| Literature DB >> 35915192 |
Carolyn B Swope1, Diana Hernández2, Lara J Cushing3.
Abstract
Following the Great Depression and related home foreclosures, the federal government established new agencies to facilitate access to affordable home mortgages, including the Home Owners' Loan Corporation (HOLC) and Federal Housing Administration (FHA). HOLC and FHA directed widespread neighborhood appraisals to determine investment risk, referred to as "redlining," which took into account residents' race. Redlining thereby contributed to segregation, disinvestment, and racial inequities in opportunities for homeownership and wealth accumulation. Recent research examines associations between historical redlining and subsequent environmental determinants of health and health-related outcomes. In this scoping review, we assess the extent of the current body of evidence, the range of outcomes studied, and key study characteristics, examining the direction and strength of the relationship between redlining, neighborhood environments, and health as well as different methodological approaches. Overall, studies nearly universally report evidence of an association between redlining and health-relevant outcomes, although heterogeneity in study design precludes direct comparison of results. We critically consider evidence regarding HOLC's causality and offer a conceptual framework for the relationship between redlining and present-day health. Finally, we point to key directions for future research to improve and broaden understanding of redlining's enduring impact and translate findings into public health and planning practice.Entities:
Keywords: Environmental justice; HOLC; Health disparities; Housing; Segregation; Structural racism
Year: 2022 PMID: 35915192 PMCID: PMC9342590 DOI: 10.1007/s11524-022-00665-z
Source DB: PubMed Journal: J Urban Health ISSN: 1099-3460 Impact factor: 5.801
Fig. 1HOLC map of Oakland, CA. Published by the Mapping Inequality project [7] under a Creative Commons Attribution-NonCommercial-ShareAlike 4.0 International License (https://creativecommons.org/licenses/by-nc-sa/4.0/).
Fig. 2PRISMA flowchart showing the study selection process
Fig. 3Geographic distribution of studies reporting results specific to a particular city or state (N = 33), and indicating with arrow the number of cities per region with redlining maps digitized by mapping inequality to date
Studies assessing the association between historical HOLC grade and subsequent health-related outcomes
| Location | Outcome(s) | Unit of analysis (sample size) | HOLC variable | Control variablesa | Abbreviated findings [95% CI] | |
|---|---|---|---|---|---|---|
| Benns et al. [ | Louisville, KY | Number of gunshot victims | Modified census block groups ( | Categorical: A, B, C, D (ref), ungraded | Population density, sociodemographic characteristics | Compared to D-graded areas, A-graded areas were associated with lower incidence of gunshot victims (IRR = 0.22 [0.07, 0.61]) |
| Diaz et al. [ | Nationwide | 30-day (1) mortality, (2) postoperative complications, and (3) readmissions | Patients hospitalized for certain surgeries ( | Categorical: A (ref), B, C, D | Age, sex, comorbidities, urgency of admission, type of operation, hospital characteristics, CT Area Deprivation Index | Patients residing in D-graded areas had higher odds of mortality (OR = 1.23 [1.13–1.34]), complications (OR = 1.12 [1.07–1.17]) and readmissions (OR = 1.06 [1.01–1.11]) compared to those residing in A-graded areas. Associations were attenuated after additional control for neighborhood deprivation |
| Hollenbach et al. [ | 9 counties in the Finger Lakes region of NY | Primary: Preterm and periviable birth Secondary: Prevalence of 6 obstetric and medical complicationsc | Live births ( | Categorical: A (ref), B and C,b C, C and D, D, 3 or more designations | Model 1: zip code poverty levels and educational attainment; Model 2: maternal and paternal race | D-graded areas were associated with higher prevalence of preterm birth compared to A-graded areas, when adjusting for community characteristics (OR = 1.46 [1.08–1.97]), as well as when adjusting separately for parental race (OR = 1.38 [1.25–1.53]). D-graded areas also linked to higher unadjusted prevalence of all secondary outcomes; greatest effect size for severe maternal depression (OR = 4.40 [3.15–6.17]) |
