06
(0.97, 1.16)
0.96
(0.66, 1.38)
0.86
(0.66, 1.11)
Commercial density
T1 (lowest)1 1 1 1 1
T20.97
(0.90, 1.04)
0.91
(0.81, 1.02)
1.06
(0.98, 1.15)
0.79
(0.55, 1.12)
1.01
(0.80, 1.29)
T3 (highest)0.99
(0.92, 1.07)
0.90
(0.80, 1.01)
1.04
(0.95, 1.13)
0.86
(0.60, 1.25)
0.87
(0.67, 1.13)
Industrial density
T1 (lowest)1 1 1 1 1
T20.99
(0.92, 1.07)
0.90
(0.81, 1.01)
1.07
(0.99, 1.16)
1.02
(0.71, 1.46)
0.95
(0.75, 1.20)
T3 (highest)1.01
(0.93, 1.09)
0.93
(0.83, 1.05)
1.08
(0.99, 1.18)
1.14
(0.79, 1.65)
0.79
(0.61, 1.02)
Land-use mix
T1 (lowest)111 1 1 1
T21.02
(0.95, 1.10)
1.02
(0.95, 1.10)
0.98
(0.88, 1.10)
1.05
(0.97, 1.14)
0.89
(0.61, 1.30)
0.88
(0.69, 1.13)
T3 (highest)1.08
(1.00, 1.16)
1.07
(0.99, 1.16)
1.11
(0.99, 1.25)
1.01
(0.93, 1.10)
1.15
(0.81, 1.65)
1.07
(0.84, 1.36)
Spatial fraction 0.515 0.473 0.651 0.487 0.518
Univariable and multivariable analyses were adjusted for significant individual variables: (a) adjusted for sex, education, household income, job, living alone, residence period, smoking, sleeping duration, level of dietary sodium, subjective health, perception of stress, symptoms of depression, obesity, and diabetes; (b) adjusted for sex, education, household income, job, living alone, residence period, smoking, alcohol drinking, level of dietary sodium, subjective health, perception of stress, symptoms of depression, and obesity; (c) adjusted for sex, education, household income, job, living alone, residence period, smoking, alcohol drinking, sleeping duration, participation in moderate or vigorous physical activity, level of dietary sodium, subjective health, perception of stress, symptoms of depression, obesity, and diabetes; (d) adjusted for sex, education, household income, job, living alone, residence period, smoking, alcohol drinking, subjective health, perception of stress, symptoms of depression, obesity, diabetes, hypertension, and dyslipidemia; (e) adjusted for sex, education, household income, job, residence period, smoking, alcohol drinking, participation in moderate or vigorous physical activity, level of dietary sodium, subjective health, perception of stress, symptoms of depression, obesity, diabetes, hypertension, and dyslipidemia. Multivariable analysis was performed using a Bayesian spatial multilevel model and adjusted for significant individual variables. MI = myocardial infarction; OR = odds ratio; CI = confidence interval. Significant association in bold as p < 0.05 and p < 0.001.
Table 4. Association between cardiovascular diseases and built environments in adults aged 60 years or older.
Table 4. Association between cardiovascular diseases and built environments in adults aged 60 years or older.
Built EnvironmentsHypertension aDiabetes bDyslipidemia cStroke dMI/angina e
UnivariableMultivariableUnivariableMultivariableUnivariableMultivariableUnivariableMultivariableUnivariableMultivariable
OR
95%CI
OR
95%CI
OR
95%CI
OR
95%CI
OR
95%CI
OR
95%CI
OR
95%CI
OR
95%CI
OR
95%CI
OR
95%CI
Population density
