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Biodiversity and Health in the Face of Climate Change
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188 Contact with the biodiverse environment was coded as either indirect or direct following Keniger etĀ  al. (2013). Indirect contact ā€œdoes 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 ā€˜reducing harm’, ā€˜restoring capacities’ or ā€˜building capacities’ according to Markevych etĀ  al. (2017). ā€˜Reducing harm’ consid- ers the role of the natural environment to reduce exposure to environmental stressors like heat or noise pollution. ā€˜Restoring capacities’ mediators support renewal of adapted resources that have become depleted through everyday demands, such as attention restoration and stress recovery. ā€˜Building capacities’ mediators highlight the role of green spaces in strengthening an individual’s 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.’s (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) ā€˜incidental’ and ā€˜intentional’ interaction types as both describe being in the presence of nature. M. R. Marselle et al.
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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
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Biodiversity and Health in the Face of Climate Change