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Addressing the ecological status and recovery of European water bodies, focusing on rivers, lakes, and transitional waters through common metrics and data analysis for effective management. Explore the impact of global change and disseminate findings.
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Water Bodies in Europe: Integrated Systems to assess Ecological Status and Recovery Funded under FP7, Theme 6: Environment (including Climate Change) Contract No.: 226273 www.wiser.eu ECOSTAT meeting, March 30th, 2011
1 Management, coordination and reporting Rivers Rivers 6.1 Uncertainty 5.1 Effects of management and global change 6.2 Combination of organism groups Lakes Lakes 3.1 3.2 3.3 3.4 5.2 Effects of management and global change 2.1 Data service 2.2 Review 6.3 Cross water categories comparison Coastal/trans. Coastal/trans. 4.1 4.2 4.3 4.4 6.4 Comparison of recovery processes 5.3 Effects of management and global change 7 Dissemination
Contents • Common metric update • Report “How likely is a successful intercalibration?” • Progress in other workpackages • Final conference
Contents • Common metric update • Report “How likely is a successful intercalibration?” • Progress in other workpackages • Final conference
Phytoplankton in lakes • Common metric: • Phytoplankton Taxonomic Index (PTI) • FunctionalTraits Index (FTI) • Evenness • Cyanobacterialblooms • GIGs / types: Central-Baltic, Northern, Mediterranean • Stressor: Eutrophication • Data: WISER WP3.1 database – constituted from 4 GIG datasets (CB-GIG, EC-GIG, Med-GIG and N-GIG)
Makrophytes in lakes • Common metric: • Maximum colonization depth • Taxonomic richness (total no of taxa, no of submerged taxa, no of functional groups) • No of charids and no of isoetids • Taxonomic composition metric • Ellenberg-Index • Water level fluctuations (relation of taxa sensitive and tolerant to water level fluctuations) • GIGs / types: CB-GIG, N-GIG • Stressor: Eutrophication, HyMo • Data: 16 countries, up to 2,000 lakes
Benthic invertebrates in lakes • Common metric: Multimetric Index • Number of EPTCBO taxa • ASPT • % Odonata • % ETO • % Crustacea • % habitat preference lithal • GIGs / types: CB-GIG, AL-GIG • Stressor: Eutrophication • Data: 742 sampling sites in 196 lakes
Fish in lakes • Common metric: • CPUE (number of fish caught per unit effort expressed in h.m2 of gillnets) • BPUE (biomass of fish caught per unit effort) • GIGs / types: N-GIG, CB-GIG, AL-GIG • Stressor: Eutrophication/general degradation • Data: Denmark 41, Estonia 21, Finland 77, France 27, Germany 69, Ireland 34, Italy 1, ROI/ NI 3, • Sweden 146 • Comments: Updated version with composition metrics in summer based on more data
Phytoplankton in coastal waters • Common metric: (Size spectra) • GIGs / types: Med-GIG • Stressor: Eutrophication • Data: WISER field data • Comments: No common metrics in taxonomic composition identified – impact by salinity • and temperature always larger than by • nutrients.
Macroalgae / angiosperms in TraC • Common metric: IC-Med Angiosperms • GIGs / types: Med-GIG • Stressor: Eutrophication • Data: France (PREI method) 36 sites, Spain (POMI method) 14 sites, Spain (CS method) 35 sites • Comments: Under development: - NEA macroalgae - NEA angiosperms - Baltic angiosperms - Med macroalgae
Benthic invertebrates in TraC • Common metric: „Pseudo common metric“, i.e. metrics of all other relevant methods • GIGs / types: NEA, Med, Black Sea • Stressor: Eutrophication, general degradation • Data: WISER field data • Comments: IC is mainly tried with direct comparison. Approach most likely applicable also to other GIGs.
Fish in transitional waters • Common metric: Transitional Water Fish Pseudo Common Metric • GIGs / types: NEA • Stressor: Correlation against 16 stress parameters • Data: Data from Portugal, Spain, France, Belgium, Netherland, Germany, United Kingdom, Ireland • Comments: “Pseudo common metric”; IC is mainly tried with direct comparison.