| Huggins [ | Austin, TX | Number of cases or deaths from tuberculosis, 1951 | HOLC polygons (N not stated) | Categorical: D vs. all other areas | None | Some but not all redlined areas had a higher number of tuberculosis cases per unit area |
| Jacoby et al. [ | Philadelphia, PA | Number of (1) firearm assaults and (2) violent crimes | 1940 census tracts (CT) ( | Categorical: A (ref), B, C, D, ungraded | 1940 sociodemographic characteristics, present-day population size | Relative to exclusively A-graded areas, D grade was associated with higher incidence of firearm assaults (IRR = 8.73 [2.24, 36.34]). Ungraded areas were associated with higher incidence of violent crimes (IRR = 4.53 [1.57, 17.29]), but the relationship was not statistically significant for D grade (IRR = 2.57 [0.91, 11.00]) |
| Krieger et al. [ | 28 urban areas in MA | Late stage at diagnosis for cervical, breast, lung, and colorectal cancer | Individuals with cancer ( | Categorical: A/B combined (ref), C, D, ungraded, mixedl | Age at diagnosis, sex/gender, race/ethnicity | Residence in a D-graded CT, compared to A- or B-graded CT, was associated with increased risk of late-stage diagnosis of lung cancer among men (RR = 1.07 [1.02, 1.13]) and breast cancer for women (RR = 1.07 [0.98, 1.17]) |
| Krieger et al. [ | New York City | Preterm birth | Singleton births ( | Categorical: A (ref), B, C, D, other (ungraded or less than 50% of land in one HOLC category) | Maternal age, nativity, education, race/ethnicity; additional separate models also control for present-day CT poverty and racialized economic segregation | Residence in a D-graded CT was associated with elevated risk compared to an A-graded CT (OR = 1.18 [1.05, 1.32]) when controlling for maternal characteristics alone. When additionally controlling for current poverty, risk was similar (OR = 1.14 [1.02, 1.28]). The association was attenuated with control for present-day racialized economic segregation in addition to maternal characteristics (OR = 1.07 [0.96, 1.20])d |
| Li and Yuan [ | New York City | (1) Cumulative percentage of people who tested positive for Covid-19, and (2) cumulative death rate from Covid-19 | Zip code tabulation area (ZCTA) (N = 165) | Categorical: A (ref), B, C, D | Racial/ethnic composition, SES, population 65 + , average household size, Covid-19 test rate, number of days tracked | Grades of B and C, although not D, were associated with a higher rate of Covid-19 infection as compared to A, but not a higher death rate. The association decreased over time |
| Lynch et al. [ | Milwaukee, WI | (1) Average infant mortality rate Prevalence of adults who reported having poor (2) mental or (3) physical health, for ≥ 14 days | CT (N = 123) | Continuous measure of redlining ranging from 0.5 to 4e | None | 1 unit increase in redlining score was associated with increase in the percent of adults reporting poor mental ( |
| McClure et al. [ | Detroit, MI | Self-rated health, ranging from 1 to 5 | Locally defined neighborhood ( Individual (N = 1471) | Continuous measure of % of locally defined neighborhood graded D | None | A 10%-point increase in redlined area in a neighborhood was associated with 0.56 [− 0.10, 1.28] increase in neighborhood prevalence of poor self-rated health, and 0.23 [− 0.06, 0.57] increase in within-person probability of experiencing poor self-rated health |
| Mujahid et al. [ | Los Angeles, CA; New York City, NY; Chicago, IL; Saint Paul, MN; Minneapolis, MN; Winston-Salem, NC; Baltimore, MD | Ideal cardiovascular health (CVH) summary measure,g ranging from 0 to 14 | Individual ( | Categorical: A (ref), B, C, D | Age, sex, level of education, family income | Living in poorer-graded neighborhoods was associated with CVH, compared to those residing in A-graded areas, only among Black participants (B-graded PR = -1.09 [− 1.80, − 0.38], C-graded PR = − 0.83 [− 1.53, − 0.12], D-graded PR = -0.82 [− 1.54, − 0.10]). No associations for white, Hispanic, or Chinese participants (D-grade white PR = − 0.33 [− 0.80, 0.15]) |
| Nardone et al. [ | 8 cities in CA | Total age-adjusted rates of ED visits for asthma | CT ( | Categorical: A (ref), B, C, D | Diesel exhaust, average annual ambient PM2.5 concentration, poverty rate, city random effect | Compared to A, D grade was associated with higher rate of ED visits due to asthma (RR = 1.39 [1.21, 1.57]), leading to 15.6 [8.8, 23.3] additional ED visits per 10,000 residents per year |
