Abstract
Background:
There is no singular approach to measuring the food environment suitable for all studies. Understanding terminology, methodology, and common issues is crucial to choosing the best approach.
Objective:
This review is designed to support a shared understanding so diverse multi-institutional teams engaged in food environment measurement can justify their measurement choices and have informed discussions about reasons for measurement strategies to vary across projects.
Methods:
This guide defines key terms and provides annotated resources identified as a useful starting point for exploring the food environment literature. The writing team was an academic-practice collaboration, reflecting on the experience of a multi-institutional team focused on retail environments across the US relevant to cardiovascular disease.
Results:
Terms and annotated resources are divided into three sections: food environment constructs, classification and measures, and errors and strategies to reduce error. Two examples of methods and challenges encountered while measuring the food environment in the context of a US health department are provided. Researchers and practice professionals are directed to the Food Environment Electronic Database Directory (https://www.foodenvironmentdirectory.com/) for comparing available data resources for food environment measurement, focused on the US; this resource incorporates updates informed by user input and literature reviews.
Discussion:
Measuring the food environment is complex and risks oversimplification. This guide serves as a starting point but only partially captures some aspects of neighborhood food environment measurement.
Conclusions:
No single food environment measure or data source meets all research and practice objectives. This shared starting point can facilitate theoretically grounded food environment measurement.
Classifications: Built Environment, Food Environment
MeSH Key Words: Neighborhood Characteristics, Geographic Information Systems, Data Sources, Environment and Public Health, Public Health Practice, Resource Guide
1. BACKGROUND
The factors that affect an individual’s decisions about obtaining and consuming food, including the availability, convenience, accessibility, and acceptability of food sources, is referred to as the foodscape [1] or food environment [2]. The neighborhood food environment in particular has a potential role in influencing diet-related health outcomes and may be modified by food policy [3, 4].
No single approach to measuring the neighborhood food environment is suitable for all studies or uses. Awareness of terminology, concepts, measurement options, and common data quality issues can support appropriate use of measures of the food environment. Prior glossaries [5–7] and reviews [8, 9] have defined food environment-related terms, but are not focused on neighborhood food environment measurement and associated challenges for those new to food environment measurement.
2. METHODS
This guide and the Food Environment Electronic Database Directory (see Table 1) were developed through an academic-practice collaboration, reflecting on the experience of a multi-institutional team focused on retail environments across the US relevant to cardiovascular disease [10–15]. While different teams at academic and practice institutions are engaged in food environment measurement, this critical review is designed to support a shared understanding so that each can justify their measurement choices and initiate informed discussion about reasons for measurement strategies to vary across projects.
Table 1.
Selected References to Guide Food Environment Research
Author | Use |
---|---|
Constructs | |
Downs et al [18] |
|
Nodari et al [6] |
|
Turner et al [24] |
|
Classification and Measurement | |
Online resource created by this writing team |
|
Swanson, G. [59] |
|
Lytle, LA. [40] |
|
Ohri-Vachaspati, P & Leviton, L. [19] |
|
Wilkins et al. [29] |
|
Types of Errors and How to Mitigate | |
Han et al. [60] |
|
Jones et al. [46] |
|
Sacks, G., Robinson, E. & Cameron, J. [39] |
|
Hirsch et al. [14] |
|
We aim to complement prior work through sharing selected definitions, annotated resources (Table 1), and two examples of food environment measurement by a local health department within the US.
Terms and resources are organized below to inform (1) constructs, (2) classification and characterization, and (3) cautions about errors and their mitigation.
3. GLOSSARY OF TERMS
3.1. Constructs: Clarifying what to measure in the food environment
This section describes conceptual elements used to define food environments.
Food Environment: Range of food products and food sources that can be accessed in one’s everyday environment (including stores and restaurants within the built environment and mobile vendors or informal food sales), providing opportunities or constraints to dietary choices. Includes availability, convenience, accessibility, and acceptability of food sources [6, 16–19]. Is situated within the broader food system with other factors that impact dietary outcomes [20] and which can be integrated over time [21].
Availability: Quantity and diversity of food stores or other establishments that can be physically accessed by individuals, often defined within a geographic area. Can also be defined for specific types of food or beverage items in institutional settings such as offices and schools, based on offerings within on-site cafeterias or vending machines [4, 6, 16, 17].
Convenience: Qualities of retail and food options that minimize effort needed from consumers to purchase, prepare, and consume food. Includes establishment characteristics beyond availability, such as store hours, delivery services, and food product characteristics, such as shelf-life [6, 16].
- Accessibility: Qualities and characteristics affecting how readily individuals can purchase and consume food items. Includes both convenience and whether the consumer has sufficient time or transportation mode options to overcome barriers to access. Importantly includes Affordability, which depends on both food prices and individual purchasing power [4, 6, 16, 17].
- Eligibility and use restrictions for Nutrition Assistance Programs such as the Supplemental Nutrition Assistance Program (SNAP) and the Special Supplemental Nutrition Program for Women, Infants, and Children (WIC) are food policy factors related to addressing food insecurity [22]. The acceptance of corresponding payment via Electronic Benefits Transfer (EBT) cards varies [22, 23].
