COMMISSION DECISION (EU) 2024/721
of 27 February 2024
establishing, pursuant to Directive 2000/60/EC of the European Parliament and of the Council, the values of the Member State monitoring system classifications as a result of the intercalibration exercise and repealing Commission Decision (EU) 2018/229
(notified under document C(2024) 1113)
(Text with EEA relevance)
Article 1
Article 2
Article 3
ANNEX 1
Part 1
Water category |
Rivers |
Geographical Intercalibration Group |
Alpine rivers |
Description of types that have been intercalibrated
Type |
River characterisation |
Catchment (km2) |
Altitude (m a.s.l.) and geomorphology |
Alkalinity |
Flow regime |
R-A1 |
Pre-Alpine, small to medium, high altitude calcareous |
10 – 1 000 |
800 – 2 500 m (catchment), boulders/cobble |
High (but not extremely high) alkalinity |
|
R-A2 |
Small to medium, high altitude, siliceous |
10 – 1 000 |
500 – 1 000 m (max. altitude of catchment 3 000 m, mean 1 500 m), boulders |
Non-calcareous (granite, metamorphic) medium to low alkalinity |
Nival-glacial flow regime |
ALPINE RIVERS GEOGRAPHICAL INTERCALIBRATION GROUP RESULTS |
|
Biological Quality Element |
Benthic invertebrate fauna |
Country and Type |
National classification systems intercalibrated |
Ecological Quality Ratios |
|
High-Good boundary |
Good-Moderate boundary |
||
Type R-A1 |
|
|
|
Austria |
Assessment of the biological quality elements – part benthic invertebrates [Erhebung der biologischen Qualitätselemente – Teil Makrozoobenthos (Detaillierte MZB-Methode)] |
0,80 |
0,60 |
France |
Multimetric index based on macroinvertebrate fauna for the ecological assessment of French wadeable rivers (I2M2) |
0,605 |
0,354 |
Germany |
PERLODES – Bewertungsverfahren von Fließgewässern auf Basis des Makrozoobenthos |
0,80 |
0,60 |
Italy |
MacrOper, based on STAR Intercalibration Common Metric Index (STAR_ICMi) |
0,97 |
0,73 |
Slovenia |
Metodologija vrednotenja ekološkega stanja vodotokov na podlagi bentoških nevretenčarjev |
0,80 |
0,60 |
Type R-A2 |
|
|
|
Austria |
Assessment of the biological quality elements – part benthic invertebrates [Erhebung der biologischen Qualitätselemente – Teil Makrozoobenthos (Detaillierte MZB-Methode)] |
0,80 |
0,60 |
France |
Multimetric index based on macroinvertebrate fauna for the ecological assessment of French wadeable rivers (I2M2) |
0,665 |
0,460 |
Italy |
MacrOper, based on STAR Intercalibration Common Metric Index (STAR_ICMi) |
0,95 |
0,71 |
Spain |
Iberian BMWP (IBMWP) |
0,83 |
0,53 |
ALPINE RIVERS GEOGRAPHICAL INTERCALIBRATION GROUP RESULTS |
|
Biological Quality Element |
Macrophytes and Phytobenthos |
Sub-Biological Quality Element |
Phytobenthos |
Type and country |
National classification systems intercalibrated |
Ecological Quality Ratios |
|
High-Good boundary |
Good-Moderate boundary |
||
Type R-A1 |
|
|
|
Austria |
Assessment of the biological quality elements – part phytobenthos [Leitfaden zur Erhebung der biologischen Qualitätselemente, Teil A3 – Fließgewässer/Phytobenthos] |
0,89 |
0,71 |
France |
IBD 2007 (Coste et al, Ecol. Ind. 2009). AFNOR NF-T-90-354, December 2007. Arrêté ministériel du 25 janvier 2010 modifié relatif aux méthodes et critères d’évaluation de l’état écologique {...} des eaux de surface |
0,94 |
0,78 |
Germany |
Verfahrensanleitung für die ökologische Bewertung von Fließgewässern zur Umsetzung der EG-Wasserrahmenrichtlinie: Makrophyten und Phytobenthos (PHYLIB), Modul Diatomeen |
0,735 |
0,54 |
Italy |
Intercalibration Common Metric Index (ICMi) (Mancini & Sollazzo, 2009) |
0,87 |
0,70 |
Slovenia |
Metodologija vrednotenja ekološkega stanja vodotokov na podlagi fitobentosa in makrofitov, fitobentos |
0,80 |
0,60 |
Type R-A2 |
|
|
|
Austria |
Assessment of the biological quality elements – part phytobenthos [Leitfaden zur Erhebung der biologischen Qualitätselemente, Teil A3 – Fließgewässer/Phytobenthos] |
0,89 |
0,71 |
France |
IBD 2007 (Coste et al, Ecol. Ind. 2009). AFNOR NF-T-90-354, December 2007. Arrêté ministériel du 25 janvier 2010 modifié relatif aux méthodes et critères d’évaluation de l’état écologique {...} des eaux de surface |
0,94 |
0,78 |
Spain |
IPS (Coste in Cemagref, 1982) |
0,94 |
0,74 |
Italy |
Intercalibration Common Metric Index (ICMi) (Mancini & Sollazzo, 2009) |
0,85 |
0,64 |
Water category |
Rivers |
Geographical Intercalibration Group |
Central-Baltic rivers |
Description of types that have been intercalibrated
Type |
River characterisation |
Catchment (km2) |
Altitude and geomorphology |
Alkalinity (meq/l) |
R-C1 |
Small lowland siliceous sand |
10 – 100 |
Lowland, dominated by sandy substrate (small particle size), 3 – 8 m width (bankfull size) |
> 0,4 |
R-C2 |
Small lowland siliceous – rock |
10 – 100 |
Lowland, rock material 3 – 8m width (bankfull size) |
< 0,4 |
R-C3 |
Small mid-altitude siliceous |
10 – 100 |
Mid-altitude, rock (granite) – gravel substrate, 2 – 10 m width (bankfull size) |
< 0,4 |
R-C4 |
Medium lowland mixed |
100 – 1 000 |
Lowland, sandy to gravel substrate, 8 – 25 m width (bankfull size) |
> 0,4 |
R-C5 |
Large lowland mixed |
1 000 – 10 000 |
Lowland, barbel zone, variation in velocity, max. altitude in catchment: 800 m a.s.l., > 25 m width (bankfull size) |
> 0,4 |
R-C6 |
Small, lowland, calcareous |
10 – 300 |
Lowland, gravel substrate (limestone), width 3 – 10 m (bankfull size) |
> 2 |
CENTRAL-BALTIC RIVERS GEOGRAPHICAL INTERCALIBRATION GROUP RESULTS |
|
Biological Quality Element |
Benthic invertebrate fauna |
Country |
National classification systems intercalibrated |
Ecological Quality Ratios |
|
High-Good boundary |
Good-Moderate boundary |
||
Austria |
Assessment of the biological quality elements – part benthic invertebrates |
0,80 |
0,60 |
Belgium (Flanders) |
Multimetric Macroinvertebrate Index Flanders (MMIF) |
0,90 |
0,70 |
Belgium (Wallonia) |
Indice Biologique Global Normalisé (IBGN) (Norme AFNOR NF T 90 350, 1992) and Arrêté du Gouvernement wallon du 13 septembre 2012 relatif à l’identification, à la caractérisation et à la fixation des seuils d’état écologique applicables aux masses d’eau de surface et modifiant le Livre II du Code de l’Environnement, contenant le Code de l’Eau. Moniteur belge 12.10.2012 |
0,94 (type R-C1) 0,97 (types R-C3, R-C5, R-C6) |
0,75 (type R-C1) 0,74 (types R-C3, R-C5, R-C6) |
Czechia |
Czech system for ecological status assessment of rivers using benthic macroinvertebrates |
0,80 |
0,60 |
Denmark |
Danish Stream Fauna Index (DSFI) |
1,00 |
0,71 |
Estonia |
Estonian surface water ecological quality assessment – river macroinvertebrates |
0,90 |
0,70 |
France |
Multimetric index based on macroinvertebrate fauna for the ecological assessment of French wadeable rivers (I2M2) |
0,665 |
0,443 |
Germany |
PERLODES – Bewertungsverfahren von Fließgewässern auf Basis des Makrozoobenthos |
0,80 |
0,60 |
Ireland |
Quality Rating System (Q-value) |
0,85 |
0,75 |
Italy |
MacrOper, based on STAR_ICM index calculation |
0,96 |
0,72 |
Latvia |
Latvian Macroinvertebrate Index (LMI) |
0,92 |
0,72 |
Lithuania |
Lithuanian River Macroinvertebrate Index |
0,80 |
0,60 |
Luxembourg |
Macroinvertebrate-based Multimetric Index (I2M2) |
0,64 |
0,45 |
Netherlands |
KRW-maatlat |
0,80 |
0,60 |
Poland |
RIVECOmacro – MMI_PL |
0,91 (type R-C1) |
0,72 (type R-C1) |
Spain |
METI |
0,93 |
0,70 |
Spain (Basque country) |
