Hostname: page-component-cd9895bd7-hc48f Total loading time: 0 Render date: 2024-12-22T03:57:57.845Z Has data issue: false hasContentIssue false

What counts? Adding nuance to retail food environment measurement tools in a Canadian context

Published online by Cambridge University Press:  19 April 2023

Alexa Rae Ferdinands
Affiliation:
School of Public Health; 3-300 Edmonton Clinic Health Academy, 11405 – 87 Ave, University of Alberta, Edmonton T6G 1C9, AB, Canada
Jennifer Ann Brown
Affiliation:
School of Public Health; 3-300 Edmonton Clinic Health Academy, 11405 – 87 Ave, University of Alberta, Edmonton T6G 1C9, AB, Canada
Charlene C Nielsen
Affiliation:
School of Public Health; 3-300 Edmonton Clinic Health Academy, 11405 – 87 Ave, University of Alberta, Edmonton T6G 1C9, AB, Canada
Candace IJ Nykiforuk
Affiliation:
School of Public Health; 3-300 Edmonton Clinic Health Academy, 11405 – 87 Ave, University of Alberta, Edmonton T6G 1C9, AB, Canada
Kim D Raine*
Affiliation:
School of Public Health; 3-300 Edmonton Clinic Health Academy, 11405 – 87 Ave, University of Alberta, Edmonton T6G 1C9, AB, Canada
*
*Corresponding author: Email [email protected]
Rights & Permissions [Opens in a new window]

Abstract

Objective:

Limitations of traditional geospatial measures, like the modified Retail Food Environment Index (mRFEI), are well documented. In response, we aimed to: (1) extend existing food environment measures by inductively developing subcategories to increase the granularity of healthy v. less healthy food retailers; (2) establish replicable coding processes and procedures; and (3) demonstrate how a food retailer codebook and database can be used in healthy public policy advocacy.

Design:

We expanded the mRFEI measure such that ‘healthy’ food retailers included grocery stores, supermarkets, hypermarkets, wholesalers, bulk food stores, produce outlets, butchers, delis, fish and seafood shops, juice/smoothie bars, and fresh and healthy quick-service retailers; and ‘less healthy’ food retailers included fast-food restaurants, convenience stores, coffee shops, dollar stores, pharmacies, bubble tea restaurants, candy stores, frozen dessert restaurants, bakeries, and food trucks. Based on 2021 government food premise licences, we used geographic information systems software to evaluate spatial accessibility of healthy and less healthy food retailers across census tracts and in proximity to schools, calculating differences between the traditional v. expanded mRFEI.

Setting:

Calgary and Edmonton, Canada.

Participants:

N/A.

Results:

Of the 10 828 food retailers geocoded, 26 % were included using traditional mRFEI measures, while 53 % were included using our expanded categorisation. Changes in mean mRFEI across census tracts were minimal, but the healthfulness of food environments surrounding schools significantly decreased.

Conclusions:

Overall, we show how our mRFEI adaptation, and transparent reporting on its use, can promote more nuanced and comprehensive food environment assessments to better support local research, policy and practice innovations.

Type
Research Paper
Creative Commons
Creative Common License - CCCreative Common License - BY
This is an Open Access article, distributed under the terms of the Creative Commons Attribution licence (http://creativecommons.org/licenses/by/4.0/), which permits unrestricted re-use, distribution and reproduction, provided the original article is properly cited.
Copyright
© The Author(s), 2023. Published by Cambridge University Press on behalf of The Nutrition Society

Retail food environments and public health

Poor diet quality is the second greatest risk factor for premature death and disability combined in Canada(1). A poor diet is characterised by an eating pattern low in fibre, protein, and micronutrients, and high in total energy, free sugars, saturated fats, and sodium. Although Canada’s Food Guide recommends Canadians limit their intake of highly processed foods and drinks typical of a poor diet, approximately half of total daily energy intake for Canada’s population in 2015 came from these sources(Reference Polsky, Moubarac and Garriguet2).

Evidence suggests that retail food environments (RFE) (i.e. ‘the availability and composition (e.g. relative mix) of food retailing within local environments’(Reference Wilkins, Morris and Radley3) (p. 1)) may be an important determinant of population-level eating patterns and diet-related chronic diseases(Reference Frank, Bigazzi and Hong4,Reference Ni Mhurchu, Vandevijvere and Waterlander5) . As such, improving the healthfulness of RFE has become an increasing public health concern across Canada(Reference Minaker, Shuh and Olstad6). In 2014, our team developed Alberta’s Nutrition Report Card on Food Environments for Children and Youth (hereafter, ‘Nutrition Report Card’) to benchmark policies and practices that support or inhibit healthy eating practices in the Canadian province of Alberta(Reference Olstad, Raine and Nykiforuk7). Two Nutrition Report Card indicators targeted RFE, acknowledging that the relative mix, or ratio, of healthy to less healthy food retailers (henceforth, ‘retailers’) in a defined geographical area can impact people’s food purchasing and eating practices(Reference Needham, Sacks and Orellana8). Indicators evaluating spatial accessibility of healthy and less healthy retailers within the RFE included: 1) availability of healthy retailers across census tracts in municipalities of interest; and 2) availability of less healthy retailers in proximity to schools(Reference Olstad, Raine and Nykiforuk7). To categorise retailers as ‘healthy’ and ‘less healthy’, we used the Centers for Disease Control and Prevention’s (CDC)(9) modified Retail Food Environment Index (mRFEI) (see section 2·2).

Challenges in measuring retail food environments

While calculating the mRFEI represents a common approach to assess relative density of healthy retailers(9,Reference Mahendra, Polsky and Robitaille10) , it is limited in detail and differentiation(Reference Brown, Ferdinands and Prowse11,Reference Thornton, Lamb and White12) . Examples of these limitations are outlined here:

  • Narrow view of the RFE. Calculating the proportion of healthy to less healthy retailers from the CDC’s list of six retailer types (see section 2.2) meant excluding retailers that potentially shape purchasing and eating practices, like coffee shops and pharmacies(Reference Lucan13,Reference Lucan, Maroko and Seitchik14) . Further, given the heterogeneity of food and beverage offerings and/or location characteristics, it was often challenging to determine whether to include or exclude certain retailers. For example, were fish and seafood stores included under the supermarkets and other grocery stores category, or excluded?