- Much research has focused on food deserts as a limiting factor to healthy food consumption, though area-based sociodemographic factors may be more crucial [24].
Acceptability: Agreement between available foods and population food preferences, factoring in taste, culture, customs, and knowledge [4, 16].
- Food Quality: Perceived and quantifiable characteristics of food products that impact alignment with consumer needs and preferences. For a health-oriented consumer, quality may include density of desired nutrients relative to unhealthy components (e.g., additives, sugar, sodium, or trans fats). Can also include freshness and appearance [6], or conversely, the degree to which foods have been processed.
- NOVA classification defines Ultra-Processed Foods as ingredient and meal formulations resulting from extensive industrial-scale processing, often containing artificial colors, flavors, emulsifiers, and other additives [25]. Implications of ultra-processed food intake continues to be examined with both a health and equity lens [26, 27], alongside associated nutrition characteristics and consumption patterns.
Food Retail Store: Commercial locations with food products available, including food to be prepared or consumed off-premises. May include retail locations that are not primarily food retailers, but offer some food items for purchase (e.g., pharmacies, department stores) [16, 28]. Note that classification of food retail stores selling a wide range of items may rely on which items are most salient, as defined by typical consumer intentions, marketing, relative pricing, or shelf space [29]. The classification of a store as healthy or unhealthy has national and cultural context and requires a subjective lens rather than uniformity [30].
Urban Agriculture: Systems and settings for cultivating, processing, and distributing fresh produce and animal products as food in urban and suburban settings. Includes community gardens, rooftop farms, and hydro-, aero-, or aquaponic facilities. Assumes a scale of production and commerce beyond personal consumption or informal community sharing [31, 32]. Though peri-urban agriculture is sometimes included within this definition, the two differ in spatial distribution and can be considered distinct parts of a food system [33].
3.2. Classification and measurement: Operationalizing food environment constructs
This section covers operationalization of Food Environment measures and sources of data (including those listed in the Food Environment Electronic Database Directory, an online resource to be updated based on ongoing user input and annual literature review, see Table 1).
Food Establishment Classification: Systematic use of criteria to define Food Retail Stores of interest (e.g., supermarkets, convenience stores, fast food outlets). Commonly incorporates standard coding systems and may consider establishment characteristics such as floor space, number of employees, or annual sales [29]. Granular classification requires attention to potential overlap among large (warehouses vs supermarkets) or small (convenience stores vs bodegas) food stores, and among restaurants (national chain fast-food vs other casual, quick service). Adopting or adapting previously published definitions is recommended to increase comparability between studies [29], unless there is scientific justification for creating a new measure. However, when existing classification definitions prove insufficient, prior models can guide tool development and testing [34].
- Standard Coding Systems: Numeric codes with corresponding labels for retail and other establishments to categorize establishment type, which may be included in establishment-level datasets used to measure the Food Environment. Comparison to ground-truthed data may aid understanding in how comprehensively such systems reflect food items available. Two common systems are:
- Standard Industrial Classification (SIC): Codes of 4 to 8 digits that group together similar establishment types: the first two numbers represent the major industry, the third digit represents subgroups within that industry, and subsequent digits give further specificity [35]. The U.S. government stopped updating codes in 1987, though original codes have since been expanded. Mainly used by the private sector for economics and marketing.
- North American Industry Classification System (NAICS): A standard created by U.S. government agencies to replace the SIC system, providing more granular classification and used for governmental operations and classifications. NAICS uses a six-digit system; the first two digits represent major sector, third represents subsector, fourth represents industry group, fifth represents industry type, and sixth represents the national industry (“0” generally indicates that the NAICS industry and US industry are the same) [35, 36].
Store Catchment Area: The geographic area primarily served by a given Food Retail Store. Can be defined in a variety of ways including distance, travel time, or transit accessibility, and will likely be larger in rural and low population density settings [37]. Defining catchment areas is useful for identifying demographics and preferences of customers that inform context-specific measurement of Food Quality, Accessibility, and Acceptability.
- Neighborhood: A geographically and socially delineated context for individuals’ behavior and environment. These may be defined through distance-based or political boundaries around homes, workplaces, schools, or commuting routes [38, 39]. People spend time in multiple settings; no single geographic unit perfectly characterizes the physical, social, cultural, and policy environments experienced [40].
- Both Geographic Extent (entire area throughout which neighborhoods will be measured) and Scale of Measurement (geographic units used for characterization and comparison have implications for errors encountered and feasibility of ground-truthing or other efforts to improve validity. Smaller-scale measurement and projects with a smaller geographic extent may allow more stakeholder involvement, tailoring of existing neighborhood definitions and measures; a larger geographic extent makes such methods less feasible, though still worth considering for a subsample of geographic units.
Density-Based Measures: Measures characterizing intensity of food establishment presence within a boundary, potentially relevant to both Availability and Accessibility. Estimates of density commonly use count of establishments within a given category as the numerator, and a defined land area as a denominator. However, retail density measures may present a challenge for interpretation, especially across settings of different urbanicity or within high density settings [39, 41, 42].