MBf (Multimetric Basque index family level) |
0,91 |
0,68 |
Sweden |
DJ-index (Dahl & Johnson 2004) |
0,80 |
0,60 |
CENTRAL-BALTIC RIVERS GEOGRAPHICAL INTERCALIBRATION GROUP RESULTS |
|
Biological Quality Element |
Macrophytes and Phytobenthos |
Sub-Biological Quality Element |
Macrophytes |
Country |
National classification systems intercalibrated |
Type |
Ecological Quality Ratios |
|
High-Good boundary |
Good-Moderate boundary |
|||
Austria |
AIM for Rivers (Austrian Index Macrophytes for rivers) |
RC-3 |
0,875 |
0,625 |
Belgium (Flanders) |
MAFWAT – Flemish macrophyte assessment system |
R-C1 |
0,80 |
0,60 |
Belgium (Wallonia) |
IBMR-WL – Biological Macrophyte Index for Rivers (Arrêté du Gouvernement wallon du 13 septembre 2012 relatif à l’identification, à la caractérisation et à la fixation des seuils d’état écologique applicables aux masses d’eau de surface et modifiant le Livre II du Code de l’Environnement, contenant le Code de l’Eau. Moniteur belge 12.10.2012) |
R-C3 |
0,925 |
0,607 |
Czechia |
Assessment method of surface running water bodies in Czechia using biological quality element macrophytes |
R-C3 (national type 1) |
0,83 |
0,67 |
R-C3 (national type 4) |
0,82 |
0,64 |
||
R-C4 |
0,86 |
0,62 |
||
Denmark |
DSPI – Danish Stream Plant Index |
R-C1, R-C4 |
0,70 |
0,50 |
Estonia |
Estonian Macrophyte Index for Rivers |
R-C4 |
0,85 |
0,65 |
Germany |
Verfahrensanleitung für die ökologische Bewertung von Fließgewässern zur Umsetzung der EG-Wasserrahmenrichtlinie: Makrophyten und Phytobenthos (PHYLIB), Modul Makrophyten |
R-C1 |
0,745 |
0,495 |
R-C3 |
0,80 |
0,55 |
||
R-C4 |
0,575 |
0,395 |
||
Germany |
NRW-Verfahren zur Bewertung von Fließgewässern mit Makrophyten |
R-C1, R-C3, R-C4 |
0,995 |
0,695 |
France |
IBMR – Indice Biologique Macrophytique en Rivière French standard NF T90-395 (2003-10-01) |
R-C3 |
0,93 |
0,79 |
R-C4 |
0,905 |
0,79 |
||
Ireland |
MTR – IE – Mean Trophic Ranking |
R-C4 |
0,74 |
0,62 |
Italy |
IBMR – IT – Biological Macrophyte Index for Rivers |
R-C1 |
0,90 |
0,80 |
R-C4 |
0,90 |
0,80 |
||
Lithuania |
Lithuanian River Macrophyte Index |
R-C4 |
0,61 |
0,41 |
Latvia |
Latvian assessment method using macrophytes |
R-C4 |
0,75 |
0,55 |
Luxembourg |
IBMR – LU – Biological Macrophyte Index for Rivers |
R-C3, R-C4, R-C5 and R-C6 |
0,89 |
0,79 |
Netherlands |
Revised assessment method for rivers in The Netherlands using macrophytes |
R-C1 and R-C4 |
0,80 |
0,60 |
Poland |
MIR – Macrophyte Index for Rivers |
R-C1 |
0,90 |
0,65 |
R-C3 |
0,910 |
0,684 |
||
R-C4 |
0,90 |
0,65 |
CENTRAL-BALTIC RIVERS GEOGRAPHICAL INTERCALIBRATION GROUP RESULTS |
|
Biological Quality Element |
Macrophytes and Phytobenthos |
Sub-Biological Quality Element |
Phytobenthos |
Country |
National classification systems intercalibrated |
Type |
Ecological Quality Ratios |
|
High-Good boundary |
Good-Moderate boundary |
|||
Austria |
Assessment of the biological quality elements – part Phytobenthos [Leitfaden zur Erhebung der biologischen Qualitätselemente, Teil A3 -Fließgewässer/Phytobenthos] |
All types, altitude < 500 m |
0,64 |
0,49 |
All types, altitude > 500 m |
0,81 |
0,53 |
||
Belgium (Flanders) |
Proportions of Impact-Sensitive and Impact-Associated Diatoms (PISIAD) |
All types |
0,80 |
0,60 |
Belgium (Wallonia) |
IPS (Coste, in CEMAGREF, 1982; Lenoir & Coste, 1996 and Arrêté du Gouvernement wallon du 13 septembre 2012 relatif à l’identification, à la caractérisation et à la fixation des seuils d’état écologique applicables aux masses d’eau de surface et modifiant le Livre II du Code de l’Environnement, contenant le Code de l’Eau. Moniteur belge 12.10.2012) |
All types |
0,98 |
0,73 |
Czechia |
Czech assessment method for rivers using phytobenthos |
R-C3, R-C4, R-C5 |
0,80 |
0,63 |
Denmark |
Danish index for benthic algae (SID_TID) |
R-C1, R-C4, R-C6 |
0,861 |
0,68 |
Estonia |
Indice de Polluosensibilité Spécifique (IPS) |
All types |
0,85 |
0,70 |
France |
IBD 2007 (Coste et al, Ecol. Ind. 2009). AFNOR NF-T-90-354, December 2007. Arrêté ministériel du 25 janvier 2010 modifié relatif aux méthodes et critères d’évaluation de l’état écologique {...} des eaux de surface |
All types |
0,94 |
0,78 |
Germany |
Verfahrensanleitung für die ökologische Bewertung von Fließgewässern zur Umsetzung der EG-Wasserrahmenrichtlinie: Makrophyten und Phytobenthos (PHYLIB), Modul Diatomeen |
R-C1 |
0,67 |
0,43 |
R-C3 |
0,67 |
0,43 |
||
R-C4 |
0,61 |
0,43 |
||
R-C5 |
0,73 |
0,55 |
||
Ireland |
Revised form of Trophic Diatom Index (TDI) |
All types |
0,93 |
0,78 |
Italy |
Intercalibration Common Metric Index (ICMi) (Mancini & Sollazzo, 2009) |
All types |
0,89 |
0,70 |
Ireland |
Revised form of Trophic Diatom Index (TDI) |
All types |
0,93 |
0,78 |
Latvia |
Latvian assessment method using phytobenthos |
R-C4, R-C5, R-C6 |
0,70 |
0,50 |
Lithuania |
Lithuanian River Phytobenthos Index |
R-C1, R-C4, R-C5, R-C6 |
0,73 |
0,55 |
Luxembourg |
Indice de Polluosensibilité Spécifique (IPS) |
R-C3, R-C4 (low alkalinity) |
0,98 |
0,78 |
R-C4 (high alkalinity), R-C5 and R-C6 |
0,99 |
0,78 |
||
Netherlands |
KRW Maatlat |
All types |
0,80 |
0,60 |
Poland |
Indeks Okrzemkowy IO dla rzek (Diatom Index for rivers) |
All types |
0,80 |
0,58 |
Spain |
Diatom multimetric (MDIAT) |
R-C2, R-C3, R-C4 |
0,93 |
0,70 |
Sweden |
Swedish assessment methods, Swedish EPA regulations (NFS 2008:1) based on Indice de Polluosensibilité Spécifique (IPS) |
All types |
0,89 |
0,74 |
Water category |
Rivers |
Geographical Intercalibration Group |
Eastern Continental rivers |
Description of types that have been intercalibrated
Type |
River characterisation |
Ecoregion |
Catchment (km2) |
Altitude (m a.s.l.) |
Geology |
Substrate |
R-E1a |
Carpathians: small to medium, mid-altitude |
10 |
10 – 1 000 |
500 – 800 |
Mixed |
|
R-E1b |
Carpathians: small to medium, mid-altitude |
10 |
10 – 1 000 |
200 – 500 |
Mixed |
|
R-E2 |
Plains: medium-sized, lowland |
11 and 12 |
100 – 1 000 |
< 200 |
Mixed |
Sand and silt |
R-E3 |
Plains: large, lowland |
11 and 12 |
> 1 000 |
< 200 |
Mixed |
Sand, silt and gravel |
R-E4 |
Plains: medium-sized, mid-altitude |
11 and 12 |
100 – 1 000 |
200 – 500 |
Mixed |
Sand and gravel |
R-EX4 |
Large, mid-altitude |
10 , 11 and 12 |
> 1 000 |
200 – 500 |
Mixed |
Gravel and boulder |
R-EX5 |
Plains: small lowland |
11 and 12 |
10 – 100 |
< 200 |
Mixed |
Sand and silt |
R-EX6 |
Plains: small, mid-altitude |
11 and 12 |
10 – 100 |
200 – 500 |
Mixed |
Gravel |
R-EX7 |
Balkan: small, calcareous, mid-altitude |
5 |
10 – 100 |
200 – 500 |
Calcareous |
Gravel |
R-EX8 |
Balkan: small to medium-sized, calcareous karst spring |
5 |
10 – 1 000 |
|
Calcareous |
Gravel, sand and silt |
EASTERN CONTINENTAL RIVERS GEOGRAPHICAL INTERCALIBRATION GROUP RESULTS |
|
Biological Quality Element |
Benthic invertebrate fauna |
Country |
National classification systems intercalibrated |
Type |
Ecological Quality Ratios |
|
High-Good boundary |
Good-Moderate boundary |
|||
Austria |
Assessment of the biological quality elements – part benthic invertebrates |
R-E4 |
0,80 |
0,60 |
Bulgaria |
IBI (BG) (Irish Biotic Index (BG)) |
R-E1a, R-E1b |
0,86 |
0,67 |
R-E2, R-E3 |
0,80 |
0,60 |
||
Croatia |
Croatian classification method for benthic macroinvertebrates |
R-E2, R-E3, R-EX5, R-EX6 |
0,80 |
0,60 |
Czechia |
