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Presented by Sandra Poikane EC Joint Research Centre Institute for Environment and Sustainability Biological indicators of lakes and rivers and the Intercalibration.

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Presentation on theme: "Presented by Sandra Poikane EC Joint Research Centre Institute for Environment and Sustainability Biological indicators of lakes and rivers and the Intercalibration."— Presentation transcript:

1 Presented by Sandra Poikane EC Joint Research Centre Institute for Environment and Sustainability Biological indicators of lakes and rivers and the Intercalibration

2 the questions to answer :  Which metrics to measure ?  Which are the best quality elements/indicators to assess each pressure?  and for each type ?  Overview on IC results

3 Information utilisation Water management Laboratory analysis Data handling Data analysis Assessment and reporting Information needs Sample collection Assessment strategy Monitoring programme Water Management cycle

4 Succesive steps should be designed based on required information product

5 Information utilisation Water management Laboratory analysis Data handling Data analysis Assessment and reporting Information needs Sample collection Assessment strategy Monitoring programme Water Management cycle (UN ECE, 2000)

6 Biological Quality Element: Phytoplankton Abundance and species composition MONITORING How to measure ? : Abundance Chlorophyll a Biomass mg/l Cell counts number/ml When ? Where ? ASSESSMENT How to assess ? Abundance Chlorophyll a Biomass mg/l - Cell counts number/ml

7 How to measure phytoplankton ?

8 Phytoplankton – abundance Chlorophyll a concentration (average growth season):  Relevant and reliable an effective indicator of trophic status  Easy to measure and not too costly to measure  Most of MS have WFD compliant assessment systems based on chl

9 Chlorophyll a: - success story of IC exercise - 5 GIGs incl 28 MS and 14 types have set chl boundaries

10 Phytoplankton – abundance  Phytoplankton biomass – can be used as measure of phytoplankton  Alpine GIG has developed boundaries using phytoplankton biomass

11 Phytoplankton – species composition – different approaches  some – AT, DE - have developed phytoplankton indices based on total biovolume and indicator species;  several countries are descriptors like biomass and % of of main groups (BE, NO, DE)  UK and HU have developed classification tools based on phytoplankton functional groups

12 Phytoplankton – species composition  Another reliable, meaningful and easy-to-use indicator is the contribution of Cyanobacteria to the total biomass of phytoplankton (and the biomass of Cyanobacteria).  an indicator of eutrophication;  serious water quality and animal and human health problems;  Most of the MS (for example, Belgium, Germany, Estonia, France, Netherlands, UK, Hungary, Lithuania) use the proportion of Cyanobacteria in their assessment systems

13 Phytoplankton  Eutrophication  All lake types  Seasonal succession  Interaction with macrophytes  Frequency – 6 months ?

14 Macrophyte vegetation  Depth limit or maximal macrophyte colonization depth is –an important characteristic of lake –of particular importance in connection with lake eutrophication

15 Macrophyte vegetation  Macrophyte coverage can be used for the assessment of the status of lakes,  it will depend on macrophyte survey approach and method  % of lake area, describing all vegetation zones

16 Macrophyte vegetation  Other potential indicators of the state of lake are the abundance of sensitive (for example, Chara sp for hard-water lakes and Isoetes sp for soft-water lakes) and impacted state taxa  Assessment methods under development  Alpine GIG (AT, DE) and Atlantic GIG (UK, IE) – results in 2006

17 Benthic fauna  Only Nordic GIGs and 3 countries have decided to start the Intercalibration exercise of benthic fauna assessment methods;  Benthic fauna assessment methods are used only for evaluation of acidification pressure;  Metrics used – Raddum and NIVA acidification indices (NO), MILA multimetric index (SE), Medin index (UK)  Based on proportion on sensitive/tolerant taxa

18 Benthic fauna  Other countries – complaining about the lack of data, impossible to carry out intercalibration  Hope that monitoring will provide the data for the development of assessment methods  Communication between monitoring and Intercalibration necessary !

19 Fish fauna  No information about WFD compliant assessment methods  Norway, Sweden – in development  Acidification, eutrophication, habitat changes  Based on sensitive and tolerant species  Again – hope monitoring will provide necessary data

20 Rivers – benthic fauna  All MS have well-established assessment methods  For example –Multi-metric Indices for General Degradation (AT); –Multi-metric Index Flanders (BE-F); –Saprobic Index (AT, RO, SL); –IBGN (FR, BE-W, L); – IBE – Extended Biotic Index (IT); –RIVPACS (UK); –various modifications of BMWP (ES, HU, PL, PT);

21 Rivers – benthic fauna  abundance of macroinvertebrate taxa, family or species level  multihabitat sampling using agreed standards  allows to calculate a variety of indicators  assessment results can be compared using ICMi – Intercalibration Common Metrics  can be used for organic matter, nutrients, hydromorphological pressure, acidification

22 Summary on benthic fauna  MS keep their traditional methods  Intercalibration through ICM enables harmonization of boundaries  Benthic fauna – the key biological element of rivers answering all pressures

23 Rivers – benthic algae  A lot of work going on :  For example: –Austrian Assessment Method for Phytobenthos; MAFWAT (BE-F); IPS (ES, BE-W); –Trophic index, saprobic index and some additional metrics based on reference conditions (AT); IBD – for diatoms (FR); –DARES - for diatoms (IE, UK); –Diatoms multimetric composed by 7 metrics (ES); –EPI – for diatoms only (IT); – Simple 4-abundance level scheme – for filamentous algae (IE); – for phytobenthos without diatoms – reference Index (DE); –IPS/PSI (L).

24 Rivers – benthic algae  current focus on diatoms  CEN standards existing for sampling and handling  Organic matter, nutrients  Other taxonomic groups could be included, but methods need to be developed  Central and Alpine GIG have started IC on diatom methods

25 Rivers – fish fauna  AT, UK, SW have developed methods, some countries are working: –Austrian Multi-metric Index for fish assessment (AT); –EFI (LT, UK); –IBI fish index (BE-F); –IP-Indice Poisson (FR); FAME (ES); Fish Q- value (IE); SEPA methods (SW).

26 Rivers - fish  electrofishing  species composition and age distribution  hydromorphological pressure (especially river continuity), but also other pressures  No IC in this round  Lack of data in many countries

27 Rivers - macrophytes  in development  organic matter, nutrients, hydromorphological pressure  especially applicable in large rivers  Start of IC in Central GIG (AT and FR have developed their assessment methods)

28 RIVERS - IC  Result of the first Intercalibration exercise will be boundary setting for macroinvertebrates for all GIGs;  Alpine and Central/ Baltic GIGs plan to come up with boundary setting for phytobenthos/ diatoms QE;

29 Conclusions - 1  Link between monitoring program and assessment systems : 1. Assessment systems in place  Lakes - Chlorophyll concentration, Some metrics for phytoplankton and macrophyte vegetation  Rivers - Benthic fauna, Diatoms  Monitoring provide appropriate data for assessment

30 Conclusions - 2 2. National assessment methods are often still under development  Lakes – benthic fauna, fish, rivers – macrophytes, fish  Monitoring will provide data for development of assessment systems

31 Conclusions - 3  Isn’t the Water Framework Directive a wonderful piece of legislation?


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