Ratio-Based Measures: Measures characterizing relative intensity across food establishment categories within a boundary, which may point to their relative Convenience. Commonly relies on binary (e.g., healthy/unhealthy) categorization [43]; estimates commonly include healthy retail establishment (variously defined) counts in the numerator and unhealthy or total food retail in the denominator, leading to challenges in low-density settings where counts may equal 0.
- Longitudinal Measures: Measures which incorporate multiple moments or periods of time, providing a way to examine trends across years or decades. Longitudinal measures of both Food Environment and dietary or health outcomes allow for examination of temporal sequencing in studies of the Food Environment on health, an identified gap in the Food Environment literature [44]. Requires consistent classification methods and temporally appropriate linked health data [14].
- Supermarket Transition or Greenlining: A longitudinal process bringing in Food Retail Stores to an area that emphasize gourmet, healthy, or natural ingredients over Affordability, which may be concurrent with gentrification, urbanization, or related sociodemographic transitions. Such changes may align with Food Quality preferences of only a segment of the population in the store catchment area, with rising food costs exacerbating inequities in food insecurity particularly if concurrent with a shrinking supply of affordable housing and amenities [45].
Sociodemographic Indicators: Characteristics of individuals and geographic units that may confound or mediate Food Environment effects. These are likely to impact where a person lives and how food is acquired, as well as impacting overall health for reasons unrelated to the Food Environment; commonly include personal and area-based education, income, and wealth, and may also incorporate household composition and area-level patterns by identity groups such as gender, race, and ethnicity, or may combine several area-based measures into a single index variable [39].
3.3. Errors: What goes wrong and how to mitigate
Terms in this final section describe sources of error that commonly arise when operationalizing food environment measures, and strategies to limit or quantify such error.
Duplication: A single food retail location appearing multiple times in a dataset or contributing to the count across multiple food retail categories. Can be addressed through systematic criteria to identify and remove duplicates. Criteria to define duplicates may differ across food retail categories; large establishments such as supermarkets at the same address in the same year are likely to represent duplication error, yet smaller establishments such as fast-food restaurants are commonly co-located, requiring other information such as business name to identify duplicates [46].
- Misclassification: Misalignment between an establishment’s food offerings and assigned retail category. Misclassification may be reduced through systematic spot checking or field validation [19], followed by refinement of classification definitions and documenting decision rules [34, 46, 47].
- Low Sensitivity: Not all relevant food establishments are correctly included, resulting in undercount for a given food retail category.
- Low Precision: Food establishments are incorrectly included, exaggerating the count for a given food retail category.
Spatial Error: Inaccurate location information, which can result from errors in the address or geocoding reference files. Consequences typically include inaccurate area-based counts, attenuated estimates of association, and reduced statistical power. Bias can also arise from systematic differences in spatial error over time or along a gradient of urbanicity (spatial errors are typically larger in rural areas than urban and suburban areas) [29]. Spatial error can be reduced through improving address completeness or the geocoding process. Documentation of geocoding methods and results can inform discussion of limitations or planning of quantitative bias analyses to evaluate likely impact on results [46, 48].
Modifiable Aerial Unit Problem: A fallacy that arises in interpretation, especially when results from a geographic unit selected because of ease of use or data availability are assumed to hold for an area definition that is more personalized or optimally-scaled. Associations across differing geographic scales may not be replicable when units differ in size (e.g., census tract versus county) or where boundaries are drawn (e.g., circular buffers centered on home addresses versus centered on postal code centroids) [49]. If such associations are not replicable (robust to a differently defined geographic unit), it may be concluded that such uncertainty produces an error known as the Uncertain Geographic Context Problem, whereby the selection of the most relevant spatial context is unclear. Newly developed statistical methods are beginning to address the impact of food environment features on health outcomes at different geographic scales [50].
Temporal Misalignment: Inaccuracies in food environment measures due to using data from a time period dictated by data availability or convenience, rather than the time period anticipated to influence dietary and health outcomes [51]. Identification of frequently updated longitudinal food environment data makes it possible to minimize temporal misalignment, especially if combined with residential histories or activity spaces to capture where individuals are located across time [39, 52].
Model Misspecification: Biased or oversimplified patterns of association resulting from inaccurate assumptions embedded in statistical modeling. Assumptions are commonly violated due to non-linearity, non-random missing data, or spatial non-independence [52, 53]. Regarding non-linear associations between food environment measures and health outcomes, some types of food retail may have the largest influence when rare (as a Limiting Factor), as absence most strongly constrains choice; once the same retail category or food type becomes common (reaching Saturation), the dietary behavior and health effects of each additional establishment may be diminished [54].
4. Practice implications: Examples from practice at a local health department
These terms may feature into the clear articulation of research aims regarding measurement, operationalization of the food environment, and any tradeoffs or potential shortcomings. The following examples illustrate use of food environment by the New York City (NYC) Department of Health and Mental Hygiene, and how purpose and geographic extent differ in ways that inform food environment measurement.