Czech system for ecological status assessment of rivers using benthic macroinvertebrates |
R-E1a, R-E1b, R-E2, R-E3 |
0,80 |
0,60 |
Hungary |
Hungarian Multimetric Macroinvertebrate Index |
R-E1b, R-E3, R-E4, R-EX5, R-EX6 |
0,80 |
0,60 |
Romania |
Assessment method for ecological status of water bodies based on macroinvertebrates |
R-E1a, R-E1b, R-E3, R-EX4 |
0,80 |
0,60 |
Slovenia |
Metodologija vrednotenja ekološkega stanja vodotokov na podlagi bentoških nevretenčarjev |
R-E4, R-EX5, R-EX6 |
0,80 |
0,60 |
Slovakia |
Slovak assessment of benthic invertebrates in rivers |
R-E1a, R-E1b, R-E2, R-E3, R-E4, R-EX4 |
0,80 |
0,60 |
EASTERN CONTINENTAL RIVERS GEOGRAPHICAL INTERCALIBRATION GROUP RESULTS |
|
Biological Quality Element |
Macrophytes and Phytobenthos |
Sub-Biological Quality Element |
Macrophytes |
Country |
National classification systems intercalibrated |
Type |
Ecological Quality Ratios |
|
High-Good boundary |
Good-Moderate boundary |
|||
Austria |
AIM for Rivers (Austrian Index Macrophytes for rivers) |
R-E4 |
0,875 |
0,625 |
Bulgaria |
Reference Index |
R-E2, R-E3 |
0,570 |
0,370 |
R-E4 |
0,510 |
0,270 |
||
Croatia |
Croatian classification method for macrophytes in rivers |
R-E2, R-E3 |
0,800 |
0,600 |
Czechia |
Assessment method of surface running water bodies in Czechia using biological quality element macrophytes |
R-E2, R-E3 |
0,750 |
0,500 |
Czechia |
Assessment method of surface running water bodies in Czechia using biological quality element macrophytes |
R-E4 |
0,770 |
0,560 |
Hungary |
Reference Index |
R-E2, R-E3 |
0,700 |
0,370 |
Romania |
Romanian Macrophyte-based assessment system for rivers (Macrophyte River Index (MARI)) |
R-E2, R-E3, R-E4 |
R-E2 and R-E3: 0,875 , R-E4: 0,783 |
all types: 0,625 |
Slovenia |
Metodologija vrednotenja ekološkega stanja vodotokov na podlagi fitobentosa in makrofitov, makrofiti |
R-E2, R-E3, R-E4 |
0,800 |
0,600 |
Slovakia |
Macrophyte Biological Index for Rivers (IBMR-SK) |
R-E2, R-E3, R-E4 |
0,800 |
0,600 |
EASTERN CONTINENTAL RIVERS GEOGRAPHICAL INTERCALIBRATION GROUP RESULTS |
|
Biological Quality Element |
Macrophytes and Phytobenthos |
Sub-Biological Quality Element |
Phytobenthos |
Country |
National classification systems intercalibrated |
Type |
Ecological Quality Ratios |
|
High-Good boundary |
Good-Moderate boundary |
|||
Austria |
Assessment of the biological quality elements – part Phytobenthos [Leitfaden zur Erhebung der biologischen Qualitätselemente, Teil A3 – Fließgewässer/Phytobenthos] |
R-E4 |
0,64 |
0,49 |
Bulgaria |
Ecological status assessment of rivers in Bulgaria based on IPS diatom index |
R-E1a, R-E1b, R-E3 |
0,87 (national type R2, R4) 0,85 (national type R7, R8) |
0,66 (national type R2, R4) 0,64 (national type R7, R8) |
Croatia |
Croatian classification method for phytobenthos in rivers |
R-E2, R-E3, R-EX5, R-EX6, R-EX7, R-EX8 |
0,862 |
0,60 |
Czechia |
Assessment system for rivers using phytobenthos |
R-E1a, R-E1b, R-E2, R-E3, R-EX4 |
0,80 |
0,60 |
Hungary |
Ecological status assessment for rivers based on diatoms |
R-E1b, R-E2, R-E3, R-EX5 |
0,80 |
0,60 |
Romania |
National (Romanian) Assessment Method for Rivers Ecological Status based on Phytobenthos (Diatoms) RO-AMRP |
R-E1a, R-E1b, R-E3 |
0,80 |
0,60 |
Slovenia |
Metodologija vrednotenja ekološkega stanja vodotokov na podlagi fitobentosa in makrofitov, fitobentos |
R-E4, R-EX5, R-EX6, R-EX7, R-EX8 |
0,80 |
0,60 |
Slovakia |
Ecological status assessment system for rivers using phytobenthos |
R-E1a, R-E1b, R-E2, R-E3, R-E4, R-EX4 |
0,90 |
0,70 |
Water category |
Rivers |
Geographical Intercalibration Group |
Mediterranean rivers |
Description of types that have been intercalibrated
Type |
River characterisation |
Catchment (km2) |
Geology |
Flow regime |
R-M1 |
Small Mediterranean streams |
< 100 |
Mixed (except siliceous) |
Highly seasonal |
R-M2 |
Medium Mediterranean streams |
100 – 1 000 |
Mixed (except siliceous) |
Highly seasonal |
R-M4 |
Mediterranean mountain streams |
|
Non-siliceous |
Highly seasonal |
R-M5 |
Temporary streams |
|
|
Temporary |
MEDITERRANEAN RIVERS GEOGRAPHICAL INTERCALIBRATION GROUP RESULTS |
|
Biological Quality Element |
Benthic invertebrate fauna |
Type and Country |
National classification systems intercalibrated |
Ecological Quality Ratios |
|
High-Good boundary |
Good-Moderate boundary |
||
R-M1 |
|
|
|
Croatia |
Croatian classification method for benthic macroinvertebrates |
0,800 |
0,600 |
France |
Multimetric index based on macroinvertebrate fauna for the ecological assessment of French wadeable rivers (I2M2) |
0,676 |
0,464 |
Greece |
Hellenic Evaluation System-2 (HESY-2) |
0,943 |
0,750 |
Italy |
MacrOper (based on STAR Intercalibration Common Metric Index ICMi) |
0,970 |
0,720 |
Portugal |
Rivers Biological Quality Assessment Method-Benthic Invertebrates (IPtIN, IPtIS) |
0,870 (type 1) |
0,678 (type 1) |
0,850 (type 3) |
0,686 (type 3) |
||
Slovenia |
Metodologija vrednotenja ekološkega stanja vodotokov na podlagi bentoških nevretenčarjev |
0,800 |
0,600 |
Spain |
Iberian Biological Monitoring Working Party (IBMWP) |
0,845 |
0,698 |
Spain |
Iberian Mediterranean Multimetric Index—using quantitative data (IMMi-T) |
0,811 |
0,707 |
R-M2 |
|
|
|
Bulgaria |
IBI (BG) (Irish Biotic Index (BG)) |
0,800 |
0,600 |
Croatia |
Croatian classification method for benthic macroinvertebrates |
0,800 |
0,600 |
France |
Multimetric index based on macroinvertebrate fauna for the ecological assessment of French wadeable rivers (I2M2) |
0,676 |
0,464 |
Greece |
Hellenic Evaluation System-2 (HESY-2) |
0,944 |
0,708 |
Italy |
MacrOper (based on STAR Intercalibration Common Metric Index ICMi) |
0,940 |
0,700 |
Portugal |
Rivers Biological Quality Assessment Method-Benthic Invertebrates (IPtIN, IPtIS) |
0,830 (type 2) |
0,693 (type 2) |
0,880 (type 4) |
0,676 (type 4) |
||
Slovenia |
Metodologija vrednotenja ekološkega stanja vodotokov na podlagi bentoških nevretenčarjev |
0,800 |
0,600 |
Spain |
Iberian Biological Monitoring Working Party (IBMWP) |
0,845 |
0,698 |
Spain |
Iberian Mediterranean Multimetric Index—using quantitative data (IMMi-T) |
0,811 |
0,707 |
R-M4 |
|
|
|
Cyprus |
STAR Intercalibration Common Metric Index (STAR_ICMi) |
0,972 |
0,729 |
France |
Multimetric index based on macroinvertebrate fauna for the ecological assessment of French wadeable rivers (I2M2) |
0,676 |
0,464 |
Greece |
Hellenic Evaluation System-2 (HESY-2) |
0,850 |
0,637 |
Italy |
MacrOper (based on STAR Intercalibration Common Metric Index ICMi) |
0,940 |
0,700 |
Spain |
Iberian Biological Monitoring Working Party (IBMWP) |
0,840 |
0,700 |
Spain |
Iberian Mediterranean Multimetric Index—using quantitative data (IMMi-T) |
0,850 |
0,694 |
R-M5 |
|
|
|
Croatia |
Croatian classification method for benthic macroinvertebrates |
0,800 |
0,600 |
Cyprus |
STAR Intercalibration Common Metric Index (STAR_ICMi) |
0,982 |
0,737 |
Greece |
Hellenic Evaluation System-2 (HESY-2) |
0,963 |
0,673 |
Italy |
MacrOper (based on STAR Intercalibration Common Metric Index ICMi) |
0,970 |
0,730 |
Portugal |
Rivers Biological Quality Assessment Method-Benthic Invertebrates (IPtIN, IPtIS) |
0,973 (type 5) |
0,705 (type 5) |
0,961 (type 6) |
0,708 (type 6) |
||
Slovenia |
Metodologija vrednotenja ekološkega stanja vodotokov na podlagi bentoških nevretenčarjev |
0,800 |
0,600 |
Spain |
Iberian Biological Monitoring Working Party (IBMWP) |