  • Imprecision within retailer categories. Vague categories restricted our ability to infer details about retailer types. For instance, within the limited-service eating places category, we could not distinguish between less healthy fast-food restaurants and potentially healthy sandwich shops. In another example, ethnic food stores typically sell many convenience and pre-packaged foods, leading them to be categorised as less healthy convenience stores, despite also offering healthy (and affordable) culturally specific foods and beverages(Reference Ohri-Vachaspati, DeWeese and Acciai15,Reference Han, Powell and Zenk16) . Thus, mRFEI categorisations may misrepresent the role of ethnic grocers as healthy options. Greater precision (i.e. capturing subcategories of retailers) could offer valuable details for stakeholders like public health practitioners, policymakers and urban planners in identifying opportunities to improve RFE healthfulness.

  • Shortcomings of simplistic binary labelling systems. The mRFEI only categorises retailers by type, without accounting for the range of foods sold within(Reference Kelly, Flood and Yeatman17). For example, a grocery store may sell an abundance of highly processed foods but remains labelled as ‘healthy’. Additionally, RFE are dynamic, continuously adapting to new business practices. Fast-food restaurants have gradually increased their healthy offerings, which can be problematic when applying binary healthfulness labels(Reference Mahendra, Polsky and Robitaille10).

  • Potential for inconsistencies and misclassifications. Despite using codebooks and outlining procedures to promote inter-coder reliability, coder subjectivity can still result in inconsistencies in determining whether to include/exclude retailers, and in categorising included retailers(Reference Wilkins, Morris and Radley18).

Researchers have documented concerns about the reliability of RFE measurement approaches across coders and contexts for years(Reference Needham, Sacks and Orellana8,Reference Thornton, Lamb and White12,Reference Lucan13,Reference Wilkins, Morris and Radley18Reference Ohri-Vachaspati, Martinez and Yedidia20) . Wilkins et al. called for transparent reporting of geospatial RFE analysis, arguing that more attention to how retailer types are defined, and reaching consensus on definitions, would enhance comparability across studies(Reference Wilkins, Morris and Radley18). Han et al. (Reference Han, Powell and Zenk16) and Ohri-Vachaspati et al. (Reference Ohri-Vachaspati, Martinez and Yedidia20) highlighted the limitations of categorising non-franchise or non-corporate food retailers with conventions like the North American Industry Classification System (NAICS) used in the mRFEI due to the lack of consensus on inclusion criteria for smaller, heterogeneous retailer types. To improve reliability, some researchers have diverged from coding using NAICS. For instance, while NAICS(21) suggests examining retailer employee numbers to make coding decisions, Ohri-Vachaspati et al. opted not to because the possibility of misclassification using this criterion was too great (e.g. convenience stores with many employees could be confused with medium-sized grocery stores)(Reference Ohri-Vachaspati, Martinez and Yedidia20).

These concerns are in addition to broader issues with relative RFE measures, such as that relative measures cannot distinguish between RFE with equally low numbers of unhealthy and healthy retailers, and RFE with equally high numbers of unhealthy and healthy retailers – even though these RFE likely influence purchasing and eating practices differently(Reference Thornton, Lamb and White12). Researchers have suggested that combinations of absolute and relative measures are needed to fully describe RFE(Reference Clary, Ramos and Shareck22,Reference Pinho, Mackenbach and Oppert23) . Indeed, the two Nutrition Report Card indicators discussed herein are interpreted holistically alongside thirty-eight other food environment indicators, upon which recommendations are based.

Grounded in the literature(Reference Mahendra, Polsky and Robitaille10,Reference Thornton, Lamb and White12,Reference Wilkins, Morris and Radley18,Reference Ohri-Vachaspati, Martinez and Yedidia20,Reference Sacks, Robinson and Cameron24) and our experiences of developing and implementing spatial accessibility indicators for the Nutrition Report Card, the need for a more comprehensive yet context-specific approach to categorising retailers in RFE assessments was evident. Here, we aim to contribute an operational lens to methodological discussions on measuring RFE.

Purposes

  1. 1. To extend existing RFE measurement strategies by developing and documenting subcategories to increase the granularity of healthy v. less healthy options, through inductively coding our Calgary and Edmonton (western Canadian cities) retailer dataset.

  2. 2. To establish replicable processes and procedures for coding and updating an RFE database, to increase reliability, avoid miscalculation and reduce the need for manual recategorisation each year.

  3. 3. To demonstrate how an RFE codebook and database can be used to generate knowledge mobilisation products (e.g. reports, policy briefs and infographics) for healthy public policy advocacy.

Methods

Study setting and population

For the Nutrition Report Card, RFE healthfulness was assessed in Calgary and Edmonton. Calgary is Alberta’s most populous city, with a population of 1 392 609(25). Edmonton, Alberta’s capital, is the second-most populous city with 932 546 people(26). Combined, Calgary and Edmonton account for approximately 60 % of Alberta’s population(27). Calgary and Edmonton have substantial discretion over their RFE through land use planning, informed by the Calgary Food Action Plan(28) and City Environmental Strategies in Edmonton(29).

Iterative and inductive development of the expanded retailer codebook and database

For each annual Nutrition Report Card, the team collected a complete list of retailers in Alberta from government public health inspectors and used geographic information systems (GIS) software to summarise two spatial accessibility indicators. From this list, we developed a database of retailers categorised as ‘healthy’ and ‘less healthy’ based on CDC mRFEI criteria(9). Our first indicator’s benchmark employed the CDC standard of an average mRFEI score of 10 across all census tracts to our municipalities of interest, indicating a relatively healthful RFE. The Canadian Census defines a census tract as a geographically stable, socio-economically homogenous land area with approximately 4000 residents(30). Our second indicator’s benchmark examined the prevalence of less healthy retailers within 500 m of all public, Catholic, and Francophone Grades K-12 schools in Calgary and Edmonton (addresses obtained from school board websites), characterising the proportion of schools with 0 to 5, v. more than 5, retailers within a 500 m radius (see section 2·4). For each iteration of the Nutrition Report Card, our team categorised retailers using the most recent government food inspection list, calculating these two indicators for Calgary and Edmonton.

