| Literature DB >> 24597725 |
Patricia Jasmin Krenn1, Pekka Oja, Sylvia Titze.
Abstract
BACKGROUND: Despite evidence that environmental features are related to physical activity, the association between the built environment and bicycling for transportation remains a poorly investigated subject. The aim of the study was to improve our understanding of the environmental determinants of bicycling as a means of transportation in urban European settings by comparing the spatial differences between the routes actually used by bicyclists and the shortest possible routes.Entities:
Mesh:
Year: 2014 PMID: 24597725 PMCID: PMC3995950 DOI: 10.1186/1479-5868-11-31
Source DB: PubMed Journal: Int J Behav Nutr Phys Act ISSN: 1479-5868 Impact factor: 6.457
Descriptive characteristics of the study sample (n = 113)
| | | |
| Female | 62 | 55 |
| Male | 51 | 45 |
| | | |
| <35 years | 45 | 40 |
| 35–50 years | 45 | 40 |
| >50 years | 23 | 29 |
| | | |
| Compulsory school | 18 | 16 |
| Apprenticeship, intermediate vocational degree | 30 | 27 |
| High-school diploma | 32 | 28 |
| University graduates | 33 | 29 |
| | | |
| <25 | 92 | 81 |
| ≥25 | 21 | 19 |
Differences in distance between the actually used and the shortest possible bicycling routes (n = 278)
| Median | 2337 | 2146 | 168 | 7.6 | <0.001 |
| IQR | 2113 | 1860 | 343 | 10.1 | |
| Minimum | 383 | 377 | 0 | 0 | |
| Maximum | 13864 | 12494 | 1946 | 37 |
IQR: Inter-quartile range.
Comparison of the environment along the actual and shortest possible routes (n = 113)
| | | | | |
| Bicycle pathwaysa | 30.0 (±28,3) | 19.3 (±20,8) | 10.7 | |
| Bicycle lanesa | 31.3 (±26.7) | 30.6 (±22.7) | 0.5 | 0.723 |
| Side roads without bicycle lanesa | 21.6 (±14,5) | 24.6 (±14,6) | −3.0 | |
| Main roads without bicycle lanesa | 9.8 (±17.7) | 21.2 (±28.1) | −10.4 | |
| Traffic lightsb | 1.5 (±1,1) | 1.7 (±1,0) | −0.2 | |
| Crossingsb | 1.3 (±0.9) | 1.6 (±1.0) | −0.3 | |
| | | | | |
| Green and aquatic areasc | 19.2 (±10.9) | 14.5 (±7.7) | 4.7 | |
| -Urban treesb | 44.9 (±30.7) | 42.2 (±27.3) | 2.7 | 0.089 |
| -Sports and recreation areasc | 7.7 (±8.7) | 4.3 (±5.2) | 3.4 | |
| -Playing fieldsc | 0.9 (±1.2) | 0.8 (±1.5) | 0.1 | |
| -Forestsc | 0.6 (±1.8) | 0.5 (±1.5) | 0.1 | 0.341 |
| -Aquatic areasc | 2.9 (±4.6) | 1.3 (±2.1) | 1.6 | |
| | | | | |
| Steepnessd | 0.2 (±0.6) | 0.4 (±0.9) | 0.2 | |
| | | | | |
| Residential areasc | 28.6 (±20.1) | 28.1 (±19.4) | 0.5 | 0.778 |
| Industrial and commercial areasc | 3.2 (±4.7) | 3.2 (±4.7) | 0.0 | 0.870 |
| Residential densitye | 64.2 (±30.2) | 67.6 (±29.2) | −3.4 | |
| Land-use mixf | 0.82 (±0.1) | 0.79 (±0.1) | 0.02 | |
| Shops and servicesb | 4.4 (±4.5) | 5.4 (±5.0) | −1.0 |
a = % of the trip length, b = points per 1 km trip length, c = % of the environment along the trip (15 m buffer), d = sum of the gradient values per 1 km trip (0: flat – 8: very steep), e = residences per ha in the route neighbourhood, f = value from the LUM formula (Frank et al., [18]), SD = standard deviation.
* = paired t-tests for normally distributed data and Wilcoxon tests for data with a skewed distribution.