0,830 |
0,630 |
Spain |
Iberian Mediterranean Multimetric Index—using quantitative data (IMMi-T) |
0,830 |
0,620 |
Spain (Balearic Islands) |
INVMIB index (INVertebrate Multimetric Illes Balears) |
0,93 |
0,68 |
MEDITERRANEAN RIVERS GEOGRAPHICAL INTERCALIBRATION GROUP RESULTS |
|
Biological Quality Element |
Macrophytes and Phytobenthos |
Sub-Biological Quality Element |
Macrophytes |
Type and Country |
National classification systems intercalibrated |
Ecological Quality Ratios |
|
High-Good boundary |
Good-Moderate boundary |
||
R-M1, M2, M4 |
|
|
|
Bulgaria (R-M1 and R-M2) |
RI (BG) (Reference Index (BG)) |
0,640 |
0,350 |
Croatia (R-M1 and R-M2) |
Croatian classification method for macrophytes in rivers |
0,800 |
0,600 |
Cyprus (R-M4) |
IBMR – Biological Macrophyte Index for Rivers |
0,795 |
0,596 |
France |
IBMR – Indice Biologique Macrophytique en Rivière French standard NF T90-395 (2003-10-01) |
0,930 |
0,745 |
Greece |
IBMR – Biological Macrophyte Index for Rivers |
0,750 |
0,560 |
Italy |
IBMR – Biological Macrophyte Index for Rivers |
0,900 |
0,800 |
Portugal (R-M1 and R-M2) |
IBMR – Biological Macrophyte Index for Rivers |
0,920 |
0,690 |
Slovenia (R-M1 and R-M2) |
Metodologija vrednotenja ekološkega stanja vodotokov na podlagi fitobentosa in makrofitov, makrofiti |
0,800 |
0,600 |
Spain |
IBMR – Biological Macrophyte Index for Rivers |
0,950 |
0,740 |
MEDITERRANEAN RIVERS GEOGRAPHICAL INTERCALIBRATION GROUP RESULTS |
|
Biological Quality Element |
Macrophytes and Phytobenthos |
Sub-Biological Quality Element |
Phytobenthos |
Type and Country |
National classification systems intercalibrated |
Ecological Quality Ratios |
|
High-Good boundary |
Good-Moderate boundary |
||
R-M1 |
|
|
|
Bulgaria |
IPS (Indice de polluo-sensibilité) |
0,820 |
0,630 |
Croatia |
Croatian classification method for phytobenthos in rivers |
0,829 |
0,555 |
France |
IBD 2007 (Coste et al, Ecol. Ind. 2009). AFNOR NF-T-90-354, December 2007. Arrêté ministériel du 25 janvier 2010 modifié relatif aux méthodes et critères d’évaluation de l’état écologique {...} des eaux de surface |
0,940 |
0,780 |
Greece |
IPS (Coste in Cemagref, 1982) Intercalibrated (EQR IPS) |
0,956 |
0,717 |
Italy |
Intercalibration Common Metric Index (ICMi) (Mancini & Sollazzo, 2009) |
0,800 |
0,610 |
Portugal |
IPS (Coste in Cemagref, 1982) |
0,970 (type 1 ) |
0,730 (type 1 ) |
0,910 (type 3 ) |
0,680 (type 3 ) |
||
Slovenia |
Metodologija vrednotenja ekološkega stanja vodotokov na podlagi fitobentosa in makrofitov, fitobentos |
0,800 |
0,600 |
Spain |
IPS (Coste in Cemagref, 1982) |
0,937 |
0,727 |
R-M2 |
|
|
|
Bulgaria |
IPDS (Indice de polluo-sensibilité) |
0,820 |
0,630 |
Croatia |
Croatian classification method for phytobenthos in rivers |
0,829 |
0,555 |
France |
IBD 2007 (Coste et al, Ecol. Ind. 2009). AFNOR NF-T-90-354, December 2007. Arrêté ministériel du 25 janvier 2010 modifié relatif aux méthodes et critères d’évaluation de l’état écologique {...} des eaux de surface |
0,940 |
0,780 |
Greece |
IPS (Coste in Cemagref, 1982) Intercalibrated (EQR IPS) |
0,953 |
0,732 |
Italy |
Intercalibration Common Metric Index (ICMi) (Mancini & Sollazzo, 2009) |
0,800 |
0,610 |
Portugal |
IPS (Coste in Cemagref, 1982)) |
0,910 (type 2 ) |
0,680 (type 2 ) |
0,970 (type 4 ) |
0,730 (type 4 ) |
||
Slovenia |
Metodologija vrednotenja ekološkega stanja vodotokov na podlagi fitobentosa in makrofitov, fitobentos |
0,800 |
0,600 |
Spain |
IPS (Coste in Cemagref, 1982) |
0,938 |
0,727 |
R-M4 |
|
|
|
Cyprus |
IPS (Coste in Cemagref, 1982) |
0,910 |
0,683 |
France |
IBD 2007 (Coste et al, Ecol. Ind. 2009). AFNOR NF-T-90-354, December 2007. Arrêté ministériel du 25 janvier 2010 modifié relatif aux méthodes et critères d’évaluation de l’état écologique {...} des eaux de surface |
0,940 |
0,780 |
Greece |
IPS (Coste in Cemagref, 1982) Intercalibrated (EQR IPS) |
0,932 |
0,716 |
Italy |
Intercalibration Common Metric Index (ICMi) (Mancini & Sollazzo, 2009) |
0,800 |
0,610 |
Spain |
IPS (Coste in Cemagref, 1982) |
0,935 |
0,727 |
R-M5 |
|
|
|
Croatia |
Croatian classification method for phytobenthos in rivers |
0,850 |
0,585 |
Cyprus |
IPS (Coste in Cemagref, 1982) |
0,958 |
0,718 |
Italy |
Intercalibration Common Metric Index (ICMi) (Mancini & Sollazzo, 2009) |
0,880 |
0,650 |
Portugal |
IPS (Coste in Cemagref, 1982) |
0,800 (Type 5 ) |
0,651 (Type 5 ) |
0,940 (Type 6 ) |
0,700 (Type 6 ) |
||
Slovenia |
Metodologija vrednotenja ekološkega stanja vodotokov na podlagi fitobentosa in makrofitov, fitobentos |
0,800 |
0,600 |
Spain |
IPS (Coste in Cemagref, 1982) |
0,935 |
0,700 |
Spain (Balearic Islands) |
Diatom multimetric index (DIATMIB) |
0,93 |
0,68 |
Water category |
Rivers |
Geographical Intercalibration Group |
Northern rivers |
Description of types that have been intercalibrated
Type |
River characterisation |
Catchment area of stretch (km2) |
Altitude and geomorphology |
Alkalinity (meq/l) |
Organic material (mg Pt/l) |
R-N1 |
Small lowland siliceous moderate alkalinity |
10 – 100 |
< 200 m a.s.l. or below the highest coastline |
0,2 – 1 |
< 30 (< 150 in Ireland) |
R-N3 |
Small/medium lowland organic low alkalinity |
10 – 1 000 |
< 0,2 |
> 30 |
|
R-N4 |
Medium lowland siliceous moderate alkalinity |
100 – 1 000 |
0,2 – 1 |
< 30 |
|
R-N5 |
Small mid-altitude siliceous low alkalinity |
10 – 100 |
Between lowland and highland |
< 0,2 |
< 30 |
R-N9 |
Small/medium mid-altitude siliceous low alkalinity organic (humic) |
10 – 1 000 |
Between lowland and highland |
< 0,2 |
> 30 |
NORTHERN RIVERS GEOGRAPHICAL INTERCALIBRATION GROUP RESULTS |
|
Biological Quality Element |
Benthic invertebrate fauna (methods sensitive for organic enrichment and general degradation) |
Country |
National classification systems intercalibrated |
Ecological Quality Ratios |
|
High-Good boundary |
Good-Moderate boundary |
||
Finland |
Revised Finnish river invertebrate fauna assessment method |
0,80 |
0,60 |
Ireland |
Quality Rating System (Q-value) |
0,85 |
0,75 |
Norway |
ASPT |
0,99 |
0,87 |
Sweden |
DJ-index (Dahl & Johnson 2004) |
0,80 |
0,60 |
Biological Quality Element |
Benthic invertebrate fauna (methods sensitive for acidification) |
Country |
National classification systems intercalibrated |
Ecological Quality Ratios |
|
High-Good boundary |
Good-Moderate boundary |
||
Ireland |
Acid Waters Indicator Community Species (IE AWICSp) |
0,99 |
0,90 |
Norway |
AcidIndex2 (Modified Raddum index2) (river acidification) |
0,675 |
0,515 |
Country |
National classification systems intercalibrated |
Ecological Quality Ratios |
|
High-Good boundary |
Good-Moderate boundary |
||
Sweden |
MISA: Multimetric Invertebrate Stream Acidification index |
0,550 |
0,400 |
NORTHERN RIVERS GEOGRAPHICAL INTERCALIBRATION GROUP RESULTS |
|
Biological Quality Element |
Macrophytes and Phytobenthos |
Sub-Biological Quality Element |
Macrophytes |
Type and Country |
National classification systems intercalibrated |
Ecological Quality Ratios |
|
High-Good boundary |
Good-Moderate boundary |
||
R-N3 and R-N9 |
|
|
|
Finland |
Trophic index TIc |
0,889 |
0,610 |
Sweden |
Trophic index TIc |
0,889 |
0,610 |
Norway |
Trophic index TIc |
0,889 |
0,610 |
NORTHERN RIVERS GEOGRAPHICAL INTERCALIBRATION GROUP RESULTS |
|
Biological Quality Element |
Macrophytes and Phytobenthos |
