Spatial prioritisation for conserving ecosystem services: comparing hotspots with heuristic optimisation

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Spatial prioritisation for conserving ecosystem services : comparing hotspots with heuristic optimisation. / Schröter, Matthias; Remme, Roy P.

In: Landscape Ecology, Vol. 31, No. 2, 01.02.2016, p. 431-450.

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@article{c6b7f4143a2044a48e3ecadaf259a595,
title = "Spatial prioritisation for conserving ecosystem services: comparing hotspots with heuristic optimisation",
abstract = "Context: The variation in spatial distribution between ecosystem services can be high. Hence, there is a need to spatially identify important sites for conservation planning. The term {\textquoteleft}ecosystem service hotspot{\textquoteright} has often been used for this purpose, but definitions of this term are ambiguous. Objectives: We review and classify methods to spatially delineate hotspots. We test how spatial configuration of hotspots for a set of ecosystem services differs depending on the applied method. We compare the outcomes to a heuristic site prioritisation approach (Marxan). Methods: The four tested hotspot methods are top richest cells, spatial clustering, intensity, and richness. In a conservation scenario we set a target of conserving 10 % of the quantity of five regulating and cultural services for the forest area of Telemark county, Norway. Results: Spatial configuration of selected areas as retrieved by the four hotspots and Marxan differed considerably. Pairwise comparisons were at the lower end of the scale of the Kappa statistic (0.11–0.27). The outcomes also differed considerably in mean target achievement, cost-effectiveness in terms of land-area needed per unit target achievement and compactness in terms of edge-to-area ratio. Conclusions: An ecosystem service hotspot can refer to either areas containing high values of one service or areas with multiple services. Differences in spatial configuration among hotspot methods can lead to uncertainties for decision-making. This also has consequences for analysing the spatial co-occurrence of hotspots of multiple services and of services and biodiversity.",
keywords = "Hot spot, Mapping, Modelling, Overlap, Ecosystems Research",
author = "Matthias Schr{\"o}ter and Remme, {Roy P.}",
note = "This research was supported by the European Research Council, grant 263027 ({\textquoteleft}Ecospace{\textquoteright}). We thank Lars Hein and other colleagues at the Environmental Systems Analysis group for useful comments on earlier manuscript versions.",
year = "2016",
month = feb,
day = "1",
doi = "10.1007/s10980-015-0258-5",
language = "English",
volume = "31",
pages = "431--450",
journal = "Landscape Ecology",
issn = "0921-2973",
publisher = "SPB Academic Publishing",
number = "2",

}

RIS

TY - JOUR

T1 - Spatial prioritisation for conserving ecosystem services

T2 - comparing hotspots with heuristic optimisation

AU - Schröter, Matthias

AU - Remme, Roy P.

N1 - This research was supported by the European Research Council, grant 263027 (‘Ecospace’). We thank Lars Hein and other colleagues at the Environmental Systems Analysis group for useful comments on earlier manuscript versions.

PY - 2016/2/1

Y1 - 2016/2/1

N2 - Context: The variation in spatial distribution between ecosystem services can be high. Hence, there is a need to spatially identify important sites for conservation planning. The term ‘ecosystem service hotspot’ has often been used for this purpose, but definitions of this term are ambiguous. Objectives: We review and classify methods to spatially delineate hotspots. We test how spatial configuration of hotspots for a set of ecosystem services differs depending on the applied method. We compare the outcomes to a heuristic site prioritisation approach (Marxan). Methods: The four tested hotspot methods are top richest cells, spatial clustering, intensity, and richness. In a conservation scenario we set a target of conserving 10 % of the quantity of five regulating and cultural services for the forest area of Telemark county, Norway. Results: Spatial configuration of selected areas as retrieved by the four hotspots and Marxan differed considerably. Pairwise comparisons were at the lower end of the scale of the Kappa statistic (0.11–0.27). The outcomes also differed considerably in mean target achievement, cost-effectiveness in terms of land-area needed per unit target achievement and compactness in terms of edge-to-area ratio. Conclusions: An ecosystem service hotspot can refer to either areas containing high values of one service or areas with multiple services. Differences in spatial configuration among hotspot methods can lead to uncertainties for decision-making. This also has consequences for analysing the spatial co-occurrence of hotspots of multiple services and of services and biodiversity.

AB - Context: The variation in spatial distribution between ecosystem services can be high. Hence, there is a need to spatially identify important sites for conservation planning. The term ‘ecosystem service hotspot’ has often been used for this purpose, but definitions of this term are ambiguous. Objectives: We review and classify methods to spatially delineate hotspots. We test how spatial configuration of hotspots for a set of ecosystem services differs depending on the applied method. We compare the outcomes to a heuristic site prioritisation approach (Marxan). Methods: The four tested hotspot methods are top richest cells, spatial clustering, intensity, and richness. In a conservation scenario we set a target of conserving 10 % of the quantity of five regulating and cultural services for the forest area of Telemark county, Norway. Results: Spatial configuration of selected areas as retrieved by the four hotspots and Marxan differed considerably. Pairwise comparisons were at the lower end of the scale of the Kappa statistic (0.11–0.27). The outcomes also differed considerably in mean target achievement, cost-effectiveness in terms of land-area needed per unit target achievement and compactness in terms of edge-to-area ratio. Conclusions: An ecosystem service hotspot can refer to either areas containing high values of one service or areas with multiple services. Differences in spatial configuration among hotspot methods can lead to uncertainties for decision-making. This also has consequences for analysing the spatial co-occurrence of hotspots of multiple services and of services and biodiversity.

KW - Hot spot

KW - Mapping

KW - Modelling

KW - Overlap

KW - Ecosystems Research

UR - http://www.scopus.com/inward/record.url?scp=84955341398&partnerID=8YFLogxK

U2 - 10.1007/s10980-015-0258-5

DO - 10.1007/s10980-015-0258-5

M3 - Journal articles

C2 - 26843784

AN - SCOPUS:84955341398

VL - 31

SP - 431

EP - 450

JO - Landscape Ecology

JF - Landscape Ecology

SN - 0921-2973

IS - 2

ER -