Example 1. Incorporating food environment into NYC Community Health Profiles
Purpose and geographic extent: The Health Department periodically publishes Community Health Profiles [55] to summarize health statistics across the city’s 59 community districts, publicly offering an historical archive. Each Community Health Profile visualizes place-based health determinants and includes geographic and social health disparities. While food environment is represented as a single ratio-based indicator in 2018, it appears alongside many other community indicators and presented within the context of myriad social and environmental (or geographic) determinants of health. The final selection of the ratio-based indicator required: a review of measures available throughout the geographic extent, a balance of simplicity and interpretability, and audience appropriateness (non-specialists, community members) [56].
Construct identified for inclusion: The ratio of supermarkets to bodegas (corner stores), a measure rooted in the food environment and health literature [43, 57]. This is relevant to inequities in availability and convenience. Food items sold in supermarkets and bodegas typically differ in nutritional quality and these venues also differ in relative affordability of fresh items. The selected ratio-based measure has advantages of interpretability and ease of comparison across geographic areas within an urban setting.
Operationalization of the selected ratio-based measure: Counts of supermarkets and bodegas come from an open-source list of retail stores from the New York State Department of Agriculture and Markets. Summary health statistics are presented alongside the supermarket to bodega ratio in each Community Health Profile report.
Limiting but not eliminating error: Data curation techniques such as deduplication, classification and spatial error mitigation manage errors, improve classification of stores (as supermarkets, bodegas, or neither), and allow comparability across community districts. For a given year, a cross-sectional list of food stores in New York City contains tens of thousands of entries; inclusion of food establishments throughout all 5 boroughs of New York City makes ground-truthing (refinement of food retail store categories) cost prohibitive. Reliance on secondary data sources may cause the calculated ratio to be affected by errors including duplication, misclassification, and spatial error, even after reducing the extent of such error via data curation steps, as described in previous studies [14, 46, 58].
Example 2. Identifying Eligible Corner Stores for Shop Healthy NYC Intervention Planning
Purpose and geographic extent: Shop Healthy NYC is a precision public health initiative implemented by the Health Department that targets neighborhoods with a high relative prevalence of diet-related chronic disease (e.g., overweight and obesity) to receive increased access to healthy food. On a rolling, yearly basis, eligible supermarkets and bodegas are recruited from a limited geography of 3–4 ZIP codes. In this year-long, two-part intervention, Shop Healthy staff work with food retailers to increase stock and promotion of healthier products.
Construct identified for pre-intervention planning: Prior to retail store recruitment, assessment of availability and eligibility of supermarkets and bodegas.
Operationalization using secondary data and ground-truthing: Establishments are initially identified from both the commercially licensed Reference USA and publicly licensed New York State Department of Agriculture and Markets. Food Establishment classifications are derived from a retail audit, using zip code geographic extent. After applying exclusion criteria (e.g., chain stores), further measures of the food environment (i.e., availability, convenience and accessibility, affordability, acceptability, and food quality) are evaluated to identify candidate ZIP codes for this intervention. Finally, in-person interactions with retail food store owners are conducted.
Comprehensive mapping of all potentially eligible locations is important for a fair process of planning and resource allocation, and for building trust with stakeholders.
Multi-stage checks to minimize error: Secondary data sources offer preliminary categorization of food stores based on square footage and standard coding systems, though errors remain even following deduplication and other curating processes. In-person confirmation by study staff allows refinement of mapped establishments by deleting, adding, or re-classifying on a block-by-block basis to minimize errors in identification of eligible stores.
5. DISCUSSION
Conceptualizing, operationalizing, and limiting error in measures of the food environment is not a simple or straightforward task. These decisions are dependent on the overall purpose, resource constraints, and environmental and social context. The heterogeneity of food stores and dynamic nature of food environments means that efficient measurement risks oversimplification. The terms and examples help orient researchers to the complexities of measuring a local food environment. However, these terms and examples represent only a starting point and do not fully capture every nuance of measuring food environment.
6. CONCLUSION
The terms, errors (and strategies for managing errors), annotated resources (including our Food Environment Electronic Database Directory, see Table 1), and examples above offer a starting point for further exploration and advancement of neighborhood food environment measurement and research to inform action to benefit population health. This guide fills a much needed gap in the local food environment research space by providing a shared starting point for designing research and identifying and managing potential errors and biases.
Acknowledgements
Funding
This research was supported by the Drexel University Urban Health Collaborative Master’s Fellowship program. Financial support for the neighborhood food environment research foundational to developing this paper was from the National Institute of Aging (grants 1R01AG049970, 3R01AG049970-04S1, 2R56AG049970-05A1), Commonwealth Universal Research Enhancement (C.U.R.E) program funded by the Pennsylvania Department of Health - 2015 Formula award - SAP #4100072543, the Urban Health Collaborative at Drexel University, and the Built Environment and Health Research Group at Columbia University.
The online resource available at https://www.foodenvironmentdirectory.com/ was created with support from the Health Resources and Services Administration (HRSA) of the U.S. Department of Health and Human Services (HHS) under grant number 1UB6HP31689-01-00 “Public Health Training Centers.”