T1 (lowest)1 1 11111
T2 0.96
(0.89, 1.03)
0.95
(0.86, 1.03)
1.12
(1.02, 1.22)
0.89
(0.73, 1.10)
0.79
(0.66, 0.94)
0.83
(0.67, 1.04)
0.99
(0.86, 1.14)
T3 (highest)0.95
(0.88, 1.03)
0.98
(0.89, 1.08)
1.20
(1.10, 1.31)
0.90
(0.70, 1.16)
1.03
(0.87, 1.23)
1.02
(0.78, 1.32)
0.95
(0.82, 1.10)
Density of physical activity facilities
T1 (lowest)1 1 1 1 1
T2 0.96
(0.89, 1.03)
1.01
(0.91, 1.11)
1.01
(0.92, 1.10)
1.19
(0.99, 1.44)
0.97
(0.83, 1.13)
T3 (highest)1.02
(0.96, 1.10)
1.02
(0.93, 1.11)
0.93
(0.85, 1.01)
1.05
(0.88, 1.25)
0.93
(0.81, 1.07)
Density of public parks
T1 (lowest)1 1 1 1 1
T2 1.01
(0.93, 1.09)
0.98
(0.89, 1.08)
1.07
(0.98, 1.17)
1.01
(0.84, 1.20)
1.01
(0.88, 1.17)
T3 (highest)1.00
(0.93, 1.08)
1.00
(0.91, 1.09)
1.05
(0.96, 1.15)
0.99
(0.83, 1.18)
1.03
(0.89, 1.19)
Density of fast-food restaurants
T1 (lowest)1 1 111 1
T2 1.05
(0.97, 1.13)
1.04
(0.95, 1.13)
1.10
(1.01, 1.21)
1.00
(0.88, 1.14)
0.89
(0.75, 1.06)
0.95
(0.82, 1.09)
T3 (highest)0.96
(0.88, 1.04)
1.01
(0.92, 1.11)
1.20
(1.09, 1.32)
1.05
(0.90, 1.23)
0.86
(0.72, 1.04)
1.05
(0.91, 1.22)
Proximity to public physical activity facilities
T1 (nearest)1 1 111 1
T2 1.08
(1.00, 1.17)
1.04
(0.94, 1.14)
1.02
(0.94, 1.12)
1.15
(1.01, 1.30)
0.88
(0.73, 1.05)
1.08
(0.93, 1.26)
T3 (farthest)1.05
(0.97, 1.13)
1.04
(0.94, 1.14)
0.88
(0.80, 0.96)
1.09
(0.90, 1.31)
1.04
(0.87, 1.25)
1.10
(0.95, 1.28)
Proximity to public parks
T1 (nearest)1 1 111 1
T2 1.01
(0.93, 1.09)
0.98
(0.89, 1.08)
0.94
(0.86, 1.03)
0.98
(0.86, 1.11)
0.87
(0.72, 1.05)
1.05
(0.90, 1.23)
T3 (farthest)1.03
(0.95, 1.11)
1.03
(0.94, 1.13)
0.82
(0.75, 0.90)
0.97
(0.78, 1.20)
1.03
(0.87, 1.23)
1.12
(0.97, 1.30)
Proximity to public transit
T1 (nearest)1 1 11111
T2 0.96
(0.89, 1.04)
0.99
(0.90, 1.08)
0.99
(0.90, 1.08)
1.03
(0.89, 1.18)
0.83
(0.69, 0.99)
0.85
(0.68, 1.06)
1.00
(0.86, 1.16)
T3 (farthest)1.03
(0.96, 1.12)
0.99
(0.90, 1.09)
0.87
(0.79, 0.95)
0.95
(0.79, 1.14)
0.96
(0.81, 1.15)
0.91
(0.70, 1.18)
1.06
(0.91, 1.23)
Street connectivity 1
T1 (lowest)1 1 1 111
T2 1.04
(0.97, 1.12)
0.97
(0.89, 1.06)
1.12
(1.03, 1.22)
1.08
(0.94, 1.23)
0.81
(0.68, 0.96)
0.83
(0.68, 1.01)
0.91
(0.79, 1.05)
T3 (highest)1.01
(0.94, 1.10)
0.96
(0.88, 1.06)
1.20
(1.10, 1.32)
1.11
(0.95, 1.30)
0.90
(0.75, 1.07)
0.93
(0.74, 1.16)
0.98
(0.85, 1.14)
Residential density
T1 (lowest)1 1 111 1
T2 0.97
(0.91, 1.05)
0.96
(0.88, 1.05)
1.13
(1.04, 1.24)
1.19
(0.88, 1.60)
0.87
(0.74, 1.04)
0.98
(0.85, 1.12)
T3 (highest)0.93
(0.86, 1.00)
0.96
(0.89, 1.08)
1.24
(1.13, 1.36)
1.33
(0.94, 1.87)
0.99
(0.82, 1.18)
0.92
(0.79, 1.07)
Commercial density
T1 (lowest)111 111 1
T2 0.96
(0.89, 1.03)
0.97
(0.89, 1.05)
0.95
(0.87, 1.04)
1.15
(1.06, 1.26)
0.82
(0.63, 1.08)
0.92
(0.78, 1.09)
0.99
(0.86, 1.14)
T3 (highest)0.92
(0.85, 1.00)
0.94
(0.86, 1.03)
1.02
(0.93, 1.12)
1.18
(1.08, 1.29)
0.81
(0.60, 1.10)
0.94
(0.79, 1.13)
0.94
(0.81, 1.10)
Industrial density
T1 (lowest)1 1 111 1
T2 0.99
(0.92, 1.07)
0.99
(0.91, 1.08)
1.17
(1.07, 1.27)
1.05
(0.87, 1.27)
0.85
(0.71, 1.01)
0.99
