Linking childhood obesity to the built environment: a multi-level analysis of home and school neighbourhood factors associated with body mass index.
Gilliland, Jason A. ; Rangel, Claudia Y. ; Healy, Martin A. 等
Childhood obesity has become a critical public health issue in
Canada, as rates have tripled over the past three decades. (1) Over one
in four Canadian children are either overweight or obese (17% and 9%
respectively). (2) The increased prevalence of childhood obesity has
been linked to the concurrent rise of physical health problems normally
associated with adults, including Type 2 diabetes, hypertension, heart
disease and pulmonary diseases, as well as socio-psychological
afflictions such as discrimination, behavioural problems, negative
self-esteem, anxiety and depression. (3-6) A rapidly expanding avenue of
research suggests that rising rates of obesity are due not only to
individual-level factors (i.e., genetics), but also to characteristics
of our local built environments that may be encouraging or discouraging
the healthy diets or active lifestyles associated with healthy body
weights. (7-10)
Previous research has confirmed that obesity is linked to the
consumption of energy-rich, fast foods. (11) Large-scale US studies have
found that adult obesity rates are positively associated with the
density of neighbourhood fast-food outlets (12) and convenience stores.
(13) Much of the emphasis on the link between food and children's
health focuses on advertising (14) or food policies within schools;
(15-17) however, some policy-makers and public health professionals are
shifting their focus to the food environments surrounding schools, as
new research indicates that many children visit food retailers on their
way to and from school, mostly filling up on high-sugar or high-fat,
energy-dense foods. (18) Several studies have shown that fast-food
outlets are more prevalent near schools (19,20) and in low-income
neighbourhoods, (21,22) suggesting that these vulnerable populations may
be at heightened risk of developing poor eating habits as a result of
increased exposure to unhealthy foods. Furthermore, it has been shown in
London, ON, that the presence of fast-food outlets and convenience
stores within 1 km of school is linked to increased junk food purchasing
(23) and poorer diets. (24) However, a national study of Canadian
students in grades 6-10 found that increased number of food retailers
within 1 km of the school did not increase the likelihood of the
students being overweight. (25) More research is needed to confirm the
links between the local food environment and childhood obesity.
[FIGURE 1 OMITTED]
Increased physical activity is associated with reduced obesity and
other health benefits for children and youth. (26) Unfortunately,
Canadian children devote 62% of their free time (after school and
weekends) to sedentary pursuits, and activity levels decline with age.
(27) A growing body of research suggests that the layout and design of
children's neighbourhood environments may be a key facilitator or
barrier to physical activity. (28) Access to opportunities for physical
activity, such as public parks and recreation facilities, has been
repeatedly associated with higher rates of physical activity among
children and adolescents. (8,28-30) Opportunities located within walking
distance of home may be doubly important for stimulating active
behaviours, as both the route and the destination contribute to overall
activity levels. (31) It has been argued that children from low-income
households tend to have fewer opportunities for health-promoting
activity because of a reduced ability to afford fee-based recreation
programs as well as systemic socio-spatial inequities with respect to
public resources. (32) However, previous research in London has shown
that publicly provided recreation opportunities are equitably
distributed with no obvious socio-spatial disparities. (33)
The purpose of this study is to identify built environment factors
associated with high BMI levels among adolescents in London, ON, to help
identify potential environmental interventions for reducing childhood
obesity.
METHODS
Survey and outcome measure
Students in grades 6, 7 and 8 at 28 elementary schools within the
city of London, ON, were invited to complete a questionnaire that asked
for their home postal code, sex, age, height, weight and various
health-related questions. The sampled schools were selected from
neighbourhoods of varying built environments across the city (see Figure
1) to represent the full diversity of environmental factors that
children experience around their homes and schools. Prior to school
recruitment, ethics approval was obtained from University of Western
Ontario's Research Ethics Board and the ethics boards at both the
Thames Valley District School Board and the London District Catholic
School Board. Informed written consent was obtained from 1,048
adolescents and their parents before data collection. A total of 966 out
of 1,048 children aged 10-14 years who participated in the study
provided the complete information on age, sex, height and
weight--information needed to construct their age-and sex-adjusted BMI
z-score--and 891 of those provided accurate address information for
deriving measures of their home built environment.