Information or content and conclusions are those of the authors and should not be construed as the official position or policy of, nor should any endorsements be inferred by HRSA, HHS or the U.S. Government.
Abbreviations
- EBT
Electronic Benefits Transfer
- NAICS
North American Industry Classification System
- NYC
New York City
- SIC
Standard Industrial Classification
- SNAP
Supplemental Nutrition Assistance Program
- WIC
Special Supplemental Nutrition Program for Women, Infants, and Children
Footnotes
Ethical Statement:
The work represented in this manuscript did not require ethical approval, because no individual-level data were used in developing this resource guide, which instead relies on experience within our academic-practice collaboration and a critical review of prior published literature.
Competing interests
The authors declare that they have no competing interest.
Conflict of Interest Statement:
The authors declare that there are no conflicts of interest.
Financial Disclosures:
The authors declare that there are no financial disclosures.
References
- [1].Clary C, Matthews SA, Kestens Y. Between exposure, access and use: Reconsidering foodscape influences on dietary behaviours. Health Place. 2017;44:1–7. [DOI] [PubMed] [Google Scholar]
- [2].Glanz K, Sallis JF, Saelens BE, Frank LD. Healthy nutrition environments: concepts and measures. Am J Health Promot. 2005;19(5):330–3, ii. DOI: 10.4278/0890-1171-19.5.330. [DOI] [PubMed] [Google Scholar]
- [3].Rose D, Bodor JN, Hutchinson PL, Swalm CM. The importance of a multi-dimensional approach for studying the links between food access and consumption. J Nutr. 2010;140(6):1170–4. DOI: 10.3945/jn.109.113159. [DOI] [PMC free article] [PubMed] [Google Scholar]
- [4].Caspi CE, Sorensen G, Subramanian SV, Kawachi I. The local food environment and diet: a systematic review. Health Place. 2012;18(5):1172–87. DOI: 10.1016/j.healthplace.2012.05.006. [DOI] [PMC free article] [PubMed] [Google Scholar]
- [5].A4NH. Glossary: Food Systems London, England (UK): Agriculture, Nutrition and Health Academy Food Environments Working Group (ANH-FEWG) Innovative Methods and Metrics for Agriculture and Nutrition Actions (IMMANA) Programme; 2020. [Available from: https://a4nh.cgiar.org/2020/01/26/glossary-food-systems/. [Google Scholar]
- [6].Nodari GR, Kennedy G, Herforth A, Downs S, Brouwer I. Background Note on Food Environment: Prepared for the CGIAR A4NH Consultative Food Environment Workshop, Nov 5–7, 2019. London, England (UK); 2020. p. 18. Available from: https://a4nh.cgiar.org/files/2020/03/FINAL-Background-note-on-Food-Environment_Revised.pdf. [Google Scholar]
- [7].Thornton LE, Pearce JR, Kavanagh AM. Using Geographic Information Systems (GIS) to assess the role of the built environment in influencing obesity: a glossary. Int J Behav Nutr Phys Act. 2011;8(1):71. DOI: 10.1186/1479-5868-8-71. [DOI] [PMC free article] [PubMed] [Google Scholar]
- [8].Charreire H, Casey R, Salze P, Simon C, Chaix B, Banos A, et al. Measuring the food environment using geographical information systems: a methodological review. Public Health Nutr. 2010;13(11):1773–85. DOI: 10.1017/S1368980010000753. [DOI] [PubMed] [Google Scholar]
- [9].Granheim SI, Lovhaug AL, Terragni L, Torheim LE, Thurston M. Mapping the digital food environment: A systematic scoping review. Obes Rev. 2022;23(1):e13356. DOI: 10.1111/obr.13356. [DOI] [PubMed] [Google Scholar]
- [10].Tabb LP, Roux AVD, Barber S, Judd S, Lovasi G, Lawson A, et al. Spatially varying racial inequities in cardiovascular health and the contribution of individual- and neighborhood-level characteristics across the United States: The REasons for geographic and racial differences in stroke (REGARDS) study. Spat Spatiotemporal Epidemiol. 2022;40:100473. DOI: 10.1016/j.sste.2021.100473. [DOI] [PMC free article] [PubMed] [Google Scholar]
- [11].India-Aldana S, Kanchi R, Adhikari S, Lopez P, Schwartz MD, Elbel BD, et al. Impact of land use and food environment on risk of type 2 diabetes: A national study of veterans, 2008–2018. Environ Res. 2022;212(Pt A):113146. DOI: 10.1016/j.envres.2022.113146. [DOI] [PMC free article] [PubMed] [Google Scholar]
- [12].Lovasi GS, Johnson NJ, Altekruse SF, Hirsch JA, Moore KA, Brown JR, et al. Healthy food retail availability and cardiovascular mortality in the United States: a cohort study. BMJ Open. 2021;11(7):e048390. DOI: 10.1136/bmjopen-2020-048390. [DOI] [PMC free article] [PubMed] [Google Scholar]