(0.86, 1.13)
T3 (highest)0.93
(0.86, 1.01)
0.95
(0.87, 1.05)
1.21
(1.10, 1.32)
1.05
(0.83, 1.31)
1.06
(0.88, 1.26)
0.96
(0.83, 1.12)
Land-use mix
T1 (lowest)1 111 1 1
T2 0.98
(0.91, 1.06)
1.11
(1.01, 1.23)
1.11
(1.01, 1.23)
0.96
(0.88, 1.05)
1.07
(0.89, 1.29)
1.05
(0.91, 1.23)
T3 (highest)1.03
(0.96, 1.12)
1.13
(1.03, 1.24)
1.13
(1.02, 1.24)
0.92
(0.84, 1.01)
1.14
(0.95, 1.36)
1.02
(0.88, 1.18)
Spatial fraction 0.706 0.473 0.938 0.491 0.488
Univariable and multivariable analyses were adjusted for significant individual variables: (a) adjusted for sex, education, household income, job, living alone, residence period, smoking, alcohol drinking, participation in moderate or vigorous physical activity, level of dietary sodium, subjective health, perception of stress, symptoms of depression, obesity, and diabetes; (b) adjusted for sex, education, household income, job, residence period, smoking, alcohol drinking, sleeping duration, participation in moderate or vigorous physical activity, level of dietary sodium, subjective health, perception of stress, symptoms of depression, and obesity; (c) adjusted for sex, education, living alone, residence period, smoking, sleeping duration, subjective health, perception of stress, symptoms of depression, obesity, and diabetes; (d) adjusted for sex, household income, job, smoking, alcohol drinking, participation in moderate or vigorous physical activity, subjective health, perception of stress, symptoms of depression, obesity, diabetes, hypertension, and dyslipidemia; (e) adjusted for sex, household income, smoking, alcohol drinking, participation in moderate or vigorous physical activity, subjective health, perception of stress, symptoms of depression, obesity, diabetes, hypertension, and dyslipidemia. Multivariable analysis was performed using a Bayesian spatial multilevel model and adjusted for significant individual variables. MI = myocardial infarction; OR = odds ratio; CI = confidence interval. Significant association in bold as p < 0.05 and p < 0.001.
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MDPI and ACS Style

Lee, E.Y.; Choi, J.; Lee, S.; Choi, B.Y. Objectively Measured Built Environments and Cardiovascular Diseases in Middle-Aged and Older Korean Adults. Int. J. Environ. Res. Public Health 2021, 18, 1861. https://doi.org/10.3390/ijerph18041861

AMA Style

Lee EY, Choi J, Lee S, Choi BY. Objectively Measured Built Environments and Cardiovascular Diseases in Middle-Aged and Older Korean Adults. International Journal of Environmental Research and Public Health. 2021; 18(4):1861. https://doi.org/10.3390/ijerph18041861

Chicago/Turabian Style

Lee, Eun Young, Jungsoon Choi, Sugie Lee, and Bo Youl Choi. 2021. "Objectively Measured Built Environments and Cardiovascular Diseases in Middle-Aged and Older Korean Adults" International Journal of Environmental Research and Public Health 18, no. 4: 1861. https://doi.org/10.3390/ijerph18041861

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