Self-reported height and weight were used to estimate the body mass
index (BMI) of participants by dividing weight in kilograms by height in
metres squared; BMI z-scores were calculated to control for differences
by age and sex. Following procedures established in previous studies,
(34) we calculated age-and sex-specific BMI z-scores based on the World
Health Organization growth curves, which in turn are based on large
samples of children selected to represent optimal growth. (35)
GIS analysis of environmental variables
Using ArcGIS 10.0 (Environmental Systems Research Institute Inc,
Redlands, CA), survey data for participants were geocoded to the
geographic centre of their home postal code. University of Western
Ontario's Research Ethics Board did not allow us to collect the
full address of students. Nevertheless, previous research indicates that
Canadian postal codes are suitable proxies of home neighbourhoods in
urban and suburban environments. (36,37) Since there is no agreed
measure of "neighbourhood", we tested four different areal
definitions around each participant's home postal code, including:
circular "buffers" encompassing the territory within a
distance of 1) 500 m and 2) 1000 m from the postal code centroid; and
"network buffers", which encompass the territory reachable
within distances of 1) 500 m and 2) 1000 m from home, as measured along
the street network. To assess the built environment around the school,
we used the same four circular and network buffers at 500 m and 1000 m
from the school address, as well as an additional areal unit: the school
"walkshed". The walkshed is the territory within a
school's observed catchment area that encompasses only those
students living within walking distance, as defined by the respective
school boards (see Figure 1). School walksheds were generated for each
school by: mapping the home postal code of every registered student not
eligible for bussing according to school board data; selecting postal
code centroids within the school board-mandated 1600 m walking distance
of the specific school; and then merging all neighbouring city blocks
that contained a selected postal code into a single walkshed polygon. We
argue that this definition of unique walksheds based on the residential
locations of students within walking distance of each school is a better
representation of the local school neighbourhood than the standard
buffers commonly used by researchers.
Previously validated databases of every fast-food outlet and
convenience store in the city and surrounding county were provided by
the Middlesex-London Health Unit, which is mandated to keep a current
inventory of all food retailers for the purpose of licensing and annual
health inspections. Using a master address database provided by the City
of London, every food retailer was geocoded to its correct building. To
"ground truth" the database, trained research assistants
performed on-site environmental audits within a 1000 m buffer around six
of the sample schools during the same period as the surveys and
confirmed 100% accuracy of the database: all food premises listed in the
health unit inventory for those test neighbourhoods were still in
business and no new food retailers were found. Fast-food outlets were
defined as restaurants with food ordered at a counter and paid for in
advance. Convenience stores were classified as small food retailers with
a floor area of less than 1000 m. Data on school locations and public
recreation opportunities (including parks, playgrounds, arenas and
recreation centres, and sports fields/facilities) were obtained from the
City of London Planning & Development Division and had been
previously validated using orthoimagery with a 30 cm ground pixel
resolution. (33,37) These data were used to calculate accessibility
measures for each participant using GIS (geographic information
systems), including the number of public recreation opportunities,
fast-food outlets and convenience stores within all defined home and
school neighbourhoods.
Statistical analyses
Attribute tables containing the built environment variables by
school and by home postal code for each participant were linked to
questionnaire data on each student within ArcGIS 10.0 and exported for
statistical analysis. The model was tested using multilevel structural
equation techniques for complex survey data. This technique allows for
simultaneous testing of the effects of school-environment (Level 2) and
home-environment (Level 1) predictors on a child's BMI z-scores.
The constructs representing built environment--presence of public
recreation opportunities, presence of fast-food outlets, and presence of
convenience stores--were operationalized at both levels. The two sets of
measurement instruments are independent, as they refer to different
geographic environments and different units of analysis. The model was
estimated using Mplus 6.0 program (Muthen and Muthen). (38)
RESULTS
Nearly three quarters (71.0%) of participants were categorized as
having a normal BMI, 16.9% were overweight, 7.6% were obese, and 4.6%
were considered underweight (Table 1). Boys were much more likely to be
overweight or obese than girls; however, BMI did not vary greatly
according to age.
