| Literature DB >> 35545010 |
Jing Shen1, Mengfei Li2, Qianhui Wang2, Ruidong Liu3, Mengmeng Ji4, Ruopeng An5.
Abstract
INTRODUCTION: This study systematically reviewed scientific evidence concerning the influence of green space on obesity in China.Entities:
Keywords: Body weight; China; Green space; Obesity; Review
Mesh:
Year: 2022 PMID: 35545010 PMCID: PMC9421664 DOI: 10.1159/000524857
Source DB: PubMed Journal: Obes Facts ISSN: 1662-4025 Impact factor: 4.807
Fig. 1Study selection flowchart.
Basic characteristics of the studies included in the review
| Study ID | First author, year | Region | Study design | Sample size | Age, years | Female, % | Sample characteristics | Statistical model | Non-response rate, % | Geographical coverage | Setting |
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| 1 | Zhang et al. [ | Shanghai | Cross-sectional | 1,100 | 46–80 | Middle-aged and older residents | Hierarchical linear models and hierarchical nonlinear models | 6 | Green and open spaces | Urban, rural | |
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| 2 | Chen et al. [ | Guangzhou | Cross-sectional | 938 | 18–70 | 58 | Adult residents | Multivariate analysis Logistic regression | 6.9 | Urban green space | Urban |
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| 3 | Huang et al. [ | China | Cross-sectional | 12,112 | 50+ | 53.17 | Middle-aged and older residents | Multilevel structural equation models | Neighborhood greenness | Urban, rural | |
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| 4 | Huang et al. [ | Shenyang, Anshan, and Jinzhou | Cross-sectional | 24,845 | 18–74 | 49 | Adult residents | Two-level logistic and generalized linear mixed regression models | 13.8 | Community greenness | Urban |
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| 5 | Leng et al. [ | Harbin | Cross-sectional | 4,155 | 20–98 | 47.7 | Adult residents | Logistic regression | Green space of neighborhood | Urban | |
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| 6 | Lu et al. [ | Shanghai | Cross-sectional | 403 | 18–80 | 51.4 | Adult residents | Structural equation modeling | 5.6 | Main green space in the survey area | Urban |
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| 7 | Xiao et al. [ | Shanghai | Cross-sectional | 8,988 | All ages | 54.08 | Residents | Two-level multilevel mixed-effects ordered logistic regression | 5.6 | Neighborhood greenness | Urban |
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| 8 | Yang et al. [ | Guangzhou | Cross-sectional | 418 | 16–60 | 55.5 | Residents | Ordered logit model | 7.1 | Neighborhood environments | Urban, suburban |
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| 9 | Yang et al. [ | Hong Kong | Cross-sectional | 1,148 | 11–13 | 48.6 | Primary school students | Multilevel regression analysis and structural equation modeling | Urban greenery | Urban | |
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| 10 | Bao et al. [ | Seven provinces/municipalities | Cross-sectional | 56,401 | 6–18 | 48.7 | Children and adolescents | Generalized linear mixed regression models | 4.5 | Greenness surrounding schools | Urban, rural |
Seven provinces/municipalities include Liaoning, Tianjin, Ningxia, Shanghai, Chongqing, Hunan, and Guangdong.
Measures of green space and body weight status in the studies included in the review
| Study ID | Type of green space measure | Detailed measure of green space | Type of body weight status measure | Detailed measure of body weight status |
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| 1 | Objective measure: GIS | Parkland proximity, green, and open spaces | Objective measure | BMI, overweight, obesity |
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| 2 | Self-report questionnaire | The distance and time from homes to green space | Self-report questionnaire | BMI, overweight, obesity |
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| 3 | Objective measure: Landsat 5 Thematic Mapper images | 1. Neighborhood greenness | Objective measure | Height, weight, waist circumference, BMI, general obesity, and abdominal obesity |
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| 4 | Objective measure: Landsat 5 Thematic Mapper satellite images, GIS | 1. NDVI | Objective measure | Height, weight, waist circumference, BMI, peripheral obesity, central obesity |
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| 5 | Objective measure: land use data, the field survey | Green space ratio, green view index, and type of evergreen tree configuration | Objective measure | Height, weight, BMI, overweight, obesity |
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| 6 | Self-report questionnaire | Perceptions of green space | Self-report questionnaire | BMI |
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| 7 | Objective measure: GIS, the novel technique of deep convolutional neural network architecture, Baidu street view images | Green access, green exposure index, NDVI, and view-based green index | Self-report questionnaire | Height, weight, BMI, overweight, obesity |
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| 8 | Objective measure: GIS, Baidu map application | Green coverage rate and distance to the park | Self-report questionnaire | Height, weight, BMI, overweight, obesity |
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| 9 | Objective measure: Land Department of Hong Kong SAR, Google street view images | The number of parks, NDVI, and street greenness | Self-report questionnaire | Height, weight, BMI, overweight, obesity |
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| 10 | Objective measure: ArcGIS, Landsat 8 Operational Land Imager (OLI) satellite images | 1. NDVI | Objective measure | BMI z-scores, waist circumference, and overweight/obesity |
GIS, geographic information system; BMI, body mass index; NDVI, normalized difference vegetation index; SAVI, soil-adjusted vegetation index.