| Nardone et al. [ | Atlanta, Chicago, Cleveland, Los Angeles, Miami, New York, Oakland, San Francisco, and St. Louis | Prevalence of 14 health indicators among adultsh | CT ( | Categorical: comparison not stated | None | Cancer, poor mental health, and lack of health insurance showed the strongest correlation with redlining, while there was little correlation between redlining and high blood pressure, congestive heart disease, and Pap smears |
| Nardone et al. [ | Los Angeles, Oakland, and San Francisco, CA | 1) Preterm birth (PTB), 2) low birth weight (LBW), 3) small-for-gestational age (SGA), and 4) perinatal mortality (PM) | Individual ( | Categorical: adjacent grades (B vs. A, C vs. B, and D vs. C) | 1940 CT sociodemographic characteristics | Without propensity score matching, prevalence of PTB, SGA, and PM was significantly higher in C- and D-graded areas, compared to A-graded areas. Adjusted models using a restricted propensity score matched sample indicated higher odds of PTB (OR = 1.02 [1.00–1.05]) and SGA (OR: 1.03 [1.00–1.05]) associated with C grade, relative to B. D grade was associated with reduced odds of PTB (OR = 0.93 [0.91–0.95]), LBW (OR = 0.94 [0.92–0.97]), and SGA (OR = 0.94 [0.92–0.96]) relative to Ci |
| Poulson et al. [ | Boston, MA | Rate of shootings (assaults and homicides involving a firearm) per 1000 people | Census block ( | Categorical: A/ungraded combined (ref), B, C, D | None | D grade was associated with higher incidence rate of shootings compared to A/ungraded areas (IRR = 11.1 [5.5, 22.4]) |
| White et al. [ | 14 urban areas nationwide | Prevalence of 7 health indicators among adultsk | Modified census blocks ( | Categorical: A, B, C, D (ref) | Nonej | Relative to A, D grade was associated with a higher odds of chronic heart disease, smoking, diabetes, no physical activity, no health insurance, and obesity in 5–13 out of 13 total cities. Odds of a routine health check up in the last year were lower in 7 cities |
| Wright et al. [ | 28 urban areas in MA | Incidence of primary invasive breast cancer, overall and by tumor estrogen (ER + , ER −) and progesterone (PR + , PR −) receptor status | Census tract ( | Categorical: A/B combined (ref), C, D, ungraded, mixedl | Individual-level race | C and D grades were associated with a reduced risk of breast cancer relative to A/B (D-grade IRR = 0.94 [0.88, 1.01] and C-grade IRR = 0.97 [0.92, 1.03]). Mixed grade and no grade were associated with higher risks (IRR = 1.05 [0.98, 1.12] and 1.01 [0.95, 1.07], respectively) |
CT census tract; IRR incidence rate ratio; OR odds ratio; PR prevalence ratio; RR risk ratio
aUnless otherwise specified, all studies examined outcomes close to the present day (2000 and later).
bZip codes containing both areas graded B and areas graded C.
cPregnancy-associated hypertension, severe maternal depression, NICU admission, 5 min APGAR score < 7, substance use, exclusive breastfeeding.
dIndex at the concentration at the extremes comparing high-income White households vs. low-income Black households.
eTracts with 100% of their area graded D had a score of 4.
fThe primary exposure of interest was foreclosure rate recovery. Redlining was considered as a confounder and effect modifier of the association between foreclosure rates during the 2007–2008 Great Recession and self-rated health.
gConsists of 7 risk factors (blood pressure, fasting glucose, cholesterol, body mass index, diet, physical activity, and smoking)
hWith current asthma, (2) diagnosed with a nondermatologic cancer, (3) ever diagnosed with angina or coronary heart disease, (4) ever diagnosed with diabetes, (5) told they have high blood pressure in past year, (6) reporting 14 days of poor mental health in the past month, (7) ever diagnosed with a stroke, (8) reporting binge drinking in last 30 days, (9) currently smoking every day or some days, (10) with current obesity, (11) reporting an average of < 7 h of sleep, (12) reporting having no current health insurance coverage, 13) receiving a Pap smear in past 3 years, (14) with high blood pressure who are taking hypertension medication.
iEstimates were similar in sensitivity analyses adjusting for maternal covariates of maternal age, parity, and year of birth. Secondary analyses of very PTB, very LBW, and neonatal morality found elevated odds associated with C versus B grade and reduced odds of very PTB associated with D versus C.
jSecondary analysis controls for CT poverty.