Table 2 provides descriptive statistics for the environmental
variables used in this study. It presents the number and percentage of
participants who have 0, 1, or 2 or more of the selected environmental
features nearby, depending on which method is used to define home and
school neighbourhoods. Two key findings are clear from the results
presented: 1) a large percentage of children have at least one public
recreation opportunity, convenience store and fast-food restaurant
within a short walk of their home and school; and 2) the way in which
neighbourhoods are delineated, in terms of distance from home or school
and how distance is measured, has a major influence on whether the
selected environmental factors appear to be accessible or not.
We employed univariate regression to determine which of the built
environment variables to include in the models on the basis of
statistically significant associations with BMI z-scores (Table 3). The
final multi-level models included the following variables for the home
environment: presence of recreation opportunities, presence of fast-food
restaurants, and presence of convenience stores, all within the 500 m
network distance of home. For the school environment, the final models
included: presence of recreation opportunities, presence of fast-food
restaurants, and presence of convenience stores, all within the
school-specific walkshed. Table 4 displays the results of the
multi-level analysis of the influence of the school and home built
environment on children's BMI z-score. Prior to testing the
hypothesized model, we examined the between-school variability in BMI
z-scores. The interclass correlation coefficient of 0.039 (p<0.05)
indicated that there were statistically significant differences in BMI
z-scores across school neighbourhoods. As predicted, the results from
the multi-level models show that the home-environment predictor
"presence of public recreation opportunities within 500 m network
distance" had a significant negative (i.e., reducing) effect on BMI
z-scores (-0.203; p<0.05). The indicators for "presence of
fast-food outlets" and "presence of convenience stores"
in the home environment, however, had no significant effect on the
outcome variable (0.012 and 0.190, respectively; p>0.05). The effect
of only one of the school-environment (Level 2) predictors, presence of
fast-food outlets within the school walkshed, was statistically
significant (0.073; p<0.05), after controlling for home-environment
variables.
DISCUSSION
This study of children aged 10-14 years in London, ON, found that
nearly three out of four participants (71.0%) were categorized as having
a normal BMI, 16.9% were overweight, 7.6% were obese, and 4.6% were
considered underweight. These findings are very similar to reported
rates of overweight (17%) and obesity (9%) among children aged 6-14
years across Canada. (2) Also consistent with previous Canadian studies
(2,39) is the finding that boys were more likely to be overweight than
girls; but, unlike previous studies, (39) we did not see any discernible
trend in BMI by age within the limited age range of our sample.
This study makes an important empirical contribution to knowledge
about the determinants of childhood obesity in Canada, as the results of
multi-level statistical analyses indicate that characteristics of the
built environment around children's homes and schools have a modest
but significant effect on their BMI. As expected from previous studies,
the presence of recreation opportunities in the home neighbourhood had a
significant effect on BMI z-scores: children who had at least one public
recreation opportunity within a 500 m walk of their home were likely to
have lower BMI z-scores than their counterparts without a recreation
opportunity nearby. Presumably, children and youth are more likely to
use parks and recreation facilities if they are located within close
walking distance of their home, and lower observed BMIs may therefore be
due to increased physical activity levels associated with greater
accessibility. Indeed, this finding follows previous research on
children 11-13 year olds in London, which revealed that those who have
two or more public recreation facilities within 500 m of their home
engaged in 16.5 more minutes of physical activity per day than children
with fewer facilities in their home neighbourhood. (28) On the other
hand, the presence of public recreation opportunities in the school
neighbourhood did not have a significant effect on children's BMI
z-scores. This finding fits with qualitative studies based on interviews
and/or focus groups with children that suggest they are likely to spend
more of their free time, especially on weekends, playing in the
neighbourhood around the home rather than around the school; (40,41)
moreover, during school hours, children are likely to play on the school
grounds rather than leave the campus to play.
