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Successful reintroduction of species: improving on windows of opportunity for biodiversity repair
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To overcome resistance of degraded ecological communities to restorative interventions, we need to understand windows of opportunity—limited time frames when species reintroduction attempts are still successful. More specifically, we need to understand what makes these windows close, as this may enable us to stretch or reopen them. We investigated this using models of simple food web modules. We show how joint changes of bottom–up and top–down control may be applied to change windows of opportunity and increase reintroduction success. Which reintroduction densities were most effective seemed system‐specific. A more general result is that reintroduction success was strongly enhanced by low to intermediate carrying capacities of basal species (e.g. periphyton and other algae in streams). This can be seen as equivalent to low to intermediate nutrient levels. When these were too high, almost any combination of restorative measures was rendered ineffective. Interestingly, reintroducing primarily and secondarily lost species at the same time was more effective than sequential reintroductions that first attempted to fix secondary extinctions. We could further enhance the success of species reintroductions by reducing the carrying capacities of basal species before the reintroduction of primarily and secondarily lost species. We discuss our results in the light of empirical work on macro‐invertebrates in streams. This serves to exemplify how our results can be applied in the practice of ecological restoration.
Title: Successful reintroduction of species: improving on windows of opportunity for biodiversity repair
Description:
To overcome resistance of degraded ecological communities to restorative interventions, we need to understand windows of opportunity—limited time frames when species reintroduction attempts are still successful.
More specifically, we need to understand what makes these windows close, as this may enable us to stretch or reopen them.
We investigated this using models of simple food web modules.
We show how joint changes of bottom–up and top–down control may be applied to change windows of opportunity and increase reintroduction success.
Which reintroduction densities were most effective seemed system‐specific.
A more general result is that reintroduction success was strongly enhanced by low to intermediate carrying capacities of basal species (e.
g.
periphyton and other algae in streams).
This can be seen as equivalent to low to intermediate nutrient levels.
When these were too high, almost any combination of restorative measures was rendered ineffective.
Interestingly, reintroducing primarily and secondarily lost species at the same time was more effective than sequential reintroductions that first attempted to fix secondary extinctions.
We could further enhance the success of species reintroductions by reducing the carrying capacities of basal species before the reintroduction of primarily and secondarily lost species.
We discuss our results in the light of empirical work on macro‐invertebrates in streams.
This serves to exemplify how our results can be applied in the practice of ecological restoration.
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