- [13].Garg PK, Platt JM, Hirsch JA, Hurvitz P, Rundle A, Biggs ML, et al. Association of neighborhood physical activity opportunities with incident cardiovascular disease in the Cardiovascular Health Study. Health Place. 2021;70:102596. DOI: 10.1016/j.healthplace.2021.102596. [DOI] [PMC free article] [PubMed] [Google Scholar]
- [14].Hirsch JA, Moore KA, Cahill J, Quinn J, Zhao Y, Bayer FJ, et al. Business Data Categorization and Refinement for Application in Longitudinal Neighborhood Health Research: a Methodology. J Urban Health. 2021;98(2):271–84. DOI: 10.1007/s11524-020-00482-2. [DOI] [PMC free article] [PubMed] [Google Scholar]
- [15].Gullon P, Bilal U, Hirsch JA, Rundle AG, Judd S, Safford MM, et al. Does a physical activity supportive environment ameliorate or exacerbate socioeconomic inequities in incident coronary heart disease? J Epidemiol Community Health. 2020. DOI: 10.1136/jech-2020-215239. [DOI] [PMC free article] [PubMed] [Google Scholar]
- [16].Turner C, Aggarwal A, Walls H, Herforth A, Drewnowski A, Coates J, et al. Concepts and critical perspectives for food environment research: A global framework with implications for action in low- and middle-income countries. Glob Food Sec. 2018;18:93–101. DOI: 10.1016/j.gfs.2018.08.003. [DOI] [Google Scholar]
- [17].Turner C, Kadiyala S, Aggarwal A, Coates J, Drewnowski A, Hawkes C, et al. Concepts and methods for food environment research in low and middle income countries. London, UK: Agriculture, Nutrition and Health Academy Food Environments Working Group (ANH-FEWG) Innovative Methods and Metrics for Agriculture and Nutrition Actions (IMMANA) Programme; 2017. [Google Scholar]
- [18].Downs SM, Ahmed S, Fanzo J, Herforth A. Food Environment Typology: Advancing an Expanded Definition, Framework, and Methodological Approach for Improved Characterization of Wild, Cultivated, and Built Food Environments toward Sustainable Diets. Foods. 2020;9(4):532. DOI: 10.3390/foods9040532. [DOI] [PMC free article] [PubMed] [Google Scholar]
- [19].Ohri-Vachaspati P, Leviton LC. Measuring food environments: a guide to available instruments. Am J Health Promot. 2010;24(6):410–26. DOI: 10.4278/ajhp.080909-LIT-190. [DOI] [PubMed] [Google Scholar]
- [20].Langellier BA, Kuhlberg JA, Ballard EA, Slesinski SC, Stankov I, Gouveia N, et al. Using community-based system dynamics modeling to understand the complex systems that influence health in cities: The SALURBAL study. Health Place. 2019;60:102215. DOI: 10.1016/j.healthplace.2019.102215. [DOI] [PMC free article] [PubMed] [Google Scholar]
- [21].Widener MJ, Shannon J. When are food deserts? Integrating time into research on food accessibility. Health Place. 2014;30:1–3. [DOI] [PubMed] [Google Scholar]
- [22].Gustafson A, Lewis S, Perkins S, Wilson C, Buckner E, Vail A. Neighbourhood and consumer food environment is associated with dietary intake among Supplemental Nutrition Assistance Program (SNAP) participants in Fayette County, Kentucky. Public Health Nutr. 2013;16(7):1229–37. DOI: 10.1017/S1368980013000505. [DOI] [PMC free article] [PubMed] [Google Scholar]
- [23].Wood BS, Horner MW. Understanding Accessibility to Snap-Accepting Food Store Locations: Disentangling the Roles of Transportation and Socioeconomic Status. Appl Spat Anal Policy. 2015;9(3):309–27. DOI: 10.1007/s12061-015-9138-2. [DOI] [Google Scholar]
- [24].Turner C, Kadiyala S, Aggarwal A, Coates J, Drewnowski A, Hawkes C, et al. Concepts and methods for food environment research in low and middle income countries. London, England (UK); 2017. p. Available from: https://a4nh.cgiar.org/2017/05/04/anh-academy-launches-technical-brief-on-foodenvironments/. [Google Scholar]
- [25].Monteiro CA, Cannon G, Levy RB, Moubarac JC, Louzada ML, Rauber F, et al. Ultra-processed foods: what they are and how to identify them. Public Health Nutr. 2019;22(5):936–41. DOI: 10.1017/S1368980018003762. [DOI] [PMC free article] [PubMed] [Google Scholar]
- [26].Gibney MJ, Forde CG, Mullally D, Gibney ER. Ultra-processed foods in human health: a critical appraisal. Am J Clin Nutr. 2017;106(3):717–24. DOI: 10.3945/ajcn.117.160440. [DOI] [PubMed] [Google Scholar]
- [27].Gibney MJ. Ultra-Processed Foods: Definitions and Policy Issues. Curr Dev Nutr. 2019;3(2):nzy077. DOI: 10.1093/cdn/nzy077. [DOI] [PMC free article] [PubMed] [Google Scholar]