For the 2015–2019 Nutrition Report Cards, we used the traditional CDC mRFEI criteria(9), adapted to the Canadian context by using the NAICS maintained by Statistics Canada(21). As per mRFEI standards, our analyses were restricted to retailers publicly accessible within the RFE (i.e. retailers within organisational environments like health care facilities and schools were excluded). Less healthy retailers included limited-service eating places (NAICS codes: 722 512CAN, 722 211US), convenience stores (445 120CAN&US), and gas stations with convenience stores (447 110CAN&US); healthy retailers included supermarkets and other grocery stores (445 110CAN&US), fruit and vegetable markets (445 230CAN&US), and general-line food merchant wholesalers (413 110CAN, 452 910US)(21). For all Nutrition Report Cards (2015–2021), retailers with multiple premise licences were considered a single location and assigned one code, unless a separately licensed premise was a franchise or corporate retailer. For example, a grocery store with separately licensed produce, bakery and meat departments was assigned one overall code (grocery store), while a grocery store with a Starbucks inside was assigned two separate codes (grocery store and limited-service eating place, respectively). This allowed for standardisation between municipalities, as the premise licensing of departments within grocery store locations varied between Calgary and Edmonton.

For the 2020 Nutrition Report Card, we expanded our mRFEI conception. We began by inductively conceptualising the newest version of our retailer codebook and RFE database, developing subcategories with empirical examples that increased the granularity of healthy v. less healthy options. Two research team members (human geographer and dietitian with extensive experience updating the dataset) independently created subcategory lists of different retailer types for comparison and consolidation. As in previous years, we started with an initial coding scheme based on the mRFEI. To expand our categorisation, we employed a second column to free code locations which did not correspond to a healthy or less healthy classification (e.g. coffee shops), or which could characterise a possible subcategory for a set classification (e.g. bulk foods stores as a subcategory of supermarkets and other grocery stores). All variations captured across the municipalities were coded this way, with emerging codes and definitions compiled in a codebook by consensus between the two team members. Diagrams were developed to help conceptualise retailer categories and map interrelationships, informed by literature from Daepp and Black(Reference Daepp and Black31) and Prowse et al. (Reference Prowse, Naylor and Olstad32). Each retailer subcategory was then assigned a label of healthy/less healthy, guided by CDC criteria(9). Final subcategories with corresponding healthfulness codes were reviewed and approved by the dietitian in consultation with a senior supervising dietitian on the research team.

For the expanded mRFEI, our healthy retailer definition was broadened to include grocery stores, supermarkets or hypermarkets (incorporating fruit and vegetable markets here), wholesalers, bulk food stores, butchers or delis, fish and seafood shops, juice or smoothie bars, and fresh and healthy quick-service retailers (like sandwich, salad or sushi restaurants). Our less healthy retailers included fast-food restaurants, convenience stores, coffee shops, dollar stores, pharmacies, bubble tea restaurants, candy stores, frozen dessert restaurants, bakeries and food trucks (at their registered location)(33).

To implement the expanded mRFEI for the 2020 Nutrition Report Card, the same two team members coded all retailers in Calgary and Edmonton. After completing the first round of coding, any coding disagreements were resolved by additional review from a third coder who referenced Google Street View, Google Reviews and retailer websites for further information (e.g. storefront and menu details). We report all final subcategories and their assignments as healthy v. less healthy, the definitions for each subcategory, and the relative frequencies of each retailer type across the two municipalities, as well as subcategories that were coded but excluded from mRFEI calculations for the Nutrition Report Card (Table 1). These exclusions may support future research on expanding RFE measurement approaches.

Table 1 Codebook for categorising retailers based on healthfulness with percent and number of total coded locations

mRFEI, modified Retail Food Environment Index; NAICS, North American Industry Classification System.

* Retailers coded as these categories were included in calculating the traditional mRFEI.

Adapted from NAICS(21), Daepp and Black(Reference Daepp and Black31), and Ohri-Vachaspati et al. (Reference Ohri-Vachaspati, Martinez and Yedidia20)

Finally, for the 2021 Nutrition Report Card, we further developed a system of matching previously coded retailers with retailers in subsequent years based on postal codes, retailer names, and addresses, reducing the need for manual re-coding each year. Retailers that renewed their premise licences could be retained with the same categorisation, while those which discontinued operations were removed. New retailers were coded using the same process of double coding and consensus, as described above.

Expanding the usefulness of existing retail food environment measures using the 2021 dataset

To demonstrate the utility of our retailer codebook and database, we calculated differences between the traditional v. expanded mRFEI (see section 2·2) across census tracts in Calgary and Edmonton, using the 2021 dataset. The CDC’s mRFEI is reported as a proportion from 0–100(9):

$${\rm{mRFEI}} = 100{\rm{\;}} \times {\rm{x\;}}\frac{{{\left( {\# {\rm{\;Healthy\;FR}}} \right)}}\over{{\left( {{\rm{\;}}\# {\rm{\;Healthy\;FR}} + {\rm{\;}}\# {\rm{\;Less\;Healthy\;FR}}} \right)}}}$$

We used descriptive and correlational statistics to test for differences between traditional and expanded mRFEI values, illustrating our comparisons with proximity analysis mapping (see section 2·4 below for details regarding geospatial analysis). For statistical testing, descriptive measures included total retailers, total schools, total census tracts and total retailers within 500 m of schools (all dataset-wide totals with information for both Calgary and Edmonton). For our first spatial accessibility indicator measuring RFE across census tracts, we report total classified retailers, total less healthy retailers and mean mRFEI with standard deviation for both the traditional and expanded measures. For our second spatial accessibility indicator measuring RFE in proximity to schools, we report total classified retailers within 500 m of schools, total less healthy retailers within 500 m of schools, total schools with less healthy retailers within 500 m, mean less healthy retailers within 500 m of schools and maximum less healthy retailers within 500 m of schools for both traditional and expanded mRFEI measures (Table 2). We also calculated Spearman’s rho as a correlation measure to test for differences between the expanded and traditional mRFEI scores obtained across census tracts, and for schools with less healthy retailers within 500 m (Table 2).

Table 2 Descriptive and correlational statistics comparing traditional and expanded mRFEI data in Calgary and Edmonton (2021). Values are counts unless otherwise indicated

mRFEI, modified Retail Food Environment Index; trad. = traditional mRFEI; Exp. = expanded mRFEI.

