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PRESERVING BIODIVERSITY IN URBAN AREAS

Preserving biodiversity becomes a major challenge as our cities grow and expand. How can we plan a city that embraces biodiversity and welcomes wildlife?

 

One of the answers comes from an emerging discipline of urban wildlife ecology and conservation. It is officially called ecological land-use complementation (ECL), and we use it as one of central concepts in our research. In brief, ECL draws on the three main hypotheses:

 

1. Lifecycle migration. Accordingly, animals use different land patch types on different stages of their lifecycle. For example, birds might move away from traditional habitats for nesting. Hence, different habitat types should be available;

 

2. Habitat island. Accordingly, area is a key determinant for species occurrence and diversity and it is generally assumed that habitat diversity increases with area. Because large islands have more habitat diversity, they hold larger populations, and a greater number of populations. Hence, the age and size of a green ara are important predictors of biodiversity within it.

 

3. Proximity matters. Our parks and green areas  are rarely effectively united into a single network connected by wooded corridors, such as green streets, private gardens and yards, so their capability of increasing biodiversity is reduced. In the same time, we all can be part of a movement that will transform our streets, gardens and backyards into wildlife-friednly corridors of life.

SO, what does it take to build an a city-scaled green network?

 

On a city level, the green network plan should consist of the following components:

 

1. core zones (large protected areas and surrounding forests and riparian habitats);

 

2. wildlife corridors (swaths of protected land that connects the core zones, allowing wildlife movement and, ideally, also utilize rivers or coastal areas);

 

3. urban reserves (preserved or restored natural habitats that serve that allow interaction between urbanites and wildlife).

If the connections between these elements merge them into a single living system, we get a chance to live in a city that is welcoming the wildlife. However, if we fail to come up with necessary policies and, most importantly, get the community involved, we will continue living in a concrete urban ocean that separates occasional green islands.

IS ANYONE KEEPING TRACK OF BIODIVERSITY IN SWEDEN?
 

Large amounts of biodivesity data reflecting the state of the Swedish environment is continuously accumulated by scientists, conservationists and amateurs. The data is, however, stored in many different databases. Swedish LifeWatch makes all this information available and searchable through a common electronic infrastructure. In addition it offers tools for analyses, visualisation and presentation.

1

The two processes of (a) landscape complementation, and (b) landscape supplementation. Landscape complementation highlights the requirement for many species to link together different habitat types to complete their life cycles and is a measure of the proximity of critical habitat types and the degree to which organism can move between them.

2

Relative to when two green-area patches are located in isolation from each other (situation a), green-area patches located close to each other (situation b), could more optimally provide for landscape complementation and supplementation functions and the support of ecosystem processes, such as seed dispersal and pollination (represented by the arrows).

3

In (a) a golf course with ponds with no forest patches could serve as suitable breeding-habitats for amphibians when located adjacent to a forest habitat due to landscape complementation. Similarly, in (b) when urban gardens are clustered adjacent to forest patches and crop fields, pollinators may be promoted. Different pollinators may use gardens for collecting pollen and nectar resources, use adjacent forest habitats as nesting sites, and perform important pollination of food cultivars on adja

4

As we see from this graph based on research of green zones in Madrid, when species population density reaches certain level animals start to explore wooded streets adjacent to a core green zone.

5

Species richness in natural landscapes appears to be much higher than in conventional urban parks with pavement, lights and furniture

Suggested readings:

Colding, J., Ecological land-use complementation’ for building resilience in urban ecosystems, Landscape and Urban Planning 81 (2007) 46–55.

Fernández-Juricic, E., Jokimäki, J., A habitat island approach to conserving birds in urban landscapes: case studies from southern and northern Europe, Biodiversity and Conservation 10: 2023–2043, 2001.

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