Sub-Biological Quality Element |
Phytobenthos |
Country |
National classification systems intercalibrated |
Ecological Quality Ratios |
|
High-Good boundary |
Good-Moderate boundary |
||
Finland |
Revised Finnish river phytobenthos method |
0,80 |
0,60 |
Ireland |
Revised form of Trophic Diatom Index (TDI) |
0,93 |
0,78 |
Norway |
Periphyton Index of Trophic Status (PIT) |
0,99 (Ca ≤ 1 mg/l) |
0,83 |
0,95 (Ca > 1 mg/l) |
|||
Sweden |
Indice de Polluosensibilité Spécifique (IPS) |
0,89 |
0,74 |
Water category |
Rivers |
Geographical Intercalibration Groups |
All |
Biological Quality Element |
Fish fauna |
Country |
National classification systems intercalibrated |
Ecological Quality Ratios |
|
High-Good boundary |
Good-Moderate boundary |
||
Austria |
FIA |
0,875 |
0,625 |
France |
FBI (Fish-Based Index): Indice Poissons Rivière (IPR). AFNOR NF-T90-344 |
1,131 |
0,876 |
Germany |
FIBS – fischbasiertes Bewertungssystem für Fließgewässer zur Umsetzung der EG-Wasserrahmenrichtlinie in Deutschland |
1,086 |
0,592 |
Italy |
NISECI index (New Index of Ecological Status of Fish Communities) |
0,800 |
0,520 |
Slovenia |
Metodologija vrednotenja ekološkega stanja vodotokov na podlagi rib |
0,800 |
0,600 |
Country |
National classification systems intercalibrated |
Ecological Quality Ratios |
|
High-Good boundary |
Good-Moderate boundary |
||
Bulgaria |
TsBRI (Type Specific Bulgarian Fish Index) |
0,860 |
0,650 |
Croatia |
Croatian classification method for fish in rivers |
0,800 |
0,600 |
Czechia |
Czech multimetric method CZI |
0,780 |
0,585 |
Romania |
EFI+ European Fish index (cyprinid wading type) |
0,939 |
0,700 |
Romania |
EFI+ European Fish index (salmonid type) |
0,911 |
0,755 |
Slovakia |
Fish Index of Slovakia FIS |
0,710 |
0,570 |
Country |
National classification systems intercalibrated |
Ecological Quality Ratios |
|
High-Good boundary |
Good-Moderate boundary |
||
Belgium Flanders |
Upstream and Lowland IBI |
0,850 |
0,650 |
Belgium Wallonia |
IBIP (Arrêté du Gouvernement wallon du 13 septembre 2012 relatif à l’identification, à la caractérisation et à la fixation des seuils d’état écologique applicables aux masses d’eau de surface et modifiant le Livre II du Code de l’Environnement, contenant le Code de l’Eau. Moniteur belge 12.10.2012) |
0,958 |
0,792 |
Denmark |
Danish index for fish in streams DFFVa |
0,700 |
0,500 |
France |
FBI (Fish-Based Index): Indice Poissons Rivière (IPR). AFNOR NF-T-90-344. |
1,131 |
0,835 |
Germany |
FIBS – fischbasiertes Bewertungssystem für Fließgewässer zur Umsetzung der EG-Wasserrahmenrichtlinie in Deutschland |
1,086 |
0,592 |
Latvia |
Latvian Fish Index |
0,880 |
0,660 |
Lithuania |
Lithuanian River Fish Index |
0,940 |
0,720 |
Luxembourg |
Classification française DCE Indice Poissons Rivière (IPR). AFNOR NF-T-90-344 |
1,131 |
0,835 |
Netherlands |
NLFISR |
0,800 |
0,600 |
Poland |
EFI+PL index |
0,800 |
0,600 |
Country |
National classification systems intercalibrated |
Ecological Quality Ratios |
|
High-Good boundary |
Good-Moderate boundary |
||
Croatia |
Croatian classification method for fish in rivers |
0,800 |
0,600 |
Greece |
Hellenic Fish Index (HeFI) |
0,800 |
0,600 |
Portugal |
F-IBIP – Fish-based Index of Biotic Integrity for Portuguese Wadeable Streams |
0,850 |
0,675 |
Spain |
IBIMED – type T2 |
0,816 |
0,705 |
Spain |
IBIMED – type T3 |
0,929 |
0,733 |
Spain |
IBIMED – type T4 |
0,864 |
0,758 |
Spain |
IBIMED – type T5 |
0,866 |
0,650 |
Spain |
IBIMED – type T6 |
0,916 |
0,764 |
Country |
National classification systems intercalibrated |
Ecological Quality Ratios |
|
High-Good boundary |
Good-Moderate boundary |
||
Finland |
Finnish Fish Index (FiFi) – type L2 |
0,665 |
0,499 |
Finland |
Finnish Fish Index (FiFi) – type L3 |
0,658 |
0,493 |
Finland |
Finnish Fish Index (FiFi) – type M1 |
0,709 |
0,532 |
Finland |
Finnish Fish Index (FiFi) – type M2 |
0,734 |
0,550 |
Finland |
Finnish Fish Index (FiFi) – type M3 |
0,723 |
0,542 |
Ireland |
Fish Classification Scheme 2 Ireland (FCS2) |
0,845 |
0,540 |
Sweden |
Swedish method VIX |
0,739 |
0,467 |
Water Category |
Rivers |
Geographical Intercalibration Groups |
All – Very Large Rivers |
Description of types that have been intercalibrated
Type |
River characterisation |
Catchment area of stretch (km2) |
Alkalinity (meq/l) |
R-L1 |
Very large low alkalinity rivers |
> 10 000 |
< 0,5 |
R-L2 |
Very large medium to high alkalinity rivers |
> 10 000 |
> 0,5 |
VERY LARGE RIVERS GEOGRAPHICAL INTERCALIBRATION GROUP |
|
Biological Quality Element |
Benthic invertebrate fauna |
Country |
National classification systems intercalibrated |
Ecological Quality Ratios |
|
High-Good boundary |
Good-Moderate boundary |
||
Austria |
Assessment of the Biological Quality Elements – part benthic invertebrates (for large alpine rivers) |
0,80 |
0,60 |
Austria |
Slovak assessment of benthic invertebrates in large rivers (for large lowland rivers) |
0,80 |
0,60 |
Belgium (Flanders) |
Multimetric Macroinvertebrate Index Flanders (MMIF) |
0,90 |
0,70 |
Bulgaria |
mRBA – Modified Rapid Biological Assessment |
0,80 |
0,60 |
Croatia |
Ecological status assessment system based on benthic invertebrates in very large rivers |
0,80 |
0,60 |
Czechia |
Czech system for ecological status assessment of large non-wadeable rivers using benthic macroinvertebrates |
0,80 |
0,60 |
Estonia |
Estonian surface water ecological quality assessment _ large river macroinvertebrates |
0,90 |
0,70 |
Finland |
Revised Finnish river invertebrate fauna assessment method |
0,80 |
0,60 |
Germany |
Germany PTI – Potamon-Typie-Index |
0,80 |
0,60 |
Greece |
STAR_ICMi index |
1,01 |
0,73 |
Hungary |
Hungary HMMI_II – Hungarian Multimetric Macroinvertebrate Index for large and very large rivers |
0,80 |
0,60 |
Italy |
ISA (Indice per la classificazione sulla base dei Substrati Artificiali) – mediterranean rivers |
0,94 |
0,70 |
Italy |
ISA (Indice per la classificazione sulla base dei Substrati Artificiali) – non-mediterranean rivers |
0,96 |
0,72 |
Latvia |
LRMI – Latvian large River Macroinvertebrate Index |
0,88 |
0,63 |
Lithuania |
Lithuanian River Macroinvertebrate Index |
0,80 |
0,60 |
Netherlands |
WFD metrics for natural water types |
0,80 |
0,60 |
Norway |
Norway ASPT – Average Score Per Taxon |
0,99 |
0,87 |
Poland |
RIVECOmacro – MMI_PL |
0,91 |
0,71 |
Portugal |
Portuguese assessment method for Large Rivers using Benthic Macroinvertebrates (IPtIN) |
0,849 |
0,637 |
Romania |
Assessment method for ecological status of water bodies based on macroinvertebrates |
0,80 |
0,60 |
Slovakia |
Slovak assessment of benthic invertebrates in large rivers |
0,80 |
0,60 |
Slovenia |
Metodologija vrednotenja ekološkega stanja vodotokov na podlagi bentoških nevretenčarjev |
0,80 |
0,60 |
Spain |
IBMWP – Iberian Biological Monitoring Working Party |
0,79 |
0,48 |
Sweden |
Average Score Per Taxon (ASPT) and DJ-index |
0,80 |
0,60 |
VERY LARGE RIVERS GEOGRAPHICAL INTERCALIBRATION GROUP |
|
Biological Quality Element |
Phytoplankton |
Country |
National classification systems intercalibrated |
Ecological Quality Ratios |
|
High-Good boundary |
Good-Moderate boundary |
||
Austria |
German PhytoFluss-Index 4.0 |
0,80 |
0,60 |
Belgium (Flanders) |
German PhytoFluss-Index 2.0 |
0,80 |
0,60 |
Bulgaria |
German PhytoFluss-Index 4.0 |
0,80 |
0,60 |
Croatia |
