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Wetland loss through drainage LB-2

Loss of Biodiversity Pressure

1 Indicator definition and unit of measurement
Loss of wetland area. . Unit of Measurement is percentage of wetland area lost with reference to an appropriate baseline year (e.g. “Ramsar” year 1971).
2 Placement in the framework
5EAP:
Chapter 5: The themes and targets of the programme, section 5.3: Protection of nature and bio-diversity and section 5.4: Management of water resources.
Agenda 21:
Chapter 15: Conservation of biological diversity, section 15.5 (g) calls for “ in situ measures to embrace vulnerable freshwater and other wetland ecosystems”.
Chapter 18: Protection of the quality and supply of freshwater resources: application of integrated approaches to the development, management and use of water resources, section 18.40 e) iii) calls for the “conservation and protection of wetlands”.
International conventions and agreements:
Ramsar convention on wetlands of international importance (2nd February 1971).
EU directive 79/409 on conservation of wild birds (Berne convention, 2nd April 1979).
EU directive 92/43 on conservation of natural habitats and of wild fauna and flora (May 1992).
Ranking:
Core ranking: 2 (52%)
Policy Relevance: 3 (3.1)
Analytical Soundness: 1 (3.4)
Responsiveness: 6 (2.6)
Most appropriate related state indicators:
Wetland extent (ha).
3 Significance
Purpose:
Wetlands are a very appropriate indicator of environmental quality both for biodiversity and water resources and for this reason they have frequently been proposed as pressure indicators.
Relevance:
There is considerable variation in the degree of importance attached, historically and more recently, to the preservation of wetland areas: regional variations are notable, with northern European countries now becoming highly sensitised to wetland protection (and restoration) issues. This may be a reflection of the smaller wetland area remaining in the north compared to southern regions.
Linkages to other pressure indicators:
In the Loss of Biodiversity policy field, LB-3: Agricultural intensity; LB-6: Change in traditional land use practices.
In Marine Environment & Coastal Zones, ME-8: Wetland loss.
In Resource Depletion, RD-1: Water consumption per capita.
In Urban Environmental Problems, UP-6: Land consumption, change from natural to built up area.
Targets:
Natura 2000 network of SPAs/SACs.
Agenda 21: Restoration of x km 2.
5EAP: No further deterioration in protected areas.
4 Methodological description and underlying definitions
Underlying definitions and concepts:
Historically, wetland habitats have been under pressure through drainage for agriculture and other land use purposes. Their important role in water resource management as well as biodiversity conservation is now recognised.
Measurement methods:
Standardisation is required to monitor wetland extent and there are difficulties in defining the boundaries of (current and historic) wetlands. An index of wetland quality is important, e.g. in relation to the degree of importance for migratory birds. The proposed European Inventory of Wetlands (Montecatini meeting) is urgently needed and should gather data on wetland extent and losses due to all identifiable human pressures.
Limitations of the indicator:
(i) There is insufficient data, even for the extent of existing wetlands, for many countries.
(ii) The indicator provides no indication of wetland quality and hence actual or potential biodiversity.
(iii) The "area" indicator subsumes pressures/cumulative impacts on wetland function.
(iv) It is difficult to incorporate the range of wetland types.
Alternative definitions:
The indicator could be disaggregated by sector e.g.: forestry or agriculture, tourism, energy, transport, waste.





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