| Literature DB >> 32743975 |
Peng Jia1,2,3, Xiongfeng Pan3,4, Fangchao Liu5, Pan He6, Weiwei Zhang7, Li Liu8, Yuxuan Zou3,9, Liding Chen10.
Abstract
Land use mix (LUM) in the neighbourhood is an important aspect for promoting healthier lifestyles and consequently reducing the risk for childhood obesity. However, findings of the association between LUM and childhood obesity remain controversial. A literature search was conducted on Cochrane Library, PubMed and Web of Science for articles published before 1 January 2019. In total, 25 cross-sectional and two longitudinal studies were identified. Among them, Geographic Information Systems were used to measure LUM in 15 studies, and perceived LUM was measured in 12 studies. Generally, most studies revealed an association between a higher LUM and higher PA levels and lower obesity rates, although some studies also reported null or negative associations. The various exposure and outcome assessment have limited the synthesis to obtain pooled estimates. The evidence remains scare on the association between LUM and children's weight status, and more longitudinal studies are needed to examine the independent pathways and causality between LUM and weight-related behaviours/outcomes.Entities:
Keywords: built environment; child; land use mix; obesity
Mesh:
Year: 2020 PMID: 32743975 PMCID: PMC7988622 DOI: 10.1111/obr.13098
Source DB: PubMed Journal: Obes Rev ISSN: 1467-7881 Impact factor: 9.213
FIGURE 1Study exclusion and inclusion flowchart
Basic characteristics of the included studies
| First author (year) | Study design | Study area, country (scale) | Sample size | Sample age (years, range and/or mean ± SD) | Statistical model |
|---|---|---|---|---|---|
| Buck (2015) | C | Delmenhorst, Lower Saxony, Germany (C) | 400 | 6.7 ± 1.7 in 2007 and 2008 | Basic log‐gamma regression |
| Carver (2014) | L | Norfolk, UK (C) | 1121 | 9 and 10 in 2007 and 2008 | Multivariable regression |
| Deforche (2010) | C | East‐and West‐Flanders, Belgium (S2) | 1445 | 17.4 ± 0.6 in 2008 | Moderated multilevel regression |
| De meester (2013) | C | Ghent, Belgium (C) | 637 | 14.5 ± 0.9 in 2008 and 2009 | Stepwise linear regression |
| De meester (2014) | C | East‐and West‐Flanders, Belgium (S2) | 736 | 11.2 ± 0.5 in 2010 and 2011 | Stepwise linear regression |
| D'Haese (2015) | C | Ghent, Belgium (C) | 606 | 9–12 in 2011–2013 | Multilevel logistic regression |
| Dwicaksono (2017) | C | New York State, USA (S) | 1246 | Not available | Ordinary least squares linear regression |
| Frank (2007) | C | Atlanta, Georgia, USA (C) | 3161 | 12–15 in 2001 and 2002 | Logistic regression |
| Hinckson (2017) | C | Auckland and Wellington, New Zealand (C2) | 524 | 15.8 ± 1.6 in 2013 and 2014 | Moderated multilevel regression |
| Hobin (2012) | C | Ontario, Canada, (S) | 22 117 | 9–12 in 2005 and 2006 | Multilevel linear regression |
| Ito (2017) | C | Massachusetts, USA (S) | 18 713 | 9–12 in 2011–2015 | Multilevel linear regression |
| Kerr (2007) | C | Atlanta, USA (C) | 3161 | 5–18 in 2001 and 2002 | Stratified logistic regression |
| Kligerman (2007) | C | San Diego County, California, USA (C) | 98 | 14.6–17.6 in mid 1980s | Linear regression |
| Larsen (2009) | C | London, Ontario, Canada (C) | 614 | 11–13 in 2006 and 2007 | Stepwise logistic regression |
| Lovasi (2011) | C | New York, NY, USA (C) | 428 | 2–15 in 2003–2005 | Generalized estimating equations regression |
| Nelson (2010) | C | Ireland (N) | 2159 | 16.0 ± 0.7 in 2010 | Bivariate logistic regression |
| Noonan (2017) | C | Liverpool, England, UK (C) | 194 | 9–10 in 2014 | Multilevel linear regression |
| Oreskovic (2014) | C | Houston, USA (C) | NA | Not available | Linear regression |
| Rosenberg (2009) | C | Boston, Cincinnati and San Diego, USA (C3) | 458 | 5–18 in 2005 | Linear regression |
| Spence (2008) | C | Edmonton, Canada (C) | 501 | 5.0 ± 0.4 in 2004 | Logistic regression |
| Su (2013) | L | Los Angeles, California, USA (C) | 4338 | 5–7 in 2002 and 2003 | Multilevel linear regression |