kEver diagnosed with chronic heart disease, (2) went to doctor in last year for routine checkup, (3) currently smoking every day or most days, (4) ever diagnosed with diabetes, (5) reporting no leisure-time physical activity in last month, (6) with current obesity (BMI ≥ 30 kg/m2 with certain exceptions), (7) without health insurance
lMixed areas had ≥ 50% of land area in HOLC-graded areas, but no HOLC grade accounting for ≥ 50% of land area. In contrast, ungraded areas had < 50% of their land in HOLC-graded areas
Studies assessing the association between historical HOLC grade and subsequent environmental determinants of health
| Location | Outcome(s) | Unit of analysis (sample size) | HOLC variable | Control variables | Abbreviated findings | |
|---|---|---|---|---|---|---|
| Hoffman et al. [ | 108 urban areas nationwide | (1) Summertime land surface temperature (LST) (2) Developed impervious surface land cover (3) Tree canopy coverage | HOLC polygons (N not stated) | Categorical: A, B, C, D | None | LST was elevated in D- relative to A-graded areas in 94% of urban areas (2.6 °C warmer on average). Impervious surface land cover was higher in D-graded areas and tree canopy cover was lower |
| Lane et al. [ | 202 urban areas nationwide | Annual ambient concentration predictions of (1) nitrogen dioxide (NO2) and (2) fine particulate matter (PM2.5) | Census block (N = 562,078) | Categorical: A, B, C, D | None | Across all cities, NO2 concentrations are 56% higher in D-graded areas than A-graded areas, while PM2.5 concentrations are 4% higher. Population-weighted mean NO2 levels were higher in D-graded areas than overall in 80% of cities (55% for PM2.5), and were lower in A-graded areas than overall in 84% of cities (68% for PM2.5) |
| Lee et al. [ | 6 cities, San Francisco Bay Area, CA | Density of off-premise alcohol outlets | Census block groups ( | Categorical: A (ref), B, C, D, ungraded | Local and adjacent population, median household income | D grade was associated with higher density of off-premise alcohol outlet density relative to A grade (RR = 1.90 [0.81, 4.84]) |
| Li & Yuan [ | 102 urban areas nationwide | mRFEI Index of healthiness of the food environment, ranging from 0 (worst) to 100 (best) | Census tract ( | Categorical: A (ref), B, C, D, ungraded (< 50% of land graded) | CT sociodemographic characteristics and population density, city-level racial segregation and natural log of the population | D-graded areas had 0.83 [0.77, 0.97] times the mRFEI score of A-graded areas |
| Locke et al. [ | 37 urban areas, with sub-analysis of 8 | Tree canopy coverage | HOLC polygon (N = 3188) | Categorical: A (ref), B, C, D | City random effect | D grade was associated with decreased percent tree canopy cover relative to A grade (M = − 20.79 percentage points [− 22.27, − 19.31]) |
| Nardone et al. [ | 102 urban areas nationwide | Summer and annual average NDVI, ranging from -1 (least green) to 1 (most green) | HOLC polygon ( | Categorical: adjacent grades (B vs. A, C vs. B, and D vs. C) | 1940 CT sociodemographic characteristics, 1940 population density, ecoregion, Census region | Unadjusted annual average mean NDVI increased on a gradient from D to A grade. Poorer HOLC grade was associated with a 0.024–0.39 unit decrease in annual average NDVI compared to the adjacent grade in adjusted models using a restricted, propensity score matched sample |
| Nowak et al. [ | All available cities nationwide | Tree cover, impervious cover, tree cover stocking (proportion of non-impervious area occupied by tree canopies), and ecosystem service value (pollution removal, carbon sequestration, avoided runoff) | Census incorporated and designated places ( | Categorical: A, B, C, D | None | Poorer grade was associated with lower % tree cover, % stocking, and ecosystem service values, and higher % impervious cover. For example, tree cover was about twice as high a proportion of A-graded areas as D-graded areas. 88.6% of cities had greater % tree cover, and 86.4% had lower % impervious cover, in A-graded areas than D-graded areas |
| Sadler et al. [ | Baltimore, MD | Healthy food access score ranging from 1 to 1145 | Residential tax parcels (N not stated) | Continuous variable with change from A to B, B to C, and C to D considered 1 unit increase | Socioeconomic distress index, racial composition, housing age | A 1-unit increase in redlining was associated with a 48–52 point increase in food access score |
| Saverino et al. [ | Richmond, VA | Afternoon mean temperature during a heat wave | Census block group (N not stated) | Continuous: quartiles of proportion A/B combined and C/D combined | None | Areas in the fourth quartile of percentage C- or D-graded were on average 0.53 °C warmer than areas in the lowest quartile, while areas in the fourth quartile of percentage A- or B-graded were on average 0.26 °C cooler than areas in the lowest quartile |