Generating knowledge mobilisation products for healthy public policy advocacy

To illustrate how the retailer codebook and database can be used to generate knowledge mobilisation products, we report geospatial indicators using the expanded mRFEI categorisation for Alberta’s 2021 Nutrition Report Card. The first indicator, measuring whether the benchmark of mRFEI ≥ 10 was met across census tracts in Calgary and Edmonton, was calculated by geocoding all retailer locations and aggregating those points to the census tracts in which they were located, using ArcGIS software(34). For the second indicator, measuring the number of less healthy retailers within 500 m of school locations, we aggregated less healthy retailers to straight-line circular buffers centred on geocoded school locations in each municipality. Notably, for circular buffers intersecting shopping mall locations, we interpreted the value of all retailers within that shopping mall as falling within the buffer, approximating unimpeded pedestrian access to multiple locations. Geocoded values from previous years were used in conjunction with new locations geocoded in ArcGIS.

We mapped mRFEI calculations and the instance of less healthy retailers in proximity to schools, calculating descriptive statistics and correlation with Spearman’s rho using Python 3(35). Thus, we were able to illustrate the spatial distribution of traditional v. expanded mRFEI measures for Calgary and Edmonton, mapping both our first (Fig. 1) and second (Fig. 2) indicators. We also report changes in the proportions of census tracts that met the mRFEI ≥ 10 benchmark (Fig. 3) and in the proportion of schools with less healthy retailers located within 500 m (Fig. 4), comparing traditional and expanded mRFEI.

Fig. 1 Choropleth maps of the (a) traditional and (b) expanded mRFEI measures for census tracts in Calgary, and (c) traditional and (d) expanded mRFEI measures for census tracts in Edmonton (2021). mRFEI, modified Retail Food Environment Index

Fig. 2 Presence or absence of less healthy retailers within 500 m of schools in Calgary using (a) traditional and (b) expanded mRFEI, and within 500 m of schools in Edmonton using (c) traditional and (d) expanded mRFEI (2021). mRFEI, modified Retail Food Environment Index

Fig. 3 Percentage of census tracts meeting the benchmark of mRFEI ≥ 10 in Calgary and Edmonton, comparing the expanded v. traditional measures (2021). mRFEI, modified Retail Food Environment Index

Fig. 4 Percentage of schools with one or more less healthy retailers within 500 m, comparing the expanded v. the traditional measures (2021)

Results

Retailer classifications for 2021

There were 10 843 retailers classified with subcategorisations in Calgary and Edmonton, with 10 828 retailers geocoded to census tracts in the 2021 Nutrition Report Card (twenty-five retailers were located on the outskirts of both cities, beyond municipal census tracts)(33). While only 26 % of these geocoded locations would be included using the traditional mRFEI (1488 in Calgary and 1355 in Edmonton), our expanded categorisation enabled us to include 53 % of locations (3188 in Calgary and 2533 in Edmonton). This was achieved by expanding our healthy category to include sandwich/salad/sushi retailers, juice shops, butcher/deli shops, bulk foods and fish shops (in addition to grocery stores and wholesalers) and by expanding our less healthy category to include coffee shops, pharmacies, bakeries, dollar stores, bubble tea shops, confectionery stores, frozen dessert shops and food trucks as less healthy (in addition to fast-food restaurants and convenience stores). Total numbers of subcategorised food retailers prior to geocoding are presented in Table 1, with asterisked categories corresponding to CDC mRFEI categories, albeit with modified nomenclature and definitions. For instance, our fast-food restaurant category corresponds to the CDC-defined limited-service eating place. Our convenience store category encompasses both stand-alone convenience stores and convenience stores attached to gas stations, and our grocery store category incorporates fruit and vegetable markets – despite these being two distinct categories according to the CDC’s NAICS framework.

Measures and knowledge mobilisation products for 2021

Table 2 presents descriptive and correlational statistics for the mRFEI calculations and proximity analysis. Calgary had 6251 retailers, 367 schools and 227 census tracts; and Edmonton had 4577 retailers, 345 schools and 200 census tracts. The number of classified retailers increased from the traditional to expanded measures for both cities (by 1700 for Calgary and 1178 for Edmonton). Across its census tracts, Calgary’s mean mRFEI remained at 15 for both the traditional and expanded measure, but Edmonton’s mean mRFEI increased from 13 (traditional) to 16 (expanded), indicating slight improvement in overall healthfulness. Both the number of less healthy retailers within 500 m of schools and the number of schools with any less healthy retailers within 500 m significantly increased from the traditional to expanded measures. Using the traditional measures, the average schools in Calgary and Edmonton had two and three less healthy retailers located within 500 m, respectively; this increased to four and five with the expanded measures. In Calgary, the maximum number of less healthy retailers within 500 m increased from 25 (traditional) to 54 (expanded). In Edmonton, the maximum number of less healthy retailer within 500 m increased from 40 (traditional) to 69 (expanded). While census tracts met the mRFEI ≥ 10 benchmark using both the traditional and expanded measures in both cities, the expanded measure captured greater exposure to less healthy retailers in proximity to Calgary and Edmonton schools.

Table 2 also shows correlation statistics for the mRFEI calculations and proximity analysis. Calgary (ρ = 0·79) had a slightly higher correlation between traditional and expanded measures when conducting mRFEI calculations than Edmonton (ρ = 0·72). Edmonton (ρ = 0·93) had a slightly higher correlation between traditional and expanded measures when conducting the 500 m proximity to school analysis than Calgary (ρ = 0·89). While high correlation values mean the two measures were similar across census tracts and school locations, there were local differences. Figs 1 and 2 illustrate where spatial distribution of those changes occurred; Figs 3 and 4 explain how changes occurred (i.e. meet/not meet benchmark or increase/decrease in less healthy retailers).

Differences between the two retailer classification measures are visually depicted in Fig. 1 for the census tract indicator, and Fig. 2 for the proximity to schools indicator, recreating figures developed for Alberta’s 2021 Nutrition Report Card. In Calgary, Fig. 1(a) (traditional) shows that more census tracts met the mRFEI benchmark ≥10 (blue areas) than in Fig. 1(b) (expanded); in Edmonton, a similar pattern is seen in Fig. 1(c) (traditional) and Fig. 1(d) (expanded). Despite greater exposure to less healthy retailers in proximity to schools indicated by the expanded mRFEI measure, the expanded measure nevertheless indicates healthier mean RFE across census tracts in both cities, overall.

Figure 2 shows the prevalence of less healthy retailers within 500 m of schools. In Calgary, there were subtle changes in the number of schools with less healthy retailers within 500 m (red dots) between traditional (Fig. 2 (a)) and expanded (Fig. 2(b)) measures, with the most notable increases along the northwest (44 %; n 20) and southwest (27 %; n 12). In Edmonton, the change between traditional (Fig. 2(c)) and expanded (Fig. 2(d)) measures is more scattered throughout the city with higher increases in the northwest (43 %; n 13) and southwest (23 %; n 7). Using the expanded measure to capture more retailer types, Alberta’s 2021 Nutrition Report Card provided key geographic insights about less healthy retailers around schools, enhancing opportunities for knowledge mobilisation to reduce unhealthy RFE exposures for young people.