Contents • Common metric update • Report “How likely is a successful intercalibration?” • Progress in other workpackages • Final conference
Aim • Scientific advice for the ongoing intercalibration exercise • To identify BQE/water type combinations where intercalibration will be difficult • If scientific knowledge is insufficient to develop WFD compliant biological assessment methods • If assessment methods are too different to be intercalibrated
Procedure • Definition of criteria for identifying technical or scientific obstacles in intercalibration (WISER and DG Environment) • Questionnaire to relevant WISER partners • Summary by WISER coordinators
Criteria • Insufficient scientific knowledge • The national and/or common metrics used for intercalibration have a poor dose-response relationship to the relevant human pressures. • Dataset is too small at present for the application of intercalibration options; an important part of the pressure gradient is missing. • Reference sites cannot be found, and benchmark sites are hard to define. • High degree of uncertainty • Assessment systems too different • Some national methods are based on too different assessment concepts or too different sampling methods. • The relation between common metric and national methods is too low. • Other criteria • Other BQEs show stronger dose-response relationship for the same pressure AND close correlation between the BQEs.
Shortcomings • Different degrees of evidence supporting the statements • Gaps, as not all GIGs are covered by WISER work. • - EC-GIG and Med-GIG main gaps in case of lakes • - Lake phytobenthos not covered
EU = Eutrophication, HD = Habitat degradation, GD = General degradation Results for lakes no no evidence yes
EU = Eutrophication, HD = Habitat degradation, GD = General degradation Results for transitional waters A M M no no evidence yes
EU = Eutrophication, HD = Habitat degradation, GD = General degradation Results for coastal waters no no evidence yes
Conclusions • No or only few obstacles for intercalibration: • Lake phytoplankton (N-GIG, CB-GIG, AL-GIG; EU) • Lake macrophytes (N-GIG, CB-GIG, Med-GIG, AL-GIG, EU/OP, HD) • Coastal water angiosperms (Mediterranean) • Coastal benthic invertebrates (NEA) • Transitional waters macroflora (Mediterranean) • Mixed picture: • Lake phytoplankton (Med-GIG, EC-GIG; EU) • Lake benthic invertebrates (N-GIG, CB-GIG, AL-GIG; EU/OP, HD) • Lake fish (N-GIG, CB-GIG, AL-GIG) • Transitional waters benthic invertebrates (all GIGs) • Transitional waters fish (NEA, Baltic) • Significant obstacles: • Lake fish (Mediterranean, EU/OP, GD) • Coastal water phytoplankton (Baltic, NEA, Black Sea) • Coastal angiosperms and macroalgae (Black Sea) • Transitional waters angiosperms (NEA) • Transitional waters macroalgae (NEA)
Conclusions II • Cases not covered by WISER: IC likely not to be finalized in 2011; scientific obstacles can not be judged by WISER.
Possible next steps • Filling the gaps, e.g. by contacting selected GIG coordinators • Validating the results, e.g. together with the GIG coordinators
Contents • Common metric update • Report “How likely is a successful intercalibration?” • Progress in other workpackages • Final conference
Uncertainty exercise • Lake phytoplankton May 2011 • Lake macrophytes April 2011 • Lake invertebrates Summer 2011 • Lake fish Summer 2011 • TraC phytoplankton Summer 2011 • TraC macroflora April to July 2011 • TraC invertebrates July 2011 • TraC fish May 2011
Contents • Common metric update • Report “How likely is a successful intercalibration?” • Progress in other workpackages • Final conference
WISER final conference • Aims: • To inform about the outcome of intercalibration • To inform about the status of assessment systems • To discuss experiences and strategies for restoration • To discuss the next steps of WFD implementation • Target group: • Environmental administration • River basin districts • Decision makers for future monitoring systems and river basin management plans
WISER final conference: Arrangements • 25-26/1/2012 • Costs: ~ 300 € (incl. accommodation, meals, conference fees) • http://www.wiser.eu/news/final_conference
WISER final conference, Day I • Overview of research needs after the end of WISER • Summary of ten years of intercalibration • State of the art assessment methods for lakes • State of the art assessment methods for TraC • Uncertainty in bioassessment • Combination of BQEs • Experiences from RBMPs • Future perspective of ecosystem assessment • Relation of WFD to other (marine) directives • Comparative analysis of BQEs and ecosystem types
WISER final conference, Day II • Assessment/restoration in the US • State of the art in river restoration • State of the art lake restoration • State of the art coastal restoration • Comparing restoration success of different ecosystem types • Specific restoration case studies in light of changes in land use and climate