Creating ‘obesogenic realities’; do our methodological choices make a difference when measuring the food environment?
© Burgoine et al.; licensee BioMed Central Ltd. 2013
Received: 23 April 2013
Accepted: 23 June 2013
Published: 2 July 2013
The use of Geographical Information Systems (GIS) to objectively measure ‘obesogenic’ food environment (foodscape) exposure has become common-place. This increase in usage has coincided with the development of a methodologically heterogeneous evidence-base, with subsequent perceived difficulties for inter-study comparability. However, when used together in previous work, different types of food environment metric have often demonstrated some degree of covariance. Differences and similarities between density and proximity metrics, and within methodologically different conceptions of density and proximity metrics need to be better understood.
Frequently used measures of food access were calculated for North East England, UK. Using food outlet data from local councils, densities of food outlets per 1000 population and per km2 were calculated for small administrative areas. Densities (counts) were also calculated based on population-weighted centroids of administrative areas buffered at 400/800/1000m street network and Euclidean distances. Proximity (street network and Euclidean distances) from these centroids to the nearest food outlet were also calculated. Metrics were compared using Spearman’s rank correlations.
Measures of foodscape density and proximity were highly correlated. Densities per km2 and per 1000 population were highly correlated (rs = 0.831). Euclidean and street network based measures of proximity (rs = 0.865) and density (rs = 0.667-0.764, depending on neighbourhood size) were also highly correlated. Density metrics based on administrative areas and buffered centroids of administrative areas were less strongly correlated (rs = 0.299-0.658).
Density and proximity metrics were largely comparable, with some exceptions. Whilst results suggested a substantial degree of comparability across existing studies, future comparability could be ensured by moving towards a more standardised set of environmental metrics, where appropriate, lessening the potential pitfalls of methodological variation between studies. The researchers’ role in creating their own obesogenic ‘reality’ should be better understood and acknowledged.
KeywordsObesogenic Environments Foodscape Methods Exposure Density Proximity
With the scale of the obesity epidemic ever increasing, there has been a recent and growing body of literature that suggests an environmental contribution of the food environment (foodscape) to dietary choices and obesity . Food choices are made in context, within our respective foodscapes at micro and macro levels [2, 3], and hold the potential to shape our behaviour. Research studies of the food environment at the neighbourhood level have reported a variety of outcomes and have employed a range of methodologies ; many use Geographical Information Systems (GIS) to objectively measure the potential environmental influence on individuals’ behaviours and overall health.
Practically, there has been increased attention paid to the ways in which environmental foodscape attributes pertaining to weight can be modelled using GIS . Many studies of the ‘obesogenic’  food environment utilise measures of density and proximity to measure food ‘access’. Food outlet density is a measure designed to reflect the range or ‘intensity’ of any given food outlet type, in terms of the number of food outlets present around an individual [6, 7]. Food outlet proximity is usually the distance to the nearest food outlet, with distance inversely related to utilisation [8, 9]. Charreire et al. systematically demonstrated the pervasiveness of density and proximity metrics in the published literature. However, the substantive differences between density and proximity metrics, beyond their theoretical distinction, are under-studied. Do areas with high food outlet density always offer residents food outlets at a closer proximity? Could ensuing analyses be simplified by using only one foodscape exposure metric? Two previous studies have concluded that both measures “tell a consistent story about food access” [9, 10], questioning the extent to which both measures are necessary, considering the effort required to compute multiple metrics and the problems associated with covariance in later analyses; more research is required to better understand this issue.
Food environment exposure metrics compared in this study, and precedent for their use in the literature
Precedent for usea
Density of food outlets per 1000 population/per km2, per LSOA
O’Dwyer & Coveney  | Maddock  | Mehta & Chang  Ball et al. | Moore & Diez Roux  | Chou et al. Mobley et al. | Simmons et al. Sturm & Datar  Black et al. | Powell et al. | Burgoine et al. Cummins et al. | Reidpath et al. | Macdonald et al. Macdonald et al.