Easy access to retailers of "junk food", such as
fast-food restaurants and convenience stores around children's
homes and schools, appeared to contribute to higher obesity levels;
however, the presence of fast-food restaurants within the school
walkshed was the only food environment variable that had a statistically
significant association with higher BMI z-scores among our sample
children. This finding follows recent research on grade 7-8 students in
London, which revealed that the presence of fast-food outlets within 1
km of school is linked to increased purchasing of junk food by students
(23) and poorer-quality diets (i.e., lower "healthy eating
index" scores). (24) The findings are also supported by qualitative
research indicating that children who purchase junk food are likely to
do it near the school, during the lunch break and the journey to and
from school, whether or not a parent may be present to evaluate their
purchase. (40,41) On the other hand, a study of grade 6-10 students in
178 schools across Canada did not find any statistically significant
relation between the characteristics of the local food environment
around each school and the likelihood of children being overweight;
however, the study did not account for the presence/absence of
recreation facilities or other opportunities for physical activity in
the local environment. (25)
This paper has a number of methodological strengths and weaknesses
that are worth noting. It makes a methodological contribution by
applying multiple areal units of different shapes and sizes (i.e.,
circular buffers, network buffers and school-specific walksheds) to
categorize the home and school environments of children. This approach
recognizes and attempts to account for the modifiable areal unit problem
that is inherent in most environment and health studies. (42) The
school-specific walkshed is a particular innovation of this study that
also proved to be the most significant method for delineating school
neighbourhoods. Another methodological improvement is that the
geodatabases of environmental variables used were locally generated by
municipal organizations and validated through rigorous processes to
achieve ground-truth. Most previous studies of this kind have relied on
commercial databases, which are often incomplete and spatially
inaccurate, (43,44) to identify the locations of food retailers and
recreation opportunities. (39,45,46)
Although BMI is a widely accepted measure for comparing body weight
status at the population level, there are limitations to using BMI for
identifying overweight/obesity among children. We used age- and
sex-adjusted BMI z-scores to determine differences by age and sex, but
accuracy can be affected by factors such as ethnicity, frame size, level
of physical fitness and biologic maturation. (47) Ideally, any
assessment of body weight status should be calculated using direct
measurements, as self-reported heights and weights for youth tend to
underestimate the prevalence of overweight and obesity. (48)
Nevertheless, as reported above, rates of overweight and obesity in our
sample population were not dramatically different from rates reported
for children in a recent nationwide study based on directly measured
BMI. (2) Self-report measures are much less intrusive and more feasible
to collect for large samples, but as an absolute value, the BMI should
be interpreted with caution.
Another potential criticism of this research might be directed at
the fact that, because of University of Western Ontario's Research
Ethics Board directives, we used children's home postal codes as
the centre of their neighbourhoods rather than their actual dwelling.
Although previous research has shown that this is a common strategy in
epidemiological studies and that postal codes are adequate proxies for
addresses in Canadian cities, (36,37) the potential limitations of this
approach must be acknowledged: if the positional discrepancy between
exact location and proxy location is large for a given case, it may lead
to the misclassification of the presence or absence of certain
environmental features. (36,37) Positional discrepancy is not a
significant problem in this study, however, as it has been estimated
that the majority of residential dwellings in urban and suburban London
are located within 100 m of their respective postal code centroid.
(37,49)
It could be argued that another limitation of the study is that it
does not examine the full range of environmental variables that have
appeared in previous literature. We limited our model to the selected
variables for two reasons: 1) previous research in the same city with
children of the same age group indicated that these were the most
significant predictors of physical activity levels, junk food purchasing
and dietary quality; and 2) the statistical test for school-level
effects revealed that the school-level built environment accounted for
only a small percentage of the variance, and therefore adding more
variables would not be efficient.
This is one of the first Canadian studies to empirically establish
a relation between neighbourhood environmental factors and
children's BMI. It is also one of the only studies of its kind to
focus on a typical mid-sized North American city, as the small but
growing literature on the environment-obesity link is still dominated by
studies set in larger cities. While causal relations cannot be inferred
from these cross-sectional data and the results are not necessarily
generalizable, the study has potentially important implications for
planners, school board officials and other decision-makers involved in
the construction and management of children's environments.