| Timperio (2017) | C | Melbourne and Geelong, Victoria, Australia (C2) | 788 | 5–12 in 2002–2006 | Linear regression |
| Tung (2016) | C | Klang, Selangor, Malaysia (C) | 250 | 9–12 in 2016 | Multilevel linear regression |
| Van dyck (2013) | C | Ghent, Belgium (C) | 477 | 13–15 in 2013 | Moderated regression |
| Vanwolleghem (2016) | C | East‐ and West‐Flanders, Belgium (S2) | 126 | 10–12 in 2013 | Generalized linear regression |
| Verhoeven (2016) | C | Flanders, Belgium (S) | 562 | 17–18 in 2013 | Zero‐inflated negative binomial regression |
| Voorhees (2011) | C | Baltimore, Maryland, USA (C) | 350 | 9–12 in 2006 | Linear regression |
Study design: C—cross‐sectional; L—longitudinal.
Study scale: (N) —National; (S) —State (e.g., in the United States) or equivalent unit (e.g., province in China and Canada); (Sn)—n states or equivalent units; (CT)—County or equivalent unit; (CTn)—n counties or equivalent units; (C) —City; (Cn)—n cities.
Measures of land use mix, weight‐related behaviours and body‐weight status in the included studies
| First author (year) | Measures of land use mix (LUM) | Measures of weight‐related behaviour | Measures of weight‐related outcomes | Results about weight‐related behaviour | Results about weight‐related outcomes |
|---|---|---|---|---|---|
| Buck (2015) | The entropy index of 5 land use types in a 1‐km school road‐network buffer (playground, green space, residential, institutional and park) | MVPA | NA | LUM was negatively associated with MVPA. | NA |
| Carver (2014) | The entropy index of 17 land use types in a 1.6‐km school road‐network buffer (farmland, woodland, grassland, uncultivated land, other urban, beach, marshland, sea, small settlement, private garden, park, residential, commercial, building, multiple‐use building, other buildings, road and unclassified) | Walking/cycling independently to school | NA | LUM was associated with walking/cycling independently to school in girls. | NA |
| Deforche (2010) | Perceived LUM around children's homes by NEWS | Active transportation index (sum of active transport to school and in leisure‐time) | NA | LUM diversity was negatively associated with active transportation. | NA |
| De meester (2013) | Perceived LUM around children's homes by NEWS | Flemish physical activity questionnaire and the Dutch version of the NEWS | NA | A lower degree of LUM diversity is associated with more min/day active transport to and from school. | NA |
| De meester (2014) | Perceived LUM around children's homes by NEWS‐Y | Activity monitor and to fill in a survey questioning demographic factors and the Flemish physical activity questionnaire | NA | More active transport was reported when parents perceived more LUM diversity and good land use mix. | NA |
| D'Haese (2015) | Perceived LUM around children's homes by NEWS‐Y | Actigraph accelerometer for children's PA | NA | The higher LUM was associated with more PA in public recreation space. | NA |
| Dwicaksono (2017) | The entropy index of 4 land use types in a 1‐km school road‐network buffer (farmers' market, supermarket, fast‐food restaurant and intersection) | NA | Students whose body mass index are at or above the 95th percentile of the sex‐ and age‐specific values are considered obese | NA | Higher land use mix was only significantly associated with lower obesity rates among middle/high school students. |
| Frank (2007) | The entropy index of 3 land use types in a 1‐km school road‐network buffer (commercial, recreation and open space) | Walked at least once over 2 days | NA | LUM was all significantly related to walking. | NA |
| Hinckson (2017) | The entropy index of 3 land use types in 0.25‐, 0.5‐, 1‐, 2‐km school road‐network buffers (residential, park and shopping area) | Perceived attributes related to walking, PA and sedentary behaviour | NA | The higher LUM was associated with more PA in public recreation space. | NA |