Density per buffer at:
400 m Euclidean radius
Counts of food outlets within 400/800/1000 m Euclidean radius buffers from population-weighted centroids of LSOA
800 m Euclidean radius
1000 m Euclidean radius
400 m Street Network
Counts of food outlets within 400/800/1000 m street network buffers from population-weighted centroids of LSOA
Smith et al. c 
800 m Street Network
1000 m Street Network
Euclidean or street network distance (m) from LSOA population-weighted centroids to nearest food outlet
Street network distance
Zenk et al. b | Pearce et al. | Macdonald et al. | Smith et al. Pearce et al. | Sharkey et al. | Pearce et al. d Sharkey & Horel  | Block et al. c  | Burdette & Whitaker  | Frank et al. c 
Our study used GIS to compute a range of commonly employed foodscape density and proximity metrics in the North East of England, UK. The research had two principle aims. Firstly, to compare food outlet density and proximity metrics to one another using correlation analysis. Secondly, to compare different metrics of density and proximity in a sensitivity analysis, to determine whether methodological differences in the calculation of each type of metric might serve to limit comparability between existing research findings. Comparisons made were as follows: 1) administrative area density per 1000 population vs. administrative area density per km2; 2) administrative area densities vs. 400/800/1000 m ‘pseudo-individual’ densities; 3) 400/800/1000 m ‘pseudo-individual’ densities, when using either Euclidean vs. street network buffers; 4) Euclidean vs. street network measures of proximity from population-weighted LSOA centroids. These four binaries of methodological comparison represent common-sense comparisons, and have been suggested as necessary in empirical work and systematic reviews in the literature [4, 11, 51–53].
The study area for this research was the former North East Government Office Region, UK, an environmentally heterogeneous area covering 8676 km2. Locations of food outlets (n = 14,454) were sourced from local councils (n = 23) under Freedom of Information (FOI) requests (for more details on the FOI Act 2000, see http://www.legislation.gov.uk/ukpga/2000/36/data.pdf). This data represents the most accurate secondary source of food outlet location data in the UK [54, 55]. Food outlets were categorised into ‘Food Bought-’ (n = 3793) and ‘Food Consumed Out of the Home’ (n = 10,661) types, based on the likely site of food preparation ; see Burgoine  for full details. For brevity, only the geographies of ‘Food Bought Out of the Home’ outlets were considered in this study (‘supermarkets’, ‘convenience’, ‘discount’ and ‘department’ stores, plus ‘specialist’ retailers (butchers, delicatessens, bakers, fishmongers, confectioners, greengrocers, health, organic, fair trade, artisan, sweet and oriental stores)); results not presented showed no differences in findings when analysing ‘Food Consumed Out of the Home’ outlets (‘restaurants’, ‘pubs’, pizzerias’, ‘fast food’, ‘cafés’/coffee shops’, ‘takeaways’, ‘sandwich shops’, ‘bakers – retail’, ‘hotels’, ‘entertainment’, ‘health and leisure’, ‘novelty stores’ and ‘pharmacies’). Using lookup tables from GeoConvert (http://geoconvert.mimas.ac.uk/), food outlet locations were mapped based on their postcodes using ArcGIS 9.3 (ESRI Inc., Redlands, CA). Recent precedent has been set in the literature for geocoding at the postcode level in the UK .
Details of the exposure metrics deduced are shown in Table 1 (the ‘Variable’ column). Neighbourhood densities of food outlets were calculated per 1000 population (population data from the 2001 UK census) and per km2 within Lower Super Output Areas (LSOAs); these are small administrative areas (median size 0.49 km2), each containing roughly 1500 residents (available from UKBORDERS, http://edina.ac.uk/census/). Densities (counts of food outlets) were also calculated within 400m, 800m and 1000m Euclidean and street network buffers from the population-weighted centroids of LSOAs. We refer to these buffered LSOA centroids as ‘pseudo-individual’ neighbourhoods on the assumption that food access at this calculated location is representative of the rest of the LSOA. Street network data were provided by Ordnance Survey as part of their MasterMap Integrated Transport Network (ITN). Proximity, Euclidean and street network distance to the nearest food outlet, was also calculated from these population-weighted centroids. Precedent for the frequent use of each metric, is also shown in Table 1, informed by recent systematic review articles [4, 52, 53, 58], which should be referred to for a comprehensive review of the literature. The metrics compared and contrasted in this study represent those that have been widely employed in obesogenic environment studies to date.
Analyses were performed throughout using SPSS 17.0 (SPSS Inc., Chicago, 2006). Descriptive statistics (medians, interquartile ranges, and ranges) for our environmental metrics are presented first. As our exposure metrics were continuous variables, differences between density and proximity metrics, and within types of density and types of proximity metrics were assessed using correlation analyses. We used Spearman’s rank correlations because the vast majority of our access metrics were not normally distributed, with their distributions tending to be positively skewed. When comparing density and proximity metrics directly, we present the inverse of the correlation co-efficient obtained. As higher proximity values actually relate to greater distances (worse access to the food outlet), this allows, for example, a positive co-efficient to be interpreted as greater density allied with greater proximity (less distance).
