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Contact with the biodiverse environment was coded as either indirect or direct
following Keniger etĀ al. (2013). Indirect contact ādoes not require a person to be
physically present in natureā (Keniger etĀ al. 2013, p.Ā 916) and can include viewing
nature through a window, and looking at photographs, paintings or motion pictures
of nature. Direct contact with nature stipulates that nature, or natural elements, are
physically present in the same space as the individual (Keniger etĀ al. 2013).1
Examples of direct contact include indoor plants, using urban green spaces for edu-
cation purposes, reading or having a picnic in the park, doing sports or exercise in a
natural setting, gardening and camping.
Moderating variables were categorised as either personal (e.g. age, gender, socio-
economic status) or contextual (e.g. urbanicity, safety) (Hartig etĀ
al. 2014; Markevych
etĀ al. 2017). Mediators were classified as āreducing harmā, ārestoring capacitiesā or
ābuilding capacitiesā according to Markevych etĀ
al. (2017). āReducing harmā consid-
ers the role of the natural environment to reduce exposure to environmental stressors
like heat or noise pollution. āRestoring capacitiesā mediators support renewal of
adapted resources that have become depleted through everyday demands, such as
attention restoration and stress recovery. āBuilding capacitiesā mediators highlight
the role of green spaces in strengthening an individualās capacity to acquire new
adaptive resources like fostering physical activity and social cohesion.
9.2.3 Synthesis ofĀ Results
To provide a synthesis of results assessing the influence of biodiversity on mental
health and well-being, a combined set of 24 studies, drawn from Lovell etĀ
al. (2014)
and from our updated review, was utilised. Nine quantitative studies identified in
Lovell etĀ al. (2014) that assessed biodiversity and mental health and well-being
relationships were included (TableĀ 9.1). Consequently, 4 studies from Lovell etĀ al.
(2014) with physical health as the outcome were excluded (Huynen etĀ al. 2004;
Poudyal etĀ al. 2009; Sieswerda etĀ al. 2001; Tilt etĀ al. 2007). Also excluded were 4
studies that, according to Lovell etĀ
al. (2014), did not directly assess biodiversity but
were included in their analysis nevertheless (Barton etĀ al. 2009; Curtin 2009;
Lemieux etĀ al. 2012; Pereira etĀ al. 2005). In this sense our synthesis of results is
more critical than Lovell etĀ
al.ās (2014) by including only those studies that consider
the biodiversity of the environment in some way. Fifteen of the 16 articles identified
in our updated search were included in the synthesis of results. Foo (2016) was
excluded from the synthesis of results because it analysed the associations between
use of the environment, individual differences in environmental experience, and
perceived physical activity, well-being and mental health given a certain level of
actual biodiversity instead of an investigation of the influence of biodiversity levels
on mental health and well-being.
1 This is a combination of Keniger etĀ al. (2013) āincidentalā and āintentionalā interaction types as
both describe being in the presence of nature. M. R. Marselle et al.
Biodiversity and Health in the Face of Climate Change
- Title
- Biodiversity and Health in the Face of Climate Change
- Authors
- Melissa Marselle
- Jutta Stadler
- Horst Korn
- Katherine Irvine
- Aletta Bonn
- Publisher
- Springer Open
- Date
- 2019
- Language
- English
- License
- CC BY 4.0
- ISBN
- 978-3-030-02318-8
- Size
- 15.5 x 24.0 cm
- Pages
- 508
- Keywords
- Environment, Environmental health, Applied ecology, Climate change, Biodiversity, Public health, Regional planning, Urban planning
- Categories
- Naturwissenschaften Umwelt und Klima