Interventions, policies and programs that increase children's
access to high-quality, publicly provided recreation opportunities
within a short walk of home may be a key to promoting active lifestyles
and reducing obesity levels among children and youth. In addition, the
study highlights the need for municipalities to consider bylaws and
policies aimed at regulating the concentration of fast-food outlets
close to schools, where children are heavily exposed, and to create
incentives that encourage more healthy food options on local menus.
Given the problems associated with rising childhood obesity rates, it is
imperative that further research be conducted into how environmental
factors influence physical activity levels and dietary habits among
children and youth, particularly if we are to develop interventions that
promote lifelong healthy behaviours.
Conflict of Interest: None to declare.
Acknowledgements: This study was supported by research grants from
the Heart and Stroke Foundation of Canada, the Green Shield Canada
Foundation and the Canadian Institutes of Health Research's
Institutes of Human Development, Child and Youth Health, and Nutrition,
Metabolism and Diabetes.
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Jason A. Gilliland, PhD, [1-3] Claudia Y. Rangel, MA, [1] Martin A.
Healy, MSc, [1] Patricia Tucker, PhD, [4] Janet E. Loebach, MEDes, [1]
Paul M. Hess, PhD, [5] Meizi He, PhD, [6] Jennifer D. Irwin, PhD, [7]
Piotr Wilk, PhD [3,8]
Author Affiliations
[1.] Human Environments Analysis Laboratory, Department of
Geography, University of Western Ontario, London, ON
[2.] School of Health Studies and Department of Paediatrics,
University of Western Ontario, London, ON
[3.] Scientist, Children's Health Research Institute &
Lawson Health Research Institute, London, ON
[4.] School of Occupational Therapy, University of Western Ontario,
London, ON
[5.] Department of Geography & Program in Planning, University
of Toronto, Toronto, ON
[6.] Department of Health & Kinesiology, The University of
Texas at San Antonio, San Antonio, TX
[7.] School of Health Studies, University of Western Ontario,
London, ON
[8.] Department of Paediatrics and Department of Epidemiology &
Biostatistics, University of Western Ontario, London, ON
Correspondence: Jason A. Gilliland, Dept. of Geography, University
of Western Ontario, 1151 Richmond St, London, ON N6A 5C2, Tel:
519-661-2111, ext. 81239, Fax: 519-661-3750; E-mail: jgillila@uwo.ca
Table 1. Demographic Characteristics of Study Participants
All Underweight Normal
n % n % n %
All 966 100.0 44 4.6 686 71.0
Sex
Boys 458 47.4 16 3.5 285 62.2
Girls 508 52.6 28 5.5 401 78.9
Age, years
10 66 6.8 3 4.6 44 66.7
11 105 10.9 9 8.6 72 68.6
12 319 33.0 14 4.4 224 70.2
13 418 43.3 17 4.1 305 73.0
14 58 6.0 1 1.7 41 70.7
Overweight Obese
n % n %
All 163 16.9 73 7.6
Sex
Boys 112 24.4 45 9.8
Girls 51 10.0 28 5.5
Age, years
10 10 15.2 9 13.6
11 10 9.5 14 13.3
12 54 16.9 27 8.5
13 78 18.7 18 4.3
14 11 19.0 5 8.6
Table 2. Built Environment Characteristics of Study Participants
Circular Buffer
500 m 1000 m
n % n %
Home Neighbourhood Environment
Number of public
recreation opportunities
0 291 30.9 89 9.4
1 147 15.6 57 6.0
2 or more 505 53.6 797 84.5
Number of fast-food outlets
0 505 53.6 181 19.2
1 104 11.0 66 7.0
2 or more 334 35.4 696 73.8
Number of convenience stores
0 435 46.1 177 18.8
1 134 14.2 55 5.8
2 or more 374 39.7 711 75.4
School Neighbourhood Environment
Number of public
recreation opportunities
0 125 12.9 77 8.0
1 103 10.7 20 2.1
2 or more 738 76.4 869 90.0
Number of fast-food outlets