HRPI – Hungarian River Phytoplankton Index |
0,80 |
0,60 |
Czechia |
CZ – Assessment method for ecological status of rivers based on phytoplankton |
0,80 |
0,60 |
Germany |
German PhytoFluss-Index |
0,80 |
0,60 |
Estonia |
EST_PHYPLA_R – Estonian Large River Phytoplankton Index |
0,85 |
0,65 |
Hungary |
HRPI – Hungarian River Phytoplankton Index |
0,80 |
0,60 |
Latvia |
Latvian Large River Phytoplankton Index |
0,80 |
0,60 |
Lithuania |
German River Phytoplankton Index (PhytoFluss-Index for lowland rivers of type 15.2) |
0,80 |
0,60 |
Poland |
IFPL metric – Method for large rivers assessment using phytoplankton |
1,08 |
0,92 |
Portugal |
Portuguese assessment method for Phytoplankton in large rivers (NMASRP) |
0,80 |
0,60 |
Romania |
ECO-FITO – Assessment Method for Ecological Status of the Water Bodies based on Phytoplankton |
0,92 |
0,76 |
Slovakia |
Phytoplankton-SK – Slovak assessment of phytoplankton in large rivers |
0,80 |
0,60 |
VERY LARGE RIVERS GEOGRAPHICAL INTERCALIBRATION GROUP |
|
Biological Quality Element |
Macrophytes and Phytobenthos |
Sub-Biological Quality Element |
Phytobenthos |
Country and Type |
National classification systems intercalibrated |
Ecological Quality Ratios |
|
High-Good boundary |
Good-Moderate boundary |
||
R-L1 |
|
|
|
Finland |
Revised Finnish river phytobenthos method |
0,80 |
0,60 |
Sweden |
Benthic algae in running water – diatom analysis |
0,89 |
0,74 |
R-L2 |
|
|
|
Austria |
Assessment of the Biological Quality Elements – part phytobenthos |
0,85 |
0,57 |
Bulgaria |
IPS (Indice de Polluo-Sensibilité) |
0,76 |
0,58 |
Croatia |
Ecological status assessment system for phytobenthos in rivers based on diatoms |
0,80 |
0,61 |
Czechia |
Assessment system for rivers using phytobenthos |
0,80 |
0,60 |
Estonia |
Estonian surface water ecological quality assessment – river phytobenthos |
0,83 |
0,64 |
France |
IBD 2007 (Coste et al, Ecol. Ind. 2009). AFNOR NF T90-354, April 2016. Arrêté ministériel du 25 janvier 2010 modifié relatif aux méthodes et critères d’évaluation de l’état écologique {...} des eaux de surface |
0,92 |
0,76 |
Germany |
Verfahrensanleitung für die ökologische Bewertung von Fließgewässern zur Umsetzung der EG-Wasserrahmenrichtlinie: Makrophyten und Phytobenthos (PHYLIB), Modul Diatomeen |
0,725 |
0,55 |
Hungary |
Ecological status assessment for rivers based on diatoms |
0,762 |
0,60 |
Italy |
Intercalibration Common Metric Index (ICMi) (Mancini &Sollazzo 2009) |
0,89 (national type C) |
0,70 (national type C) |
0,82 (national type M3 ) |
0,62 (national type M3 ) |
||
Latvia |
Latvian assessment method using phytobenthos in very large rivers (IPS index) |
0,78 |
0,58 |
Lithuania |
Lithuanian River Phytobenthos Index |
0,73 |
0,55 |
Netherlands |
WFD-metrics for natural water types |
0,80 |
0,60 |
Portugal |
IPS (Coste in Cemagref, 1982) |
0,90 |
0,67 |
Romania |
National (Romanian) Assessment Method for Rivers Ecological Status based on Phytobenthos (Diatoms) – RO-AMRP |
0,80 |
0,60 |
Slovakia |
Ecological status assessment system for rivers using phytobenthos |
0,90 |
0,70 |
Slovenia |
Metodologija vrednotenja ekološkega stanja vodotokov na podlagi fitobentosa in makrofitov, fitobentos |
0,80 |
0,60 |
Spain |
IPS (Coste in Cemagref, 1982) |
0,68 |
0,48 |
VERY LARGE RIVERS GEOGRAPHICAL INTERCALIBRATION GROUP |
|
Biological Quality Element |
Fish fauna |
Country |
National classification systems intercalibrated |
|
Ecological Quality Ratios |
|||
|
High-Good boundary |
Good-Moderate boundary |
||||
Austria |
Fish Index Austria (FIA) |
|
n.i. |
0,625 |
||
Belgium (Flanders) |
Flemish Index of Biotic Integrity (IBIFL) |
|
n.i. |
0,805 |
||
Bulgaria |
Bulgarian River Index for the Danube River (BRID) |
|
n.i. |
0,600 |
||
Croatia |
Croatian fish index for large rivers (CFILR) |
|
0,87 |
0,550 |
||
Czechia |
Czech Multimetric Fish Index for Rivers (CZI) |
|
0,800 |
0,600 |
||
Greece |
Hellenic Fish Index (HeFI) |
|
n.i. |
0,650 |
||
Hungary |
Hungarian Multimetric Fish Index Group (HMMFI) |
Highland |
0,800 |
0,600 |
||
Lowland |
||||||
Latvia |
Latvian Large River Fish Index |
|
n.i. |
0,660 |
||
Lithuania |
Lithuanian River Fish Index |
|
n.i. |
0,720 |
||
Norway |
European Fish Index (EFI) |
|
0,996 |
0,755 |
||
Poland |
Index of Biotic Integrity with Diadromous Fish Index (IBIPL) |
|
n.i. |
0,688 |
||
Portugal |
Fish-based index of biotic integrity for Portuguese Large Rivers (FIBIP-GR) |
|
0,860 |
0,600 |
||
Romania |
New European Fish (EFI+I) |
Boat-sampling |
0,971 |
0,651 |
||
Wade-sampling |
0,939 |
0,655 |
||||
Slovakia |
Fish Index of Slovakia (FIS) |
|
n.i. |
0,661 |
||
Slovenia |
Metodologija vrednotenja ekološkega stanja vodotokov na podlagi rib |
|
0,800 |
0,600 |
||
Spain |
New European Fish (EFI+I) |
Boat-sampling |
n.i. |
0,614 |
||
Sweden |
Swedish Method VIX |
|
0,739 |
0,467 |
||
|
Water category |
Lakes |
Geographical Intercalibration Group |
Alpine lakes |
Description of types that have been intercalibrated
Type |
Lake characterisation |
Altitude (m above sea level) |
Mean depth (m) |
Alkalinity (meq/l) |
Lake size (km2) |
L-AL3 |
Lowland or mid-altitude, deep, moderate to high alkalinity (alpine influence), large |
50 – 800 |
> 15 |
> 1 |
> 0,5 |
L-AL4 |
Mid-altitude, shallow, moderate to high alkalinity (alpine influence), large |
200 – 800 |
3 – 15 |
> 1 |
> 0,5 |
ALPINE LAKES GEOGRAPHICAL INTERCALIBRATION GROUP RESULTS |
|
Biological Quality Element |
Phytoplankton |
Country |
National classification systems intercalibrated |
Ecological Quality Ratios |
|
High-good boundary |
Good-moderate boundary |
||
Austria |
Evaluation of the biological quality elements, Part B2 – phytoplankton |
0,80 |
0,60 |
France |
Phytoplankton Index for Lakes (IPLAC): Indice Phytoplancton Lacustre |
0,80 |
0,60 |
Germany |
PSI (Phyto-Seen-Index) – Bewertungsverfahren für Seen mittels Phytoplankton zur Umsetzung der EG-Wasserrahmenrichtlinie in Deutschland |
0,80 |
0,60 |
Italy |
Italian Phytoplankton Assessment Method (IPAM) |
0,80 |
0,60 |
Slovenia |
Metodologija vrednotenja ekološkega stanja jezer na podlagi fitoplanktona |
0,80 |
0,60 |
ALPINE LAKES GEOGRAPHICAL INTERCALIBRATION GROUP RESULTS |
|
Biological Quality Element |
Macrophytes and Phytobenthos |
Sub-Biological Quality Element |
Macrophytes |
Country |
National classification systems intercalibrated |
IC type |
Ecological Quality Ratios |
|
High-good boundary |
Good-moderate boundary |
|||
Austria |
AIM for Lakes (Austrian Index Macrophytes for lakes) |
L-AL3+ L-AL4 |
0,80 |
0,60 |
France |
French Macrophyte Index for Lakes (IBML): Indice Biologique Macrophytique en Lacs |
L-AL3+ L-AL4 |
0,92 |
0,72 |
Germany |
Verfahrensanleitung für die ökologische Bewertung von Seen zur Umsetzung der EG-Wasserrahmenrichtlinie: Makrophyten und Phytobenthos (PHYLIB), Modul Makrophyten |
L-AL3+ L-AL4 |
0,76 |
0,51 |
Germany |
Verfahrensanleitung für die ökologische Bewertung von Seen zur Umsetzung der EG-Wasserrahmenrichtlinie: Makrophyten und Phytobenthos (PHYLIB), Modul Makrophyten und Phytobenthos |
LAL4 |
0,74 |
0,47 |
Italy |
MacroIMMI (Macrophytic index for the evaluation of the ecological quality of the Italian lakes) |
L-AL3+ L-AL4 |
0,80 |
0,60 |
Slovenia |
Metodologija vrednotenja ekološkega stanja jezer na podlagi fitobentosa in makrofitov, makrofiti |
L-AL3 |
0,80 |
0,60 |