Estimated effects of green space on body weight status in the studies included in the review
| Study ID | Estimated effects of green space on body weight status | Main findings of study |
|---|---|---|
| 1 | 1. A 1-SD increase in proximity of parkland (t = 2.238, | 1. Parkland proximity related to BMI: + |
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| 2 | Easier access to urban green space was related to lower odds of overweight or obesity when an urban green space was within 1 km (β = −0.320, | Accessibility of green space related to obesity: − |
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| 3 | 1. A significant negative association between residential greenness and overweight/obesity (odds = 0.73, 95% CI = 0.58, 0.92) | 1. Residential greenness related to overweight/obesity: − |
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| 4 | Each interquartile range (0.17 unit) increase in NDVI500-m was associated with 0.18 kg/m2 (95% CI = 0.24, 0.11) lower BMI, 20% (95% CI = 26%, 13%) lower odds for peripheral obesity, and 12% (95% CI = 17%, 7%) lower odds for central obesity | 1. Community greenness related to BMI: − |
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| 5 | 1. In neighborhoods with a green space ratio lower than 28%, residents had a higher risk of overweight or obesity (OR = 1.22, 95% CI = 1.01, 1.46) | 1. Green space ratio equal to or lower than 28% related to overweight/obesity: + |
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| 6 | Perception of large parks positively correlates to BMI (β = 0.169, SE = 0.087, | 1. Perception of large parks related to BMI: + |
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| 7 | 1. Longer distance from parks relieves the risk of obesity or overweightness (β = −0.004, | 1. View-based green index related to obesity: − |
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| 8 | 1. Green coverage rate was an important factor affecting residents’ BMI and has a significant negative impact on the risk of overweight or obesity ( | 1. Green coverage rate related to BMI, overweight, or obesity: − |
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| 9 | 1. Street greenness (β = −0.132, 95% CI = 0.019, 0.257) and the number of parks surrounding schools (β = −0.118, 95% CI = 0.006, 0.204) were significantly negatively associated with BMI with the 400 m buffer | 1. Street greenness related to BMI: − |
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| 10 | 1. An interquartile range increase in NDVI-1,000 m was associated with lower zBMI (β = −0.11, 95% CI = −0.13, −0.09) and waist circumference (β = −0.64, 95% CI = −0.78, −0.50) | 1. NDVI-1,000 m related to zBMI: − |
Correlation: + positively, − negatively, 0 insignificantly. BMI, body mass index; NDVI, normalized difference vegetation index.
Study quality assessment
| Study ID criterion | 1 | 2 | 3 | 4 | 5 | 6 | 7 | 8 | 9 | 10 |
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| 1. Was the research question or objective in this paper clearly stated? | 1 | 1 | 1 | 1 | 1 | 1 | 1 | 1 | 1 | 1 |
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| 2. Was the study population clearly specified and defined? | 1 | 1 | 1 | 1 | 1 | 1 | 1 | 1 | 1 | 1 |
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| 3. Was the participation rate of eligible persons at least 50%? | 1 | 1 | 1 | 1 | 1 | 1 | 1 | 1 | 1 | 1 |
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| 4. Were all the subjects selected or recruited from the same or similar populations (including the same time period)? Were inclusion and exclusion criteria for being in the study pre-specified and applied uniformly to all participants? | 1 | 1 | 1 | 1 | 1 | 1 | 1 | 1 | 1 | 1 |
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| 5. Was a sample size justification, power description, or variance and effect estimates provided? | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
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| 6. For the analyses in this paper, were the exposure(s) of interest measured prior to the outcome(s) being measured? | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
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| 7. Was the timeframe sufficient so that one could reasonably expect to see an association between exposure and outcome if it existed? | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
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| 8. For exposures that can vary in amount or level, did the study examine different levels of the exposure as related to the outcome (e.g., categories of exposure or exposure measured as continuous variable)? | 0 | 1 | 0 | 1 | 0 | 0 | 0 | 1 | 0 | 1 |
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| 9. Were the exposure measures (independent variables) clearly defined, valid, reliable, and implemented consistently across all study participants? | 1 | 0 | 1 | 1 | 1 | 0 | 1 | 1 | 1 | 1 |
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| 10. Was the exposure(s) assessed more than once over time? | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
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| 11. Were the outcome measures (dependent variables) clearly defined, valid, reliable, and implemented consistently across all study participants? | 1 | 0 | 1 | 1 | 1 | 0 | 0 | 0 | 0 | 1 |
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| 12. Were the outcome assessors blinded to the exposure status of participants? | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
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| 13. Was loss to follow-up after baseline 20% or less? | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
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| 14. Were key potential confounding variables measured and adjusted statistically for their impact on the relationship between exposure(s) and outcome(s)? | 1 | 0 | 1 | 1 | 1 | 1 | 1 | 1 | 1 | 1 |
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| Total score | 7 | 5 | 7 | 8 | 7 | 5 | 6 | 7 | 6 | 8 |
This study quality assessment tool was adopted from the National Institutes of Health's Quality Assessment Tool for Observational Cohort and Cross-Sectional Studies. For each criterion, a score of one was assigned if “Y” was the response, whereas a score of zero was assigned otherwise. A study-specific global score, ranging from 0 to 14, was calculated by summing up scores across all 14 criteria. Study quality assessment helped measure strength of scientific evidence, but was not used to determine the inclusion of studies.