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The biodiversity level (low vs. high) was crossed with the setting location (urban vs. peri-urban) as follows: urban squares with green elements, urban parks, pinewood forest plantations, and peri-urban natural protected areas.
This is especially true for some tropical areas, where the overall biodiversity level is the highest and its loss is the most intensive.
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The most important thing Ewers and his team are trying to discover is what additional wildlife they can maintain in forest fragments, and what impact the scale and distribution of those fragments will have on biodiversity levels.
In addition, it is recognised that biodiversity levels vary between agro-ecological regions [3].
Despite high biodiversity levels, many groups of marine invertebrates in this area have remained uninvestigated.
In agricultural landscapes the amount and variety of available habitat is directly correlated with biodiversity levels.
Regionalisation of LoCs must be provided for as biodiversity levels and protection goals vary across the EU.
With current increase of biodiversity loss during the last decades, there is an urgent need to quickly estimate biodiversity levels.
Second, degraded lands may support biodiversity levels similar to or even above those of surrounding managed landscapes.
These results go some way in understanding the fact that although most semi-arid catchments have very low yearly recharge estimates, they are still capable of sustaining high biodiversity levels.
The high biodiversity of bioconstructors during the Givetian-Frasnian acme of Palaeozoic reef development contrasts sharply with very low biodiversity levels during the Famennian.
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