ALPINE LAKES GEOGRAPHICAL INTERCALIBRATION GROUP RESULTS |
|
Biological Quality Element |
Benthic invertebrate fauna |
Country |
National classification systems intercalibrated |
Ecological Quality Ratios |
|
High-good boundary |
Good-moderate boundary |
||
Austria |
Method for the assessment of Alpine lakes using benthic invertebrates |
0,80 |
0,60 |
Germany |
AESHNA – Bewertungsverfahren für das eulitorale Makrozoobenthos in Seen zur Umsetzung der EG-Wasserrahmenrichtlinie in Deutschland |
0,80 |
0,60 |
Slovenia |
Metodologija vrednotenja ekološkega stanja jezer na podlagi bentoških nevretenčarjev |
0,80 |
0,60 |
ALPINE LAKES GEOGRAPHICAL INTERCALIBRATION GROUP RESULTS |
|
Biological Quality Element |
Fish fauna |
Country |
National classification systems intercalibrated |
Ecological Quality Ratios |
|
High-good boundary |
Good-moderate boundary |
||
Austria |
ALFI (Austrian lake fish index): A multimetric index to assess the ecological status of alpine lakes based on fish fauna |
0,80 |
0,60 |
Germany |
DeLFI_SITE – Deutsches probennahmestandort-spezifisches Bewertungsverfahren für Fische in Seen zur Umsetzung der EG-Wasserrahmenrichtlinie |
0,85 |
0,69 |
Italy |
Lake Fish Index (LFI) |
0,82 |
0,64 |
Slovenia |
Metodologija vrednotenja ekološkega stanja jezer na podlagi rib |
0,80 |
0,60 |
Water category |
Lakes |
Geographical Intercalibration Group |
Central/Baltic lakes |
Description of types that have been intercalibrated
Type |
Lake characterisation |
Altitude (m above sea level) |
Mean depth (m) |
Alkalinity (meq/l) |
Residence time (years) |
L-CB1 |
Lowland, shallow, calcareous |
< 200 |
3 – 15 |
> 1 |
1 – 10 |
L-CB2 |
Lowland, very shallow, calcareous |
< 200 |
< 3 |
> 1 |
0,1 – 1 |
CENTRAL-BALTIC LAKES GEOGRAPHICAL INTERCALIBRATION GROUP RESULTS |
|
Biological Quality Element |
Phytoplankton |
Country |
National classification systems intercalibrated |
Ecological Quality Ratios |
|
High-good boundary |
Good-moderate boundary |
||
Belgium (Flanders) |
Flemish phytoplankton assessment method for lakes |
0,80 |
0,60 |
Denmark |
Danish Lake Phytoplankton Index |
0,80 |
0,60 |
Estonia |
Estonian surface water ecological quality assessment – lake phytoplankton |
0,80 |
0,60 |
Germany |
PSI (Phyto-Seen-Index) – Bewertungsverfahren für Seen mittels Phytoplankton zur Umsetzung der EG-Wasserrahmenrichtlinie in Deutschland – German Phyto-Lake-Index (Phyto-See-Index) |
0,80 |
0,60 |
Ireland |
IE Lake Phytoplankton Index |
0,80 |
0,60 |
Latvia |
Latvian Lake Phytoplankton Index |
0,81 |
0,61 |
Lithuania |
German Lake Phytoplankton Index (Phyto-See-Index) |
0,81 |
0,61 |
Netherlands |
WFD – metrics for natural water types |
0,80 |
0,60 |
Poland |
Phytoplankton method for Polish Lakes (PMPL) |
0,80 |
0,60 |
CENTRAL-BALTIC LAKES GEOGRAPHICAL INTERCALIBRATION GROUP RESULTS |
|
Biological Quality Element |
Macrophytes and Phytobenthos |
Sub-Biological Quality Element |
Macrophytes |
Country |
National classification systems intercalibrated |
IC type |
Ecological Quality Ratios |
|
High-good boundary |
Good-moderate boundary |
|||
Belgium (Flanders) |
Flemish macrophyte assessment system |
All types |
0,80 |
0,60 |
Denmark |
Danish Lake Macrophytes Index |
All types |
0,80 |
0,60 |
Estonia |
Estonian surface water ecological quality assessment – lake macrophytes |
LCB1 |
0,78 |
0,52 |
LCB2 |
0,76 |
0,50 |
||
Germany |
Verfahrensanleitung für die ökologische Bewertung von Seen zur Umsetzung der EG-Wasserrahmenrichtlinie: Makrophyten und Phytobenthos (PHYLIB), Modul Makrophyten |
All types |
0,80 |
0,60 |
Latvia |
Latvian Lake Macrophyte Assessment Method |
All types |
0,80 |
0,60 |
Lithuania |
Lithuanian Lake Macrophyte Index |
All types |
0,75 |
0,50 |
Netherlands |
WFD-metrics for natural water types |
All types |
0,80 |
0,60 |
Poland |
Macrophyte based indication method for lakes – Ecological Status Macrophyte Index ESMI (multimetric) |
All types |
0,68 |
0,41 |
CENTRAL-BALTIC LAKES GEOGRAPHICAL INTERCALIBRATION GROUP RESULTS |
|
Biological Quality Element |
Benthic invertebrate fauna |
Country |
National classification systems intercalibrated |
Ecological Quality Ratios |
|
High-good boundary |
Good-moderate |
||
Belgium (Flanders) |
Multimetric Macroinvertebrate Index Flanders (MMIF) |
0,90 |
0,70 |
Denmark |
Danish Lake Macroinvertebrate Index (DLMI) |
0,696 |
0,511 |
Estonia |
Estonian surface water ecological quality assessment – lake macroinvertebrates |
0,86 |
0,70 |
Germany |
AESHNA – Bewertungsverfahren für das eulitorale Makrozoobenthos in Seen zur Umsetzung der EG-Wasserrahmenrichtlinie in Deutschland |
0,80 |
0,60 |
Latvia |
Latvian Lake Macroinvertebrate Multimetric Index (LLMMI) |
0,85 |
0,52 |
Lithuania |
Lithuanian Lake Macroinvertebrate Index |
0,74 |
0,50 |
Netherlands |
WFDi – Metric for Natural Watertypes |
0,80 |
0,60 |
Poland |
Lake Macroinvertebrate Index (LMI) |
0,92 |
0,588 |
CENTRAL-BALTIC LAKES GEOGRAPHICAL INTERCALIBRATION GROUP RESULTS |
|
Biological Quality Element |
Fish fauna |
Description of common intercalibration types
Type |
Lake characterisation |
Altitude (m above sea level) |
Mean depth (m) |
Alkalinity (meq/l) |
Residence time (years) |
L-CB1 |
Lowland, shallow, calcareous |
< 200 |
3 – 15 |
> 1 |
1 – 10 |
L-CB2 |
Lowland, very shallow, calcareous |
< 200 |
< 3 |
> 1 |
0,1 – 1 |
L-CB3 |
Lowland, shallow, small, siliceous (moderate alkalinity) |
< 200 |
3 – 15 |
0,2 – 1 |
1 – 10 |
L-CB4 |
Heavily modified water bodies |
200 – 700 |
3 – 30 |
> 0,2 |
0,1 – 5 |
Country |
National classification systems intercalibrated |
Ecological Quality Ratios |
|
High-good boundary |
Good-moderate |
||
Czechia |
CZ-FBI |
0,870 |
0,619 |
Denmark |
Danish Lake Fish Index |
0,75 |
0,54 |
EE |
LAFIEE |
0,80 |
0,61 |
Germany |
DeLFI_SITE – Deutsches probennahmestandort-spezifisches Bewertungsverfahren für Fische in Seen zur Umsetzung der EG-Wasserrahmenrichtlinie |
0,95 |
0,80 |
France |
ELFI (European Lake Fish Index): Indice Ichtyofaune Lacustre (IIL) |
0,73 |
0,49 |
Latvia |
Latvian Lake Fish Index |
0,76 |
0,57 |
Lithuania |
Lithuanian Lake Fish Index |
0,865 |
0,605 |
Netherlands |
VISMAATLAT |
0,80 |
0,60 |
Poland |
LFI+ |
0,866 |
0,595 |
Poland |
LFI EN |
0,804 |
0,557 |
Water category |
Lakes |
Geographical Intercalibration Group |
Eastern Continental lakes |
Description of common intercalibration types
Type |
Lake characterisation |
Altitude (m above sea level) |
Mean depth (m) |
Alkalinity (meq/l) |
Conductivity (μS/cm) |
L-EC1 |
Lowland very shallow hard-water |
< 200 |
< 6 |
1 – 4 |
300 – 1 000 |
EASTERN CONTINENTAL LAKES GEOGRAPHICAL INTERCALIBRATION GROUP |
|
Biological Quality Element |
Phytoplankton |
Country |
National classification systems intercalibrated |
Ecological Quality Ratios |
|
High-good boundary |
Good-moderate boundary |
||
Bulgaria |
HLPI-Hungarian lake phytoplankton index |
0,80 |
0,60 |
Hungary |
HLPI-Hungarian lake phytoplankton index |
0,80 |
0,60 |
Romania |
HLPI-Hungarian lake phytoplankton index |
0,80 |
0,60 |
EASTERN CONTINENTAL LAKES GEOGRAPHICAL INTERCALIBRATION GROUP |
|
Biological Quality Element |
Macrophytes and Phytobenthos |
Sub-Biological Quality Element |
Macrophytes |
Country |
National classification systems intercalibrated |
Ecological Quality Ratios |
|
High-good boundary |
Good-moderate boundary |
||
Bulgaria |
RI-BG – Adapted Reference Index |