Figure 3 shows the difference between traditional and expanded mRFEI measures for census tracts. In Calgary, 46 % of census tracts (n 105) had no change in terms of meeting a threshold mRFEI value ≥ 10 using either the traditional or expanded measures; 13 % of census tracts (n 29) increased their mRFEI to meet the benchmark with the expanded measure; 1 % decreased their mRFEI to not meet it (n 2); and 40 % of census tracts (n 91) had no change with an mRFEI < 10. In Edmonton, 43 % of census tracts (n 86) had no change in meeting an mRFEI ≥ 10 using either of the traditional or expanded measures; 16 % of census tracts (n 32) increased their mRFEI to meet the benchmark with the expanded measure; 3 % decreased their mRFEI to not meet it (n 6); and 38 % of census tracts (n 76) had no change with an mRFEI < 10.

Figure 4 shows how using the expanded measure changed the analysis of retailers within 500 m of schools. In Calgary, the number of schools near less healthy retailers increased from 60 % to 72 % (n 218 to 263); the 12 % change (n 45) meant there was a decrease from 40 % to 28 % of schools (n 149 to 104) without less healthy retailers (P < 0·001). In Edmonton, the number of schools near less healthy retailers increased from 68 % to 77 % (n 235 to 265); the 9 % change (n 30) meant there was a decrease from 41 % to 23 % of schools without less healthy retailers (n 110 to 80) (P < 0·001). Put another way, using the expanded measure, there were only 104 schools (or 28·3 % of the total) in Calgary, and 80 schools (or 23·2 % of the total) in Edmonton, that had no less healthy retailers within 500 m. We consider this additional information on the prevalence of less healthy retailers in proximity to schools as the greatest advantage of using the expanded measure for Alberta’s 2021 Nutrition Report Card.

Discussion

We contribute to RFE measurement literature by fulfilling our objectives of: (1) extending the mRFEI with subcategories capturing additional details about RFE; (2) establishing processes and procedures for redundant coding and ease of annual updating; and (3) demonstrating how the retailer codebook and database were used to generate knowledge mobilisation products for healthy public policy advocacy. Researchers may find value in replicating and tailoring these processes to their local settings.

Expanded v. traditional modified Retail Food Environment Index measures

As described in section 1·3, other researchers have noted incompleteness of traditional RFE measures like the mRFEI(Reference Thornton, Lamb and White12,Reference Ohri-Vachaspati, Martinez and Yedidia20) . We provide empirical evidence for these arguments. By using the traditional measure to calculate the proportion of healthy to less healthy retailers in census tracts (as determined from a small list of three healthy and three less healthy retailer types), we illustrated how the mRFEI omits many retailers potentially shaping purchasing and eating practices. Our expanded metric fills these gaps.

When using the expanded v. traditional measure for the 2021 dataset, the number of classified retailers increased for both cities; the traditional measure captured 26 % of locations in the list provided by provincial health inspectors, whereas the expanded measure captured more than double the number of these locations with 53 %. Although the mean mRFEI across census tracts in Calgary remained stable, and there was a slight increase in Edmonton, overall, changes in the mRFEI for census tracts were negligible in both cities.

However, when using the expanded mRFEI, the healthfulness of RFE surrounding schools decreased. Less healthy retailers in our expanded measure (coffee shops, pharmacies, bakeries, dollar stores, bubble tea restaurants, confectionery, frozen dessert restaurants and food trucks) were frequently found near schools. Therefore, even if RFE across census tracts remained proportionately stable, RFE around schools may be less healthy than previously thought. Schools are key activity settings for young people; the types of retailers young people are exposed to as they travel between home and their activity settings can affect social norms regarding foods considered ‘common’(Reference Brown, Ferdinands and Prowse11,Reference Hollands, Carter and Anwer36) . Research has found that retailers geographically accessible to young people, like those surrounding schools, tend to promote energy-dense, nutrient-poor foods and beverages(Reference Brown, Ferdinands and Prowse11). Repeated, compounding exposures to unhealthy RFE may negatively impact young people’s eating practices at a critical point in their development, with eating habits established at this age often extending into adulthood(Reference Venter and Harris37). As we focused on the RFE, we did not account for the within-school (i.e. organisational) food environment. But to obtain a fuller picture of environmental influences on children’s eating practices, in-school food environment audits at a representative sample of schools in Calgary and Edmonton could provide valuable contextualising data.

The importance of context and transparent reporting in geospatial retail food environments analyses

Geospatial analysis is the most common form of RFE measurement(Reference Kelly, Flood and Yeatman17). Although consolidating and reducing the number of geospatial RFE measurement approaches could enhance comparability across studies, doing so may overlook global RFE variability. Measurement tools developed in one geographical location may not be generalisable to other jurisdictions(Reference Thornton, Lamb and White12). Measurement validity requires staying true to contextual elements of RFE, like how food norms are established in particular geographic and cultural regions. Considering the need for such variability, transparent reporting is essential(Reference Wilkins, Radley and Morris38). Included and excluded retailer types must be reported such that readers can accurately learn from authors’ conclusions. Wilkins et al. developed the Geo-FERN (Geographic Information Systems Food Environment ReportiNg) thirty-eight-item checklist which consists of ‘essential’ and ‘desirable’ criteria regarding retailer data sources, data extraction, retailer construct definitions, geocoding methods and access metrics(Reference Wilkins, Morris and Radley18). Such a checklist can offer structure and a starting point to normalise comprehensive reporting of RFE measurement methods. It may be useful for researchers intending to apply our expanded measure.