Descriptive statistics for exposure metrics across administrative areas (n = 1656)
Per 1000 population
Per 400m Euclidean buffer
Per 800m Euclidean buffer
Per 1000m Euclidean buffer
Per 400m street network buffer
Per 800m street network buffer
Per 1000m street network buffer
Street network distance
Density compared to proximity
Spearman’s rank correlations between LSOA (n = 1656) density and proximity measures*
Per 1000 population (1)
Per km2 (2)
Per 400m Euclidean buffer (3)
Per 800m Euclidean buffer (4)
Per 1000m Euclidean buffer (5)
Per 400m street network buffer (6)
Per 800m street network buffer (7)
Per 1000m street network buffer (8)
Euclidean distance (9)
Street network distance (10)
Heterogeneity within exposure metrics
This section examines the extent to which methodological heterogeneity within exposure metrics may impact upon comparability between findings in the literature to date. We make four necessary comparisons, as outlined in the aims.
Density per 1000 population vs. density per km2
Correlation analysis (Table 3) showed that whether LSOA density of ‘Food Bought-’ outlets is calculated per 1000 population or per km2, both measures were correlated very strongly (rs = 0.831, p < 0.001) giving similar impressions of food access throughout the study area.
Area level vs. 400/800/1000m ‘pseudo-individual’ level density
Table 3 showed that only moderate/moderately-strong correlations existed between area level and ‘pseudo-individual’ level metrics, ranging between rs = 0.299 and rs = 0.658. Whilst they are all significant (p < 0.001) and in the same positive direction, these correlations suggest that we could be less sure of comparing results across studies that utilise these different approaches. The specific degree to which this statement holds true was attenuated by the metric examined: area and ‘pseudo-individual’ metrics were more comparable at smaller Euclidean and street network buffer distances, largely decreasing in strength at 800m, and further still at 1000m. The more nuanced street network buffers of ‘pseudo-individual’ density were largely more comparable with area level metrics, however, the 400m Euclidean buffer was the most similar (rs = 0.549 for LSOA density per 1000 population, rs = 0.658 for LSOA density per km2, both p < 0.001).
Street network vs. Euclidean 400/800/1000m ‘pseudo-individual’ level density
Correlation results (Table 3) showed that levels of ‘pseudo-individual’ density were similar whether using a Euclidean or street network approach (at the same distance), and increasingly so when accounting for larger neighbourhoods (400m rs = 0.667; 800m rs = 0.769; 1000m rs = 0.783, all p < 0.001). 400m Euclidean neighbourhood densities were however more strongly correlated with 800m street network densities (rs = 0.764), and 800m Euclidean densities with 1000m street network densities (rs = 0.854).
Street network vs. Euclidean proximity
Results presented in Table 3 showed that ‘Food Bought-’ proximity was comparable when assessed via Euclidean and street network distances (rs = 0.865, p < 0.001). Much like the similarity displayed between Euclidean and street network ‘pseudo-individual’ neighbourhoods, this finding suggested that there was a substantial degree of comparability between the two metrics.
This paper contributes to obesogenic foodscape research in two ways. Firstly, measures of density and proximity were compared to assess the extent to which they represent different facets of the foodscape. These measures are theoretically distinct and commonly differentiated in the literature, and it has been argued that to use just one metric is to do a disservice to the range of ways in which environments may affect behaviour . However, using both metrics may lead to multicollinearity issues in ensuing analyses, resulting from covariance between the two metrics. Further, opting for either of the two metrics may provide a ‘shortcut’ for researchers wishing to employ only a single, representative metric of foodscape exposure. Indeed, correlation analyses presented here provided tentative evidence that these measures represent the foodscape in very similar ways, suggesting that neighbourhoods with high food outlet density were also those where residents live within closer proximity to food, supporting previous findings [9, 10]. However, this study does not represent definitive evidence that this is always the case, and opposite results have been observed . Furthermore, although incidental, at the very least each measure may be susceptible to a different level of measurement error . For example, where food outlet location data is not totally comprehensive, measures of food outlet density may be more prone to error (systematic underestimation of exposure) than measures of proximity (which, by chance, may remain completely accurate).