0,83 |
0,58 |
Hungary |
HU-RI – Adapted Reference Index |
0,89 |
0,67 |
Romania |
MIRO – Macrophyte Index for Romanian Lakes (Adapted Reference Index) |
0,86 |
0,66 |
EASTERN CONTINENTAL LAKES GEOGRAPHICAL INTERCALIBRATION GROUP |
|
Biological Quality Element |
Benthic invertebrate fauna |
Country |
National classification systems intercalibrated |
Ecological Quality Ratios |
|
High-good boundary |
Good-moderate boundary |
||
Bulgaria |
HMMI_lakes (Hungarian Macrozoobenton Multimetric Index for Lakes |
0,85 |
0,65 |
Hungary |
HMMI_lakes (Hungarian Macrozoobenton Multimetric Index for Lakes |
0,85 |
0,65 |
Romania |
ECO-NL-BENT Romanian ecological status assessment system for natural lakes using benthic invertebrates |
0,93 |
0,60 |
Water category |
Lakes |
Geographical Intercalibration Group |
Mediterranean lakes |
Description of types that have been intercalibrated
Type |
Lake characterisation |
Altitude (m) |
Annual mean precipitation (mm) and T (°C) |
Mean depth (m) |
Area (km2) |
Catchment (km2) |
Alkalinity (meq/l) |
L-M5/7 |
Reservoirs, deep, large, siliceous, ‘wet’ areas |
< 1 000 |
> 800 and/or < 15 |
> 15 |
0,5 – 50 |
< 20 000 |
< 1 |
L-M8 |
Reservoirs, deep, large, calcareous |
< 1 000 |
- |
> 15 |
0,5 – 50 |
< 20 000 |
> 1 |
MEDITERRANEAN LAKES GEOGRAPHICAL INTERCALIBRATION GROUP RESULTS |
|
Biological Quality Element |
Phytoplankton |
Country and Type |
National classification methods intercalibrated |
Ecological Quality Ratios |
|
High-good boundary |
Good-moderate boundary |
||
LM 5/7 |
|||
France |
Phytoplankton Index for Lakes (IPLAC): Indice Phytoplancton Lacustre |
n.d. (*1) |
0,60 |
Greece |
New Mediterranean Assessment System for Reservoirs (NMASRP) |
n.d. (*1) |
0,60 |
Italy |
New Italian Method (NITMET) |
n.d. (*1) |
0,60 |
Portugal |
Reservoirs Biological Quality Assessment Method – Phytoplankton (New Mediterranean Assessment System for Reservoirs Phytoplankton: NMASRP). |
n.d. (*1) |
0,60 |
Spain |
Mediterranean Assessment System for Reservoirs Phytoplankton (MASRP). |
n.d. (*1) |
0,58 |
L-M8 |
|||
Cyprus |
New Mediterranean Assessment System for Reservoirs Phytoplankton (NMASRP). |
n.d. (*1) |
0,60 |
France |
Phytoplankton Index for Lakes (IPLAC): Indice Phytoplancton Lacustre |
n.d. (*1) |
0,60 |
Greece |
New Mediterranean Assessment System for Reservoirs (NMASRP) |
n.d. (*1) |
0,60 |
Italy |
New Italian Method (NITMET) |
n.d. (*1) |
0,60 |
Spain |
Mediterranean Assessment System for Reservoirs Phytoplankton (MASRP). |
n.d. (*1) |
0,60 |
Water category |
Lakes |
Geographical Intercalibration Group |
Northern lakes |
NORTHERN LAKES GEOGRAPHICAL INTERCALIBRATION GROUP RESULTS |
|
Biological Quality Element |
Phytoplankton |
Type |
Lake characterisation |
Altitude (m above sea level) |
Mean depth (m) |
Alkalinity (meq/l) |
Colour (mg Pt/l) |
L-N1 |
Lowland, shallow, moderate alkalinity, clear |
< 200 |
3 – 15 |
0,2 – 1 |
< 30 |
L-N2a |
Lowland, shallow, low alkalinity, clear |
< 200 |
3 – 15 |
< 0,2 |
< 30 |
L-N2b |
Lowland, deep, low alkalinity, clear |
< 200 |
> 15 |
< 0,2 |
< 30 |
L-N3a |
Lowland, shallow, low alkalinity, meso-humic |
< 200 |
3 – 15 |
< 0,2 |
30 – 90 |
L-N5 |
Mid-altitude, shallow, low alkalinity, clear |
200 – 800 |
3 – 15 |
< 0,2 |
< 30 |
L-N6a |
Mid-altitude, shallow, low alkalinity, meso-humic |
200 – 800 |
3 – 15 |
< 0,2 |
30 – 90 |
L-N8a |
Lowland, shallow, moderate alkalinity, meso-humic |
< 200 |
3 – 15 |
0,2 – 1 |
30 – 90 |
Country |
National classification methods intercalibrated |
Ecological Quality Ratios |
|
High-good boundary |
Good-moderate boundary |
||
Finland |
Finnish phytoplankton assessment method for lakes |
0,80 |
0,60 |
Ireland |
IE Lake Phytoplankton Index |
0,80 |
0,60 |
Norway |
Lake phytoplankton ecological status classification method |
0,80 |
0,60 |
Sweden |
Ecological assessment methods for lakes. quality factor phytoplankton |
0,80 |
0,60 |
NORTHERN LAKES GEOGRAPHICAL INTERCALIBRATION GROUP RESULTS |
|
Biological Quality Element |
Macrophytes and Phytobenthos |
Sub-Biological Quality Element |
Macrophytes |
Description of types that have been intercalibrated
Type |
Lake characterisation |
Alkalinity (meq/l) |
Colour (mg Pt/l) |
L-N-M 101 |
Low alkalinity, clear |
0,05 – 0,2 |
< 30 |
L-N-M 102 |
Low alkalinity, humic |
0,05 – 0,2 |
> 30 |
L-N-M 201 |
Moderate alkalinity, clear |
0,2 – 1,0 |
< 30 |
L-N-M 202 |
Moderate alkalinity, humic |
0,2 – 1,0 |
> 30 |
L-N-M 301a |
High alkalinity, clear, atlantic subtype |
> 1,0 |
< 30 |
L-N-M 302a |
High alkalinity, humic, atlantic subtype |
> 1,0 |
> 30 |
Country |
National classification methods intercalibrated |
Ecological Quality Ratios |
|
High-good boundary |
Good-moderate |
||
Finland |
Finnish macrophyte classification system (Finnmac) |
0,8 (all types) |
0,6 (all types) |
Ireland |
Free Macrophyte Index |
0,9 (all types) |
0,68 (all types) |
Norway |
National macrophyte index (Trophic Index – TIc) |
Type 101: 0,98 Type 102: 0,96 Type 201: 0,95 Type 202: 0,99 |
Type 101: 0,87 Type 102: 0,87 Type 201: 0,75 Type 202: 0,77 |
Sweden |
Trophic Macrophyte Index (TMI) |
Type 101: 0,93 Type 102: 0,93 Type 201: 0,89 Type 202: 0,91 |
Type 101: 0,80 Type 102: 0,83 Type 201: 0,78 Type 202: 0,78 |
NORTHERN LAKES GEOGRAPHICAL INTERCALIBRATION GROUP RESULTS |
|
Biological Quality Element |
Benthic invertebrates Fauna |
Description of types that have been intercalibrated
Type |
Lake characterisation |
Ecoregion |
Altitude (m absl) |
Alkalinity (meq/l) |
Colour (mg Pt/l) |
Lake littoral acidification |
|
|
|
|
|
L-N-BF1 |
Lowland/mid-altitude, low alkalinity, clear |
n.d. |
< 800 |
0,05 – 0,2 |
< 30 |
Lake profundal eutrophication |
|
|
|
|
|
L-N-BF2 |
Ecoregion 22, low alkalinity, clear and humic |
22 |
Area > 1 km2 , max. depth > 6 m |
< 0,2 |
n.d. |
Country |
National classification methods intercalibrated |
Ecological Quality Ratios |
|
High-good |
Good-moderate |
||
Lake littoral acidification |
|||
IE |
LAMM (Lake Acidification Macroinvertebrate Metric) |
0,86 |
0,70 |
Norway |
MultiClear: Multimetric Invertebrate Index for Clear Lakes |
0,95 |
0,74 |
Sweden |
MILA: Multimetric Invertebrate Lake Acidification index |
0,85 |
0,60 |
Lake profundal eutrophication |
|||
Finland |
Revised Finnish lake invertebrate fauna assessment method (PICM) |
0,80 |
0,60 |
Sweden |
BQI (Benthic Quality Index) |
0,84 |
0,67 |
NORTHERN LAKES GEOGRAPHICAL INTERCALIBRATION GROUP RESULTS |
|
Biological Quality Element |
Fish fauna |
Description of types that have been intercalibrated
Type |
Lake characterisation |
Lake area km2 |
Alkalinity (meq/l) |
Colour (mg Pt/l) |
L-N-F1 |
Dimictic clear water lakes |
< 40 |
< 0,2 |
< 30 |
L-N-F2 |
Dimictic humic lakes |
< 5 |
< 0,2 |
30 – 90 |
Country |
National classification methods intercalibrated |
Ecological Quality Ratios |
|
High-good boundary |
Good-moderate boundary |
||
Eutrophication |
|||
Finland |
EQR4 |
0,80 |
0,60 |
Ireland |
FIL2 |
0,76 |
0,53 |
Norway |
EindexW3 |
0,75 |
0,56 |
Sweden |
EindexW3 |
0,75 |
0,56 |
Acidification |
|||
Norway |
AindexW5 |
0,74 |
0,55 |
Sweden |
AindexW5 |
0,74 |
0,55 |
Water category |
Lakes |
Geographical Intercalibration Group |
Cross-GIG Phytobenthos |
Description of types that have been intercalibrated
Type |
Lake characterisation |
Alkalinity (meq/l) |
Ecoregions |
HA |
High alkalinity lakes |
> 1 |