| Schinasi et al. [ | Philadelphia, PA | Land cover and housing characteristics linked to enhanced heat vulnerability, including roof color, shape, and shape and color combined, and presence of immediately adjacent mature or immature tree canopy | Residential properties ( | Categorical: A (ref), B, C, D | 1940 racialized economic segregation and CT sociodemographic characteristics | Compared to properties in A-graded areas, properties in D-graded areas had elevated risk of low or no mature tree canopy, in both models adjusting for historic characteristics (RR = 5.09 [2.78–9.32]) and for present-day characteristics (RR = 5.96 [5.76, 6.16]) |
| Schwartz et al. [ | 13 Ohio urban areas | Tobacco retailer density | Modified CTs (N = 3846) | Categorical: A (ref), B, C, D, ungraded; all pairwise comparison | CT sociodemographic characteristics, city fixed effect | D grade was associated with higher density of tobacco retailers relative to A (RR = 1.98 [1.52, 2.60]) |
| Trangenstein et al. [ | Baltimore, MD | Clusters of four types of alcohol outlets | Census block groups ( | Categorical: B, C, D, ungraded (ref) | Population density, sociodemographic characteristics, concentrated disadvantage index, residential stability, social control or disinvestment, built environment characteristics | Compared to ungraded areas, D grade was associated with higher odds of being in a general (OR = 8.82 [2.99, 25.98]), off-premise (OR = 7.32 [2.00, 26.79]), on-premise (OR = 8.07 [2.26, 28.77]), or LBD-7 (combined on/off-premise) (OR = 8.60 [2.93, 25.30]) alcohol outlet cluster |
| Wilson [ | Baltimore, MD; Dallas, TX; Kansas City, MO | 1) LST, two summer days and 2) NDVI, two summer days | HOLC polygons | Categorical: A, B, C, D | None | C- and D-graded areas had higher median land surface temperatures than A or B in all cities ( |
NDVI normalized difference vegetation index; OR risk ratio; RR risk ratio
Studies assessing the association between historical HOLC grade and subsequent (a) environmental determinants of health and (b) health-related outcomes
| Location | Outcome(s) | Unit of analysis (sample size) | HOLC variable | Control variables | Abbreviated findings | |
|---|---|---|---|---|---|---|
| Huang & Sehgal [ | Baltimore, MD | (1) Life expectancy at birth, (2) age-differentiated mortality rates, (3) teen pregnancy per 1000 female residents 15–19, (4) % of births given at term, (5) % of births with satisfactory birth weight, (6) % of births receiving 1st trimester prenatal care, (7) % children age 0–6 with elevated blood lead levels, (8) liquor outlets per 1000 residents, and (9) fast food outlets per 1000 residents | Planning board-defined community statistical areas ( | Categorical: A/B (ref), C, D | Sociodemographic characteristics | Compared to A/B-graded areas, a D grade is associated with a 5.23 [3.49, 6.98] year reduction in life expectancy. D grades were also associated with significantly higher mortality for the age groups 25–44, 45–64, and 65–84. For example, a D grade is associated with 95.47 [52.03, 138.91] additional deaths per 10,000 residents in a 5-year period. C-graded areas had 23.61 [7.97, 39.26] additional births per 1000 female residents 15–19; D, 20.36 [4.34, 36.37] additional births. C, but not D, grade was associated with reduction in % of births in which the mother received 1st trimester prenatal care (C: − 5.06 [− 8.7, − 1.43]; D: − 1.82 [− 5.54, 1.9]). D-graded areas were associated with 2.18 [1.38, 2.98] additional liquor stores per 1000 residents |
| Li et al. [ | 11 urban areas within TX | (1) Mean, minimum, and maximum LST on 1 June and 31 August Heat-related emergency department visits including (2) inpatient admissions and (3) outpatient visits | ZCTA (N not stated) | Categorical: 50% or more ZCTA area graded C or D, vs. less than 50% ZCTA area graded C or D | For outcomes 2 and 3: population aged 65 and older, non-White, Hispanic, lower income, living alone, and who does not speak English well | More redlined areas had a 3.90 °C hotter average daytime LST ( |
| Namin et al. [ | 115 urban areas nationwide | (1) Tree canopy coverage (2) Lifetime cancer risk associated with air toxics 3) Average respiratory hazard index | HOLC polygon ( | Categorical: A (ref), B, C, D | Population density (tree canopy coverage only), city random effect | D-graded areas had 16.21% less tree canopy coverage than A on average in 2011 but were more likely to experience an increase in coverage between 2001 and 2011 Compared to A-, D-graded areas had a 2.6 mean unit increase in lifetime cancer risk and 9% increase in geometric mean respiratory hazard |
LST land surface temperature
Fig. 4Conceptual model of the pathway from historical redlining to present-day health outcomes