Secondly, this paper evaluated the extent to which methodological heterogeneity in calculating an exposure metric (density or proximity) contributes to a lack of inter-study comparability in findings. To some extent, results here suggested that such criticisms may be unfounded: measures of proximity from population-weighted centroids were highly correlated when using Euclidean or street network distance, corroborating findings from the only one comparable previous US study . In addition, measures of ‘pseudo-individual’ density using Euclidean or street network distances were nearly equal at similar geographical scales, as has also been found elsewhere [51, 60], whilst becoming more similar at greater distances. Buffer distances beyond 1000m have been used in the literature [6, 11, 12, 25] and we could therefore expect even greater convergence. This said, there was evidence to suggest that Euclidean buffers were most comparable to marginally larger street network buffers: 400m Euclidean buffers most strongly correlated with 800m street network buffers and 800m Euclidean buffers most strongly correlated with 1000m street network buffers, confirming similar results from Thornton et al.. This is likely to be because in general, Euclidean buffers result in a larger footprint, thus encapsulating more food stores, as illustrated in Figure 1. Statistical investigations also reported density per km2 and per 1000 population to be similar, inviting comparability across this methodological binary.
Measures of density at the area or ‘pseudo-individual’ level were only moderately correlated with one another, suggesting a limited extent to which findings across this divide should be compared. Unfortunately, this divide across metrics at the area or ‘pseudo-individual’ level separates two large bodies of academic work (Table 1), where studies have either located individuals within administrative area neighbourhoods, or created bespoke neighbourhood buffers around said individuals. Therefore, it may be of benefit to the field if a single (area or ‘pseudo-individual’) density metric were to be used in future research to maximise inter-study comparability, wherever possible. At the very least, studies should consider providing a rationale for their preference of approach to density calculation, whilst better and more fully acknowledging the assumptions and limitations inherent to either choice.
Beyond implying comparability across studies then, results suggest that there may only be small gains made from using street network distances for measures of ‘pseudo-individual’ density or proximity. This may be important when time or resources are at a premium or where street network data is unavailable. However, we disagree with Sparks et al. who conclude that this equates to a reduced “computational burden on those wishing to use GIS methodology” – from which we infer that through not having to use more complex street network data, the usability of GIS methods is increased. It is argued here that there is a ‘tipping point’, where the value of using increasingly detailed metrics begins to diminish in relation to the computational effort required to create them. However, as we know little of this ‘tipping point’, and we should be mindful of scale differences (calculating street network availability may be more critical at 400m radii than 1000m radii, for example), we should always try to do the best that we can, even when confronted with technological challenges.
We argue here that we need to further consider how we can advance our methods and our metrics of exposure in objective studies of obesogenic food environments. Some studies have already sought to use measures of variety in relation to the food environment [6, 11, 32]; for example, the ratio of fast food to full service restaurants , designed to complement measures of density and proximity. Others have begun to use inverse distance weighted (IDW) measures of facility access, which to some extent ameliorate concerns arising over the relatively arbitrary definitions of ‘neighbourhood’ applied throughout the literature . In reality however, it may never be possible, or even appropriate, to reach a point where even a well-conceived measure of food access can become a universal standard, suitable for use across all studies, as has been tentatively suggested . Other methodological differences between studies – in statistical techniques, or in terms of study populations and their characteristics, which might vary between countries for example, and so on – ensure that two studies will rarely, if ever, be completely comparable to one another. This does not detract however from the importance of attempting to understand the implications of such diversity, which is what we have begun to address here. A valid and reliable research evidence base, where differences in study findings can be fully understood and appreciated with respect to the methods used, from which conclusions about neighbourhood level effects on diet can be accurately drawn, will be absolutely critical in justifying neighbourhood interventions or pilot interventions designed to promote health, such as restricting the clustering of unhealthy food retailers.
