| Literature DB >> 35136275 |
Galleguillos-Torres Marcelo1, Brouillet Constance1, Molloy Joseph2, Axhausen Kay2, Zani David2, Van Strien Maarten1, Grêt-Regamey Adrienne1.
Abstract
Densification of cities threatens the provision of public open space for people living in and around cities. The increasing evidence of the many benefits of recreational walking for physical and mental health during the COVID-19 pandemic has highlighted an urgent need for fostering the availability of public open space. In this context, urban planners need information to anticipate recreational needs and propose long-term, resilient solutions that consider the growing demand driven by increasing urban population and intensified in times of crisis such as the recent pandemic. In this paper, we harness the unique large MOBIS:COVID-19 GPS travel diary data on mobility behaviour collected during a normal baseline period and during the first wave of the Covid-19 pandemic in the Canton of Zurich Switzerland. We estimate a sufficiency rate that allows to geolocate locations where the demand for public open space is higher than the available offer. In a second step, we explore if preference patterns for recreational areas have changed during the pandemic. Results indicate that the main cities and important towns in the case study area are saturated by current demand, and that the pandemic has amplified the problem. In particular, urban dwellers look for tranquil areas to recreate. Such information is crucial to guide decision-making processes for planning the cities of the future.Entities:
Keywords: Covid-19 pandemic; Public open spaces; Recreational walking; Sufficiency rate
Year: 2022 PMID: 35136275 PMCID: PMC8813161 DOI: 10.1016/j.landurbplan.2022.104373
Source DB: PubMed Journal: Landsc Urban Plan ISSN: 0169-2046 Impact factor: 6.142
Fig. 1Case study area – Canton of Zurich, Switzerland, with 20.1% settlement area, 43.4% agricultural area, 30.7% forest areas, and 5.8% non-productive area.
Fig. 2Demand for public open space during baseline (left) and Covid-19 period (right) in the Canton of Zurich, Switzerland. Demand was calculated as the daily percentage of the population in the service area that did a recreational walk during the period. Lighter colours mean less people are in need of public space, while darker colours mean more people require walkable open space.
Fig. 3Supply capacity of public open space in the Canton of Zurich, Switzerland. Supply was calculated as the number of people that could fit the public open space area available in each raster cell. Lighter colours mean that there is little available public open spaces, darker colours mean there is more public open space.
Georeferenced explanatory variables used to predict the sum of the walked distance per hectare adjusted for population. Detailed descriptions of the variables are presented in Appendix 3.
| THEMATIC GROUPS | VARIABLES | Units (all calculated per hectare cell) | Source | Spatial resolution |
|---|---|---|---|---|
| Settlements | Area of settlement area | m2 | SwissTLM3D ( | 0.2–3 |
| Road network and accessibility | Distance to public transport | m | ( | 1 |
| Roughness and aspect | Mean slope | ° | SwissALTI3D ( | 2 |
| Mean altitude | m | SwissALTI3D ( | 2 | |
| Visibility index | % of area with direct view | ( | 100 | |
| Infrastructures for outdoor activities (hiking, biking) | Density of hiking trails | m2 | SwissTLM3D ( | 0.2–3 |
| Streams and rivers | Length of stream and river shores | m | SwissTLM3D ( | 0.2–3 |
| Distance to streams and rivers | m | SwissTLM3D ( | 0.2–3 | |
| Lakes | Length of lakeshores | m | SwissTLM3D ( | 0.2–3 |
| Distance to lakes | m | SwissTLM3D ( | 0.2–3 | |
| Woodlands | NDVI | no unit | Dr. Achilleas Psomas, WSL | 10 |
| Share of forest | % | SwissTLM3D ( | 0.2–3 | |
| Land -use/-cover | Vegetation height (VHM) | m | ( | 1 |
| Share of shrub | % | SwissTLM3D ( | 0.2–3 | |
| Share of grass | % | SwissTLM3D ( | 0.2–3 | |
| Number of land-use classes | Count within a radius of 200 | Swiss Land Use Statistics (Swiss Federal Statistical Office, GEOSTAT) | 100 | |
| Disturbance | Tranquillity index | no unit | ( | 100 |
Fig. 4Walked distance per ha during baseline (left) and Covid-19 period (right) adjusted for population for the Canton of Zurich, Switzerland. Each cell is showing the daily average of the amount of meters walked during the period divided by the population density. Lighter colours mean fewer meters of recreational walks took place relative to the residential population; darker colours mean more meters were walked relative to the residential population.
Fig. 5Walking areas sufficiency rate (%) for the Canton of Zurich during (a) baseline period, and (b) Covid-19 period (zoom-in to Zurich city and Winterthur). Red colours mean the recreational walking space is saturated so it is not enough for the residents in the service area of the pixel. Purple colours indicate that the recreational walking space is enough but close to saturation.
Summary of fitted count regression models: regression coefficients and goodness of fit results for the Hurdle and zero-inflated models for the baseline period (left) and the Covid-19 period (right). In red: negative influence, in green: positive influence on dependant variable.
Fig. 6Permutation-based variable importance of both models during the baseline period (left) and the Covid-19 period (right).
Fig. 7Median distance walked during the baseline and Covid-19 periods for several sociodemographic groups.
| Variables | Description | Source | Spatial resolution |
|---|---|---|---|
| Distance to public transport | The centroid of each cell was located and the distance to bus or tram stop was calculated. Train stations were also considered. In case of several public transport options, the closest one was selected. | (Kanton Zurich, 2021) | 1 |
| Mean slope | The mean slope inside the cell. | SwissALTI3D ( | 2 |
| Mean altitude | The mean altitude inside the cell. | SwissALTI3D ( | 2 |
| Visibility index | Visibility index calculate how many other cells are visible from the corresponding cell using a view radius and digital elevation models. | ( | 100 |
| Density of hiking trails | The area of hiking trails was calculated inside each cell. Then a percentage of hiking trail area was calculated for each cell. | SwissTLM3D ( | 0.2–3 |
| Distance to streams and rivers | The centroid of each cell was located and the distance to streams or rivers was computed. In case of several streams or rivers, the closest one was selected. | SwissTLM3D ( | 0.2–3 |
| Distance to lakes | The centroid of each cell was located and the distance to lakes or any water surface (ponds) was calculated. In case of several lakes or ponds, the closest one was selected | SwissTLM3D ( | 0.2–3 |
| NDVI | Average NDVI (Normalized Difference Vegetation Index) for each cell. | Dr. Achilleas Psomas, WSL, Switzerland | 10 |
| Vegetation height | Average Vegetation height was calculated for each cell. Vegetation height was obtained from digital surface models, digital elevation models, and vegetation indexes. | ( | 1 |
| Share of shrubs | The percentage of shrubs area in each cell was calculated. | SwissTLM3D ( | |
| Number of land use classes | The number of land use classes inside each cell. | Swiss Land Use Statistics (Swiss Federal Statistical Office, GEOSTAT) | 100 |
| Tranquillity index | Average tranquillity index was computed for each cell. Tranquillity index is computed based on a big list of hearing and seeing stimulus. The more important factors defining the tranquillity index are: noises from cars, and motorbikes, groups of people (hearing and seeing) and urban developments (hearing and seeing) on the negative side. Birdsong, peace and quiet sounds, and seeing a natural landscape are the more important positive influences on the index. | ( | 100 |