- [28].Lucan SC, Maroko AR, Seitchik JL, Yoon DH, Sperry LE, Schechter CB. Unexpected Neighborhood Sources of Food and Drink: Implications for Research and Community Health. Am J Prev Med. 2018;55(2):e29–e38. DOI: 10.1016/j.amepre.2018.04.011. [DOI] [PMC free article] [PubMed] [Google Scholar]
- [29].Wilkins EL, Morris MA, Radley D, Griffiths C. Using Geographic Information Systems to measure retail food environments: Discussion of methodological considerations and a proposed reporting checklist (Geo-FERN). Health Place. 2017;44:110–7. DOI: 10.1016/j.healthplace.2017.01.008. [DOI] [PubMed] [Google Scholar]
- [30].Vernez Moudon A, Drewnowski A, Duncan GE, Hurvitz PM, Saelens BE, Scharnhorst E. Characterizing the food environment: pitfalls and future directions. Public Health Nutr. 2013;16(7):123843. DOI: 10.1017/S1368980013000773. [DOI] [PMC free article] [PubMed] [Google Scholar]
- [31].Urban Agriculture Grants and Engagement Opportunities (US): US Department of Agriculture; 2021. [cited 2021 November 15]. Available from: https://www.farmers.gov/your-business/urban/opportunities. [Google Scholar]
- [32].What is urban farming? (US): Greensgrow; 2021. [cited 2021 November 15]. Available from: https://www.greensgrow.org/urban-farm/what-is-urban-farming/. [Google Scholar]
- [33].Opitz I, Berges R, Piorr A, Krikser T. Contributing to food security in urban areas: differences between urban agriculture and peri-urban agriculture in the Global North. Agric Human Values. 2015;33(2):341–58. DOI: 10.1007/s10460-015-9610-2. [DOI] [Google Scholar]
- [34].Lake AA, Burgoine T, Greenhalgh F, Stamp E, Tyrrell R. The foodscape: classification and field validation of secondary data sources. Health Place. 2010;16(4):666–73. DOI: 10.1016/j.healthplace.2010.02.004. [DOI] [PubMed] [Google Scholar]
- [35].Henneberry B. SIC Codes vs. NAICS Codes - What’s the Difference? New York, NY (US): Thomas Publishing Company; 2021. [cited 2021 November 15]. Available from: https://www.thomasnet.com/articles/other/sic-codes-vs-naics-codes-what-s-the-difference/. [Google Scholar]
- [36].ECPC. North American Industry Classification System. (US): Office of Management and Budget; 2022. p. 958. Available from: https://www.census.gov/naics/reference_files_tools/2022_NAICS_Manual.pdf. [Google Scholar]
- [37].Brown B. What is a Catchment Area? + Methods & Tools for Your Analysis (US): Safe Graph; 2021. [cited 2021 November 15]. Available from: https://www.safegraph.com/blog/catchment-area. [Google Scholar]
- [38].Burgoine T, Monsivais P. Characterising food environment exposure at home, at work, and along commuting journeys using data on adults in the UK. Int J Behav Nutr Phys Act. 2013;10(1):85. DOI: 10.1186/1479-5868-10-85. [DOI] [PMC free article] [PubMed] [Google Scholar]
- [39].Sacks G, Robinson E, Cameron AJ. Issues in Measuring the Healthiness of Food Environments and Interpreting Relationships with Diet, Obesity and Related Health Outcomes. Curr Obes Rep. 2019;8(2):98–111. DOI: 10.1007/s13679-019-00342-4. [DOI] [PubMed] [Google Scholar]
- [40].Lytle LA. Measuring the food environment: state of the science. Am J Prev Med. 2009;36(4 Suppl):S134–44. DOI: 10.1016/j.amepre.2009.01.018. [DOI] [PMC free article] [PubMed] [Google Scholar]
- [41].Thornton LE, Pearce JR, Kavanagh AM. Using Geographic Information Systems (GIS) to assess the role of the built environment in influencing obesity: a glossary. International Journal of Behavioral Nutrition and Physical Activity. 2011;8(1):71. DOI: 10.1186/1479-5868-8-71. [DOI] [PMC free article] [PubMed] [Google Scholar]
- [42].Rundle A, Neckerman KM, Freeman L, Lovasi GS, Purciel M, Quinn J, et al. Neighborhood food environment and walkability predict obesity in New York City. Environ Health Perspect. 2009;117(3):442–7. DOI: 10.1289/ehp.11590. [DOI] [PMC free article] [PubMed] [Google Scholar]
- [43].Thornton LE, Lamb KE, White SR. The use and misuse of ratio and proportion exposure measures in food environment research. Int J Behav Nutr Phys Act. 2020;17(1):118. DOI: 10.1186/s12966-020-01019-1. [DOI] [PMC free article] [PubMed] [Google Scholar]
- [44].Lytle LA, Sokol RL. Measures of the food environment: A systematic review of the field, 2007–2015. Health Place. 2017;44:18–34. DOI: 10.1016/j.healthplace.2016.12.007. [DOI] [PubMed] [Google Scholar]