This paper has a number of limitations. In this study we did not compare all foodscape metrics employed in the field to date; instead, we focused on many of the most commonly used metrics in order to relate to as much of the field as possible. Also, we did not investigate the entire foodscape here; different relationships may have been found for ‘Food Consumed Out of the Home’ outlets, although work not presented suggests this is not the case. There is also little compelling logic to suggest that the relationships tested here might be systematically biased according to the type of food outlet selected for study. Furthermore, the category of ‘Food Bought Out of the Home’ includes outlet types such as ‘supermarkets’ and ‘convenience stores’, density and proximity of which are frequently assessed in the literature. We did not have access to data on the exact locations of participants in this study, hence measures of proximity and some measures of density were calculated from administrative area population-weighted centroids, where we assumed at least one individual to live. This is an approach adopted in the literature where participant location data has not been available [11, 20], however we acknowledge that this could constitute a type of ‘errors-in-variables’ bias and that exposure throughout any given administrative area will vary , and would be likely to decrease away from population-weighted centroids. Our approach of using population-weighted centroids was at least consistent between areas. External validity in findings cannot be assumed, and we cannot rule out that results here may be particular to the North East of England, despite the large and heterogeneous study area, and the similarities between the study area and many other regions of the UK, notably in terms of its diverse socio-economic profile, with which we know foodscape exposure varies [15, 35, 37]. Lastly, we acknowledge that a greater density or proximity of food does not necessarily equate to more utilisation of these facilities. Considerations such as transport preferences, motivation to walk, economic factors, neighbourhood perceptions and so on will all contribute broadly to ‘access’ beyond purely a geographic perspective. We know for example that in Newcastle upon Tyne, in the North East of England, adults conducting their main supermarket shop on foot travel a median distance one-way of 510 m, as compared to 2528 m for those with access to a car . It is also worth considering that the vast majority of food environment exposure studies have tended to focus exclusively on residential neighbourhood exposure, despite the apparent necessity of accounting for time spent in wider ‘activity spaces’ , too. This said, our study compared foodscape metrics that are widely used in the field, rendering this research highly relevant, regardless of whether these previous studies conceived of access in a purely spatial sense or otherwise.
Our findings should be viewed in the context of creating different ‘obesogenic realities’ during the research design and analysis process. Despite occasional assertions to the objectivity of the “scientific approach”, quantitative researchers are ‘critical agents’ in the GIS process [65, 66], and are required throughout their research to make a myriad of choices; the potential for these choices to impact upon results has been suggested elsewhere , and demonstrated to some extent here. In this way we create our own obesogenic realities and we should remain reflexive towards, and critical of these creations, in order to improve results and to chart a course for better future research. ‘Researcher bias’ has been well discussed in qualitative literatures, where data is often seen as being ‘generated’ rather than ‘collected’ as a reflection of the investigator’s input into the research process [68, 69]. Such issues of bias are less frequently discussed in quantitative discourse, particularly in relation to GIS, despite their apparent poignancy, although feminist critiques of GIS amongst others seek to increasingly understand the “exclusions, silences, and marginalizing [sic] power of our representations” [70–72]. Objective GIS studies are often based on the notion of ‘technological determinism’ [65, 69], yet the extent to which this is possible is arguably limited. Leszczynski  warns against committing the ‘ontic fallacy’, whereby we unquestioningly accept our representation of reality to “mirror nature”, and through failing to acknowledge the impact of the choices we make as researchers on the results we obtain, we risk falling into the ontological trap of what can truly be known. This paper demonstrates the need for such concern by contrasting an extensive range of environmental metrics and demonstrating that at least in some instances, the choices that we make do matter.
Ideally, our understanding of how individuals interact with their food environments should advance alongside available data sources and expertise, to allow similar but appropriate metrics of both density and proximity to be used between studies. This would facilitate the creation of a methodologically consistent evidence base, upon which to ascertain an objective environmental influence upon individuals, whilst not having to make excuses for methodological variation. Whilst desirable however, this may not be possible or indeed appropriate. Nevertheless, this study helps us to understand the current state of evidence in obesogenic environment research, by demonstrating that heterogeneity between most exposure metrics is not necessarily problematic.
The data collection for this work was partly supported by an Economic and Social Research Council quota PhD studentship [ES/F021976/1]. The data analysis was undertaken by the Centre for Diet and Activity Research (CEDAR), a UK Clinical Research Collaboration (UKCRC) Public Health Research Centre of Excellence. Funding from the British Heart Foundation, Economic and Social Research Council, Medical Research Council, the National Institute for Health Research and the Wellcome Trust under the auspices of the UK Clinical Research Collaboration, is gratefully acknowledged. The digital maps used hold Crown Copyright from EDINA Digimap, a JISC supplied service. We are grateful to local councils throughout the study area for kindly supplying data to enable this work and to Ordnance Survey for supplying their MasterMap Integrated Transport Network (ITN) data.
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