| Hobin (2012) | The entropy index of 3 land use types in a 1‐km school road‐network buffer (commercial, residential and office) | Students' time spent in PA | NA | A negative association between LUM diversity and students' time spent in PA. | NA |
| Ito (2017) | The entropy index of 4 land use types in a 0.8‐km school road‐network buffer (residential, commercial, recreational and institutional) | Walk to school | NA | LUM was associated with the increased odds of children walking to school. | NA |
| Kerr (2007) | The entropy index of 4 land use types in a 1‐km school road‐network buffer (residential, commercial, open space and institutional) | Walking | NA | LUM was positively associated with walking. | NA |
| Kligerman (2007) | The entropy index of 5 land use types in 0.4‐, 0.8‐, 1.6‐km school road‐network buffers (residential, recreational, retail, park and institutional) | Accelerometer | NA | LUM was positively associated with MVPA. | NA |
| Larsen (2009) | The entropy index of 6 land use types in a 1‐km school road‐network buffer (recreational, agricultural, residential, institutional, industrial and commercial) | Children's mode of travel to and from school | NA | LUM may contribute to a more appealing walking environment for youths. | NA |
| Lovasi (2011) | The entropy index of 5 land use types in a 0.5‐km school road‐network buffer (subway, bus stop, park, residential and playground) | Accelerometer | BMI z‐score | LUM density were positively associated with PA. | LUM density were associated with adiposity |
| Nelson (2010) | Perceived LUM around children's homes by NEWS | Participants' self‐reported active | NA | The positive perception of places for walking/cycling, LUM diversity increased the odds of active commuting to school | NA |
| Noonan (2017) | Perceived LUM around children's schools by NEWS‐Y | NA | LUM diversity was positively associated with active school commuting. | NA | |
| Oreskovic (2014) | The entropy index of 3 land use types in a 1‐km school road‐network buffer (bicycle path, major road and park) | Accelerometer‐determined MVPA | NA | LUM was positively associated with daily MVPA. | NA |
| Rosenberg (2009) | Perceived LUM around children's homes by NEWS‐Y | NA | NA | LUM density was positively associated with PA. | NA |
| Spence (2008) | The entropy index of 4 land use types in a 1.5‐km school road‐network buffer (institutional, maintenance, dining and leisure) | NA | Risk of overweight | NA | No significant associations were observed for overweight or obese and LUM |
| Su (2013) | Fragstats: % of landscape in a particular use, Simpson's diversity index and contagion and interspersion in a 0.5‐km home/school road‐network buffer | Walking to school | NA | LUM was positively associated with walking to school | NA |
| Timperio (2017) | The entropy index of 4 land use types in a 0.8‐km school road‐network buffer (residential, agricultural, governmental and institutional) | Accelerometer‐determined MVPA | NA | LUM was positively associated with MVPA. | NA |
| Tung (2016) | Perceived LUM around children's homes by NEWS | PA questionnaire for older children and neighbourhood environmental walkability scale | NA | LUM was positively associated with PA. | NA |
| Van dyck (2013) | Perceived LUM around children's homes by NEWS | PA questionnaire and the neighbourhood environmental walkability scale | NA | LUM density was positively associated with PA. | NA |
| Vanwolleghem (2016) | Perceived LUM around children's homes by NEWS‐Y | Accelerometer‐determined MVPA | NA | LUM accessibility was negatively associated with MVPA. | NA |
| Verhoeven (2016) | Perceived LUM around children's homes by NEWS | Walking to school | NA | LUM was positively associated with PA. | NA |
| Voorhees (2011) | Perceived LUM around children's homes by NEWS | Accelerometer‐determined MVPA | NA | LUM accessibility was positively associated with MVPA. | NA |
Abbreviations: MVPA, moderate‐to‐vigorous physical activity; NA, not available; NEWS, Neighborhood Environment Walkability Scale; NEWS‐Y, Neighborhood Environment Walkability Scale for Youth; PA, physical activity.