Limitations and strengths

Our approach addressed some, but not all, mRFEI limitations (see section 1·2). Our measure is intended for high-level use, recognising it may not capture in-store variation in the healthfulness of food and beverage offerings, and that retailer offerings may not directly correlate with what consumers actually purchase and eat(Reference Moayyed, Kelly and Feng39). To address these broader limitations, researchers have called for multi-level measurement strategies that account for both community (type, availability and accessibility of retailers) and consumer (price, promotion, placement and nutritional quality of food choices) aspects of the RFE(Reference Minaker, Shuh and Olstad6,Reference Caspi, Sorensen and Subramanian40,Reference Engler-Stringer, Le and Gerrard41) . Community food environment measures generally do not account for the accompanying consumer food environment, meaning they may not reflect diet-related exposures of interest. One way to partially address these issues is to conduct in-store/restaurant food environment assessments, using validated tools like the Nutrition Environment Measures Survey for Stores and Restaurants (NEMS-S/R)(Reference Glanz, Sallis and Saelens42,Reference Saelens, Glanz and Sallis43) , in tandem with geographic access measurements(Reference Mahendra, Polsky and Robitaille10). Given our study’s large scale, conducting in-store audits for all 10 843 retailers was not feasible but could be achieved in smaller-scale, community-level RFE assessments.

Geocoding school and retailer locations involved minor manual editing to augment spatial accuracy (e.g. new schools in recent neighbourhood developments). This was important for integrity of the proximity analysis. However, the 500 m distance may not apply to all school types (e.g. distance may not matter for elementary school students who cannot leave schoolgrounds so do not access retailers during the school day but may be greater for high school students who drive). The choice to use census tracts for mRFEI calculations was subject to the modifiable areal unit problem – different values could result from using smaller or larger administrative units when aggregating retailer locations(Reference Prouse, Ramos and Grant44). However, census tracts have been consistently used for Alberta’s Nutrition Report Card and are stable units for annual comparisons. Finally, we relied on secondary datasets that were not ground-truthed (a resource-intensive process), which may inaccurately represent spatial accessibility by including retailers that have closed or neglecting some retailers altogether(Reference Daepp and Black31).

Strengths of our approach include the ease and rigour of our revised coding process. Having detailed, accurate RFE data (e.g. statistics regarding the number and proportions of specific retailer types) is essential for establishing buy-in among policymakers, to demonstrate how local RFE may not offer people enough healthy eating opportunities(Reference Minaker45). The inductive process benefited from being grounded in the team’s years of practical experience applying the coding scheme and our interdisciplinarity (expertise in nutrition, geography and public health). This process was also strengthened by using Google Street View, facilitating deeper knowledge of retailers during desktop coding.

Future research directions

Our retailer subcategories could be used in at least three additional ways by research, practice and/or policy teams: (1) applying our coding beyond Alberta, since many of the retailer categories in our codebook exist elsewhere in North America; (2) extending the mRFEI by inductively developing unique subcategories based on local data and/or excluded categories outlined in Table 1 (with transparent reporting of codebook details); and (3) developing new geospatial indicators based on indicated and other subcategories. For example, Alberta’s Nutrition Guidelines’(46) healthfulness labels for foods and beverages (choose most often, choose sometimes and choose least often) could be applied to retailer subcategories to assess implementation of jurisdiction-specific nutrition policies, as has been done by team collaborators(Reference Brown, Ferdinands and Prowse11,Reference Daepp and Black31,Reference Sim, Veugelers and Prowse47) . Using such guidelines could be one step towards moving past binary categorisations of retailers as healthy/less healthy. Given the increase in less healthy retailers observed using the expanded mRFEI measure in proximity to schools, researchers should continue to problematise young people’s RFE, including RFE around activity settings like recreation centres and childcare facilities(48). Researchers interested in examining adults’ RFE may also benefit from including more retailer types in analyses, like full-service restaurants.

The processes and procedures outlined may be salient for community organisations and education and health authorities keen to catalyse local action for health-promoting change. We are working to translate these coding processes and procedures into an online learning platform and mobile application to guide communities in conducting their own RFE assessments. In doing these assessments, there may be value in examining the potential for retailer misclassification according to neighbourhood demographic composition in Canada, given research findings from Han et al. in the USA suggesting that smaller atypical retailers (e.g. convenience stores and specialty food stores) were more likely to be misclassified in Black census tracts than White census tracts(Reference Han, Powell and Zenk16). The recently released Canadian Food Environment Dataset (Can-FED)(Reference Stevenson, Kaufmann and Colley49), which includes nineteen absolute measures and two relative measures (mRFEI and fast-food restaurant mix) of RFE across Canada, offers additional research and collaboration opportunities, such as applying our expanded mRFEI measures to that dataset.

Lastly, our flexible approach allows for adding emergent retailer subcategories over time. This flexibility is important during the COVID-19 pandemic, which has changed how we interact with RFE. For instance, ‘ghost kitchen’ (i.e. delivery-only restaurant with no sit-in space) openings accelerated with lockdowns, and most restaurants now offer delivery(Reference Goddard50). Even though delivery is geographically dispersed from physical retailer locations, the normalisation of exposure to these retailers may warrant future investigation.

Conclusions

This manuscript presents a methodological advancement by novel adaptation of the traditional mRFEI to an expanded mRFEI, which may be valuable for researchers interested in conducting rigorous and comprehensive RFE assessments. We echo others in their calls for more transparent reporting of the processes and procedures used to measure RFE. We argue that increasing the number and precision of retailer subcategories can facilitate a more robust comparison of RFE healthfulness indicators across time and space. Not only does the expanded measure capture exposure to more retailers, but it also allows for nuanced RFE descriptions. Measuring RFE with more specificity can empower communities to improve food environments with interventions tailored to their challenges like zoning bylaws, restrictions on advertising, calorie labelling and other evidence-based tools.

Acknowledgements

Acknowledgements: The authors would like to acknowledge Jaskiran Gill for her contributions to food retailer coding, Darcy Reynard for his contributions to previous iterations of the geospatial analysis and Krista Milford for project coordination of Alberta’s Nutrition Report Card on Food Environments for Children and Youth. Authorship: A.R.F. contributed to creating the retailer codebook and database, interpreting the findings, and writing the original draft. J.A.B. contributed to creating the retailer codebook and database, GIS analysis, interpreting the findings, and writing the original draft. C.C.N. contributed to GIS analysis and interpreting the findings. K.D.R. and C.I.J.N. contributed to overall study conceptualisation, supervision and funding acquisition. All authors reviewed, edited and approved the final manuscript. Ethics of human subject participation: Not applicable. No human participants, human material or human data were involved in this study.

Financial support:

This work was supported by Alberta Innovates Health Solutions Cancer Prevention Research Opportunity [grant number 201500846]. C.I.J.N. received support as an Applied Public Health Chair from the Canadian Institutes of Health Research in partnership with the Public Health Agency of Canada and Alberta Innovates – Health Solutions [2014–2019; CPP 137909]. Funding bodies were not involved in the design of the study, data collection, data analysis, data interpretation or in the writing of the manuscript.