- [45].Anguelovski I. Healthy Food Stores, Greenlining and Food Gentrification: Contesting New Forms of Privilege, Displacement and Locally Unwanted Land Uses in Racially Mixed Neighborhoods. Int J Urban Reg Res. 2015;39(6):1209–30. DOI: 10.1111/1468-2427.12299. [DOI] [Google Scholar]
- [46].Jones KK, Zenk SN, Tarlov E, Powell LM, Matthews SA, Horoi I. A step-by-step approach to improve data quality when using commercial business lists to characterize retail food environments. BMC Res Notes. 2017;10(1):35. DOI: 10.1186/s13104-016-2355-1. [DOI] [PMC free article] [PubMed] [Google Scholar]
- [47].Ohri-Vachaspati P, Martinez D, Yedidia MJ, Petlick N. Improving data accuracy of commercial food outlet databases. Am J Health Promot. 2011;26(2):116–22. DOI: 10.4278/ajhp.100120-QUAN-21. [DOI] [PubMed] [Google Scholar]
- [48].Lash TL, Fox MP, Fink AK. Applying quantitative bias analysis to epidemiologic data. New York: Springer; 2009. [Google Scholar]
- [49].James P, Berrigan D, Hart JE, Hipp JA, Hoehner CM, Kerr J, et al. Effects of buffer size and shape on associations between the built environment and energy balance. Health Place. 2014;27:162–70. DOI: 10.1016/j.healthplace.2014.02.003. [DOI] [PMC free article] [PubMed] [Google Scholar]
- [50].Baek J, Hirsch JA, Moore K, Tabb LP, Barrientos-Gutierrez T, Lisabeth LD, et al. Statistical Methods to Study Variation in Associations Between Food Store Availability and Body Mass in the Multi-Ethnic Study of Atherosclerosis. Epidemiology. 2017;28(3):403–11. DOI: 10.1097/EDE.0000000000000631. [DOI] [PMC free article] [PubMed] [Google Scholar]
- [51].Gamba RJ, Schuchter J, Rutt C, Seto EY. Measuring the food environment and its effects on obesity in the United States: a systematic review of methods and results. J Community Health. 2015;40(3):464–75. DOI: 10.1007/s10900-014-9958-z. [DOI] [PubMed] [Google Scholar]
- [52].Cummins S, Clary C, Shareck M. Enduring challenges in estimating the effect of the food environment on obesity. Am J Clin Nutr. 2017;106(2):445–6. DOI: 10.3945/ajcn.117.161547. [DOI] [PubMed] [Google Scholar]
- [53].Clary C, Lewis DJ, Flint E, Smith NR, Kestens Y, Cummins S. The Local Food Environment and Fruit and Vegetable Intake: A Geographically Weighted Regression Approach in the ORiEL Study. Am J Epidemiol. 2016;184(11):837–46. DOI: 10.1093/aje/kww073. [DOI] [PMC free article] [PubMed] [Google Scholar]
- [54].Costanza R, Daly L, Fioramonti L, Giovannini E, Kubiszewski I, Mortensen LF, et al. Modelling and measuring sustainable wellbeing in connection with the UN Sustainable Development Goals. Ecol Econ. 2016;130:350–5. DOI: 10.1016/j.ecolecon.2016.07.009. [DOI] [Google Scholar]
- [55].Hygiene NDoHaM. Community Health Profiles New York, NY (US): NYC Department of Health and Mental Hygiene; [cited 2021 November 15]. Available from: https://a816-health.nyc.gov/hdi/profiles/. [Google Scholar]
- [56].Stark JH, Neckerman K, Lovasi GS, Konty K, Quinn J, Arno P, et al. Neighbourhood food environments and body mass index among New York City adults. J Epidemiol Community Health. 2013;67(9):736–42. DOI: 10.1136/jech-2013-202354. [DOI] [PMC free article] [PubMed] [Google Scholar]
- [57].Fuster M, Sakowitz EN. Examining the Association Between Hispanic Caribbean Restaurant Characteristics and Healthy Menu Images in New York City. Curr Dev Nutr. 2020;4(Supplement_2):275-. DOI: 10.1093/cdn/nzaa043_126. [DOI] [Google Scholar]
- [58].Kaufman TK, Sheehan DM, Rundle A, Neckerman KM, Bader MD, Jack D, et al. Measuring health-relevant businesses over 21 years: refining the National Establishment Time-Series (NETS), a dynamic longitudinal data set. BMC Res Notes. 2015;8(1):507. DOI: 10.1186/s13104-015-1482-4. [DOI] [PMC free article] [PubMed] [Google Scholar]
- [59].Nutrition GSCf. Food Market Measures Toolkit: Assessment of Food Environment, Consumers, and Store Owners. Omaha, Nebraska (US); 2015. p. Available from: https://healthyeatingresearch.org/research/food-market-measures-toolkit-assessment-of-food-environment-consumers-and-store-owners/. [Google Scholar]
- [60].Han E, Powell LM, Zenk SN, Rimkus L, Ohri-Vachaspati P, Chaloupka FJ. Classification bias in commercial business lists for retail food stores in the U.S. Int J Behav Nutr Phys Act. 2012;9(1):46. DOI: 10.1186/1479-5868-9-46. [DOI] [PMC free article] [PubMed] [Google Scholar]