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it is relevant to take the functional role of the area within that ecosystem into
account. For example, the redevelopment of a park may either be beneficial or det-
rimental to this function.
We will focus on the residential environment for a moment. This environment is
defined in very different ways. In some studies it is defined as an administrative unit,
such as a census tract or postcode area. In other studies, the residential area is
defined as a buffer around the resident’s home. In the latter case, the buffer sizes that
are used vary considerably, from 100 metres up to 3
km (Egorov et
al. 2017; van den
Berg et
al. 2010). There are no clear rules for the most appropriate definition to use.
However, using the boundaries of administrative units may be considered rather
arbitrary from the perspective of a citizen’s lived experience. A very nearby green
area that is located just on the other side of an administrative boundary may be as
relevant as a green area within one’s own administrative area (which might even be
located further away). Furthermore, administrative units may not all have the same
size, which may introduce confounds.
As for using buffer sizes, it may be argued that the optimal size depends on the
mobility of the population, or the population segment, at hand. For example, when
focusing on physical activity during outdoor play without adult supervision by chil-
dren below the age of 10
years, then in many contexts using a buffer size of 1
km or
more does not seem very sensible; parents usually do not allow their young children
to play that far away from home on their own. Using a ‘wrong’ buffer size is likely
to lower the strength of associations. If too large, irrelevant natural areas or natural
elements are included; if too small, relevant natural areas/elements are ignored.
8.2.3 How to Measure Distance?
With regard to the use of distance in buffer approaches, there is also the issue of
whether this should be Euclidean distance or network distance. Accessibility
depends more on network distance than on Euclidean distance, since in the latter
case barriers may prevent people from travelling in a straight line. However, net-
work distances depend on the mode of transport. The network for travelling by foot
may be quite different from that for travelling by car. Stairs, lawns and small alleys
may be accessible or crossed by foot, but not by car. Incomplete networks can easily
lead to an overestimation of network distance for some people, and in this way
introduce a source of error. Nowadays, some researchers also take vertical distance
into account (Jim and Chen 2010). A person living on the 20th floor of a high-rise
residential building first has to get to the ground level, before getting out of doors
(except for balconies and roof gardens, of course). When small buffer sizes are con-
sidered appropriate, taking vertical distance into account may make a substantial
difference.
8 Biodiversity in the Context of ‘Biodiversity – Mental Health’ Research
Biodiversity and Health in the Face of Climate Change
- Titel
- Biodiversity and Health in the Face of Climate Change
- Autoren
- Melissa Marselle
- Jutta Stadler
- Horst Korn
- Katherine Irvine
- Aletta Bonn
- Verlag
- Springer Open
- Datum
- 2019
- Sprache
- englisch
- Lizenz
- CC BY 4.0
- ISBN
- 978-3-030-02318-8
- Abmessungen
- 15.5 x 24.0 cm
- Seiten
- 508
- Schlagwörter
- Environment, Environmental health, Applied ecology, Climate change, Biodiversity, Public health, Regional planning, Urban planning
- Kategorien
- Naturwissenschaften Umwelt und Klima