Conflict of interest:

There are no conflicts of interest.

Footnotes

Alexa R Ferdinands and Jennifer Ann Brown are co-first authors

References

Institute for Health Metrics and Evaluation (IHME) (2020) Canada Profile. Seattle, WA: IHME, University of Washington. http://www.healthdata.org/canada (accessed December 2020).Google Scholar
Polsky, JY, Moubarac, JC & Garriguet, D (2020) Consumption of ultra-processed foods in Canada. Health Rep 31, 315.Google ScholarPubMed
Wilkins, E, Morris, M, Radley, D et al. (2019) Methods of measuring associations between the retail food environment and weight status: importance of classifications and metrics. SSM Popul Health 8, 100404.CrossRefGoogle ScholarPubMed
Frank, LD, Bigazzi, A, Hong, A et al. (2022) Built environment influences on healthy eating and active living: the NEWPATH study. Obesity 30, 424434.CrossRefGoogle ScholarPubMed
Ni Mhurchu, C, Vandevijvere, S, Waterlander, W et al. (2013) Monitoring the availability of healthy and unhealthy foods and non-alcoholic beverages in community and consumer retail food environments globally. Obes Rev 14, 108119.CrossRefGoogle ScholarPubMed
Minaker, LM, Shuh, A, Olstad, DL et al. (2016) Retail food environments research in Canada: a scoping review. Can J Public Health 107, eS413.CrossRefGoogle ScholarPubMed
Olstad, DL, Raine, KD & Nykiforuk, CI (2014) Development of a report card on healthy food environments and nutrition for children in Canada. Prev Med 69, 287295.CrossRefGoogle ScholarPubMed
Needham, C, Sacks, G, Orellana, L et al. (2020) A systematic review of the Australian food retail environment: characteristics, variation by geographic area, socioeconomic position and associations with diet and obesity. Obes Rev 21, e12941.CrossRefGoogle ScholarPubMed
Centers for Disease Control and Prevention (2011) Division of Nutrition Physical Activity and Obesity, Department of Health and Human Services. Children’s Food Environment State Indicator Report. http://www.cdc.gov/obesity/downloads/childrensfoodenvironment.pdf (accessed October 2021).Google Scholar
Mahendra, A, Polsky, JY, Robitaille, É et al. (2017) Geographic retail food environment measures for use in public health. Health Promot Chronic Dis Prev Can 37, 357.CrossRefGoogle ScholarPubMed
Brown, JA, Ferdinands, AR, Prowse, R et al. (2021) Seeing the food swamp for the weeds: moving beyond food retail mix in evaluating young people’s food environments. SSM – Popul Health 14, 100803.CrossRefGoogle ScholarPubMed
Thornton, LE, Lamb, KE & White, SR (2020) The use and misuse of ratio and proportion exposure measures in food environment research. Int J Behav Nutr Phys Act 17, 17.CrossRefGoogle ScholarPubMed
Lucan, SC (2015) Concerning limitations of food-environment research: a narrative review and commentary framed around obesity and diet-related diseases in youth. J Acad Nutr Diet 115, 205212.CrossRefGoogle ScholarPubMed
Lucan, SC, Maroko, AR, Seitchik, JL et al. (2018) Unexpected neighborhood sources of food and drink: implications for research and community health. Am J Prev Med 55, e29e38.CrossRefGoogle ScholarPubMed
Ohri-Vachaspati, P, DeWeese, RS, Acciai, F et al. (2019) Healthy food access in low-income high-minority communities: a longitudinal assessment—2009–2017. Int J Environ Res Public Health 16, 2354.CrossRefGoogle ScholarPubMed
Han, E, Powell, LM, Zenk, SN et al. (2012) Classification bias in commercial business lists for retail food stores in the US. Int J Behav Nutr Phys Act 9, 19.CrossRefGoogle Scholar
Kelly, B, Flood, VM & Yeatman, H (2011) Measuring local food environments: an overview of available methods and measures. Health Place 17, 12841293.CrossRefGoogle ScholarPubMed
Wilkins, EL, Morris, MA, Radley, D et al. (2017) Using geographic information systems to measure retail food environments: discussion of methodological considerations and a proposed reporting checklist (Geo-FERN). Health Place 44, 110117.CrossRefGoogle Scholar
Lytle, LA & Sokol, RL (2017) Measures of the food environment: a systematic review of the field, 2007–2015. Health Place 44, 1834.CrossRefGoogle ScholarPubMed
Ohri-Vachaspati, P, Martinez, D, Yedidia, MJ et al. (2011) Improving data accuracy of commercial food outlet databases. Am J Health Promot 26, 116122.CrossRefGoogle ScholarPubMed
Statistics Canada (2017) North American Industry Classification System (NAICS) Canada, Version 3.0. https://www150.statcan.gc.ca/n1/en/catalogue/12-501-X (accessed October 2021).Google Scholar
Clary, CM, Ramos, Y, Shareck, M et al. (2015) Should we use absolute or relative measures when assessing foodscape exposure in relation to fruit and vegetable intake? Evidence from a wide-scale Canadian study. Prev Med 71, 8387.CrossRefGoogle ScholarPubMed
Pinho, MG, Mackenbach, JD, Oppert, JM et al. (2019) Exploring absolute and relative measures of exposure to food environments in relation to dietary patterns among European adults. Public Health Nutr 22, 10371047.CrossRefGoogle ScholarPubMed
Sacks, G, Robinson, E & Cameron, AJ (2019) Issues in measuring the healthiness of food environments and interpreting relationships with diet, obesity and related health outcomes. Curr Obes Rep 8, 98111.CrossRefGoogle ScholarPubMed
Statistics Canada (2017) Calgary (Census Metropolitan Area), Alberta and Saskatchewan [Province] (table). Census Profile. 2016 Census. Statistics Canada Catalogue no. 98–316-X2016001. Ottawa. Released November 29, 2017. https://www12.statcan.gc.ca/census-recensement/2016/dp-pd/prof/index.cfm?Lang=E (accessed October 2021).Google Scholar
Statistics Canada (2017) Edmonton, CY [Census Subdivision], Alberta and Division No. 11, CDR (Census Division), Alberta (Table). Census Profile. 2016 Census. Statistics Canada Catalogue no. 98–316-X2016001. Ottawa. Released November 29, 2017. https://www12.statcan.gc.ca/census-recensement/2016/dp-pd/prof/index.cfm?Lang=E (accessed October 2021).Google Scholar