0 471 48.8 84 8.7
1 49 5.1 58 6.0
2 or more 446 46.2 824 85.3
Number of convenience stores
0 304 31.5 20 2.1
1 254 26.3 162 16.8
2 or more 408 42.2 784 81.2
Network Buffer
500 m 1000 m
n % n %
Home Neighbourhood Environment
Number of public
recreation opportunities
0 634 67.2 252 26.7
1 175 18.6 164 17.4
2 or more 134 14.2 527 55.9
Number of fast-food outlets
0 694 73.6 378 40.1
1 92 9.8 117 12.4
2 or more 157 16.7 448 47.5
Number of convenience stores
0 652 69.1 344 36.5
1 122 12.9 108 11.5
2 or more 169 18.0 491 52.1
School Neighbourhood Environment
Number of public
recreation opportunities
0 277 28.7 185 19.2
1 307 31.8 71 7.4
2 or more 382 39.6 710 73.5
Number of fast-food outlets
0 682 70.6 271 28.1
1 15 1.6 20 2.1
2 or more 269 27.9 675 69.9
Number of convenience stores
0 473 49.0 187 19.4
1 281 29.1 104 10.8
2 or more 212 22.0 675 69.9
School
Walkshed
n %
Home Neighbourhood Environment
Number of public
recreation opportunities
0
1
2 or more
Number of fast-food outlets
0
1
2 or more
Number of convenience stores
0
1
2 or more
School Neighbourhood Environment
Number of public
recreation opportunities
0 38 3.9
1 47 4.9
2 or more 881 91.2
Number of fast-food outlets
0 54 5.6
1 118 12.2
2 or more 794 82.2
Number of convenience stores
0 108 11.2
1 27 2.8
2 or more 831 86.0
Table 3. Results of the Univariate Multi-level Regression Analyses
Examining the Relationship Between School and Home Built Environment
and Children's BMI Z-Scores
Circular Buffer
500 m 1000 m
Estimate (SE) Estimate (SE)
Home Neighbourhood
Environment
Number of public recreation -0.109 (0.10) 0.043 (0.03)
opportunities
Number of fast-food outlets 0.204 * (0.09) 0.032 (0.02)
Number of convenience stores 0.076 (0.10) 0.044 * (0.02)
School Neighbourhood
Environment
Number of public recreation -0.136 (0.26) -0.097 * (0.04)
opportunities
Number of fast-food outlets 0.028 (0.13) 0.044 (0.02)
Number of convenience stores 0.138 (0.14) 0.048 * (0.02)
Network Buffer
500 m 1000 m
Estimate (SE) Estimate (SE)
Home Neighbourhood
Environment
Number of public recreation -0.182 * (0.09) 0.017 (0.03)
opportunities
Number of fast-food outlets 0.139 (0.10) 0.026 (0.02)
Number of convenience stores 0.219 * (0.10) 0.026 (0.02)
School Neighbourhood
Environment
Number of public recreation 0.305 (0.25) 0.389 (0.24)
opportunities
Number of fast-food outlets 0.166 (0.26) -0.005 (0.02)
Number of convenience stores 0.18 (0.13) 0.021 (0.02)
School
Walkshed
Estimate (SE)
Home Neighbourhood
Environment
Number of public recreation
opportunities
Number of fast-food outlets
Number of convenience stores
School Neighbourhood
Environment
Number of public recreation -0.017 (0.05)
opportunities
Number of fast-food outlets 0.095 * (0.03)
Number of convenience stores 0.057 * (0.02)
* Significant at p=0.05
Table 4. Results of the Multivariate Multi-level Regression Analysis
Assessing the Influence of the School and Home Built Environment
on Children's BMI Z-Scores
Fixed Effect Estimate SE Est./SE p-value
Home environment
(500 m network buffer)
Recreation opportunities -0.203 0.093 -2.183 0.03
Fast-food outlets 0.012 0.121 0.099 0.92
Convenience stores 0.190 0.122 1.559 0.12
School environment (walkshed)
Recreation opportunities -0.019 0.041 -0.471 0.64
Fast-food outlets 0.073 0.034 2.160 0.03
Convenience stores 0.020 0.021 0.947 0.34
Random effects Estimate SE Est./SE p-value
Child-level residual 1.673 0.080 20.821 0.00
variance
School-level residual 0.021 0.019 1.074 0.28
variance
Intraclass correlation coefficient for BMI z-score=0.039 (p=0.041).
Number of children=891; number of clusters=28.