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Planning reserves for ecosystem services

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Ecosystem services and biodiversity map differently, so conservation plans face spatial tradeoffs.

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Conservation planning for ecosystem services

Chan KM, Shaw MR, Cameron DR, et al. · PLoS biology · 2006

doi.org/10.1371/journal.pbio.0040379Read the full paper ↗229 citationscc by

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Planning reserves for ecosystem services

These passages occur verbatim in the stored paper text. They support the points listed below; they do not verify every statement in the explanation.

500 ha units.

These features are allocated by “planning units,” which are the uniform spatial unit of analysis (500 ha in this analysis).

20 MARXAN runs.

In this analysis, we ran MARXAN 20 times for each service to ensure an even sampling of possible networks.
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What they did

Mapped seven benefit functions across 11,272 planning units and built MARXAN conservation networks for a California ecoregion.

What they found

Services had distinct spatial patterns and low correlations; places like Salinas Valley scored high for pollination but not other services.

The limits

What it doesn't show

Does not field-test whether implementing a network delivers measured service gains.

Key terms

Ecosystem service
Human benefit from ecosystems (e.g., pollination).
MARXAN
Spatial optimizer for reserve networks.
Planning unit
500 ha analysis cell.
Irreplaceability
Selection frequency across solutions.
Tradeoff
Gains in one service cost another.
Biodiversity feature
Species/habitat conservation target.

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Benefit functions:

Common questions

Services mapped?

Seven.

Unit size?

500 ha.

MARXAN runs?

20 per service.

Correlations?

Generally low.

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