Statistics Canada (2017) Alberta [Province] and Canada [Country] (Table). Census Profile. 2016 Census. Statistics Canada Catalogue no. 98–316-X2016001. Ottawa. Released November 29, 2017. https://www12.statcan.gc.ca/census-recensement/2016/dp-pd/prof/index.cfm?Lang=E (accessed November 2021).Google Scholar
City of Calgary (2021) Calgary Food Action Plan. https://www.calgary.ca/ca/cmo/calgary-food-system-assessment-and-action-plan.html (accessed February 2021).Google Scholar
City of Edmonton (2022) City Environmental Strategies. https://www.edmonton.ca/city_government/city_organization/office-of-environment (accessed Jul 2022).Google Scholar
Statistics Canada (2018) Census Tract: Detailed Definition. https://www150.statcan.gc.ca/n1/pub/92-195-x/2011001/geo/ct-sr/def-eng.htm (accessed October 2021).Google Scholar
Daepp, MI & Black, J (2017) Assessing the validity of commercial and municipal food environment data sets in Vancouver, Canada. Public Health Nutr 20, 26492659.CrossRefGoogle ScholarPubMed
Prowse, RJ, Naylor, PJ, Olstad, DL et al. (2018) Food marketing in recreational sport settings in Canada: a cross-sectional audit in different policy environments using the Food and beverage Marketing Assessment Tool for Settings (FoodMATS). Int J Behav Nutr Phys Act 15, 39.CrossRefGoogle Scholar
Benchmarking Food Environments (2021) Alberta’s 2021 Nutrition Report Card on Food Environments for Children and Youth. https://abpolicycoalitionforprevention.ca/evidence/albertas-nutrition-report-card/ (accessed February 2022).Google Scholar
Esri (2021) ArcGIS Pro, Release 2.8 (Software). Environmental Systems Research Institute, Redlands CA. https://www.esri.com (accessed February 2022).Google Scholar
Python (2021) Python, Release 3 (Software). https://www.python.org (accessed February 2022).Google Scholar
Hollands, GJ, Carter, P, Anwer, S et al. (2019) Altering the availability or proximity of food, alcohol, and tobacco products to change their selection and consumption. Cochrane Database Syst Rev 9, CD012573.Google ScholarPubMed
Venter, C & Harris, G (2009) The development of childhood dietary preferences and their implications for later adult health. Nutr Bull 34, 391394.CrossRefGoogle Scholar
Wilkins, E, Radley, D, Morris, M et al. (2019) A systematic review employing the GeoFERN framework to examine methods, reporting quality and associations between the retail food environment and obesity. Health Place 57, 186199.CrossRefGoogle ScholarPubMed
Moayyed, H, Kelly, B, Feng, X et al. (2017) Evaluation of a ‘healthiness’ rating system for food outlet types in Australian residential communities. Nutr Diet 74, 2935.CrossRefGoogle ScholarPubMed
Caspi, CE, Sorensen, G, Subramanian, SV et al. (2012) The local food environment and diet: a systematic review. Health Place 18, 11721187.CrossRefGoogle ScholarPubMed
Engler-Stringer, R, Le, H, Gerrard, A et al. (2014) The community and consumer food environment and children’s diet: a systematic review. BMC Public Health 14, 15.CrossRefGoogle ScholarPubMed
Glanz, K, Sallis, JF, Saelens, BE et al. (2007) Nutrition Environment Measures Survey in Stores (NEMS-S): development and evaluation. Am J Prev Med 32, 282289.CrossRefGoogle ScholarPubMed
Saelens, BE, Glanz, K, Sallis, JF et al. (2007) Nutrition Environment Measures Study in Restaurants (NEMS-R): development and evaluation. Am J Prev Med 32, 273281.CrossRefGoogle ScholarPubMed
Prouse, V, Ramos, H, Grant, JL et al. (2014) How and when scale matters: the modifiable areal unit problem and income inequality in Halifax. Can J Urban Res 23, 6182.Google Scholar
Minaker, LM (2013) Measuring the Food Environment in Canada. www.hc-sc.gc.ca/fn-an/nutrition/pol/index-eng.php (accessed October 2021).Google Scholar
Sim, S, Veugelers, PJ, Prowse, R et al. (2021) Unhealthy food options in the school environment are associated with diet quality and body weights of elementary school children in Canada. Public Health Nutr 24, 45724581.CrossRefGoogle ScholarPubMed
World Health Organization (2016) Report of the Commission on Ending Childhood Obesity. https://apps.who.int/iris/bitstream/handle/10665/204176/9789241510066_eng.pdf?sequence=1 (accessed October 2020).Google Scholar
Stevenson, AC, Kaufmann, C, Colley, RC et al. (2022) A Pan-Canadian dataset of neighbourhood retail food environment measures using Statistics Canada’s Business Register. Health Rep 33, 314.Google ScholarPubMed
Goddard, E (2021) The impact of COVID-19 on food retail and food service in Canada: a second assessment. Can J Agric Econ 69, 167175.CrossRefGoogle Scholar
Figure 0

Table 1 Codebook for categorising retailers based on healthfulness with percent and number of total coded locations†

Figure 1

Table 2 Descriptive and correlational statistics comparing traditional and expanded mRFEI data in Calgary and Edmonton (2021). Values are counts unless otherwise indicated

Figure 2

Fig. 1 Choropleth maps of the (a) traditional and (b) expanded mRFEI measures for census tracts in Calgary, and (c) traditional and (d) expanded mRFEI measures for census tracts in Edmonton (2021). mRFEI, modified Retail Food Environment Index

Figure 3

Fig. 2 Presence or absence of less healthy retailers within 500 m of schools in Calgary using (a) traditional and (b) expanded mRFEI, and within 500 m of schools in Edmonton using (c) traditional and (d) expanded mRFEI (2021). mRFEI, modified Retail Food Environment Index

Figure 4

Fig. 3 Percentage of census tracts meeting the benchmark of mRFEI ≥ 10 in Calgary and Edmonton, comparing the expanded v. traditional measures (2021). mRFEI, modified Retail Food Environment Index

Figure 5

Fig. 4 Percentage of schools with one or more less healthy retailers within 500 m, comparing the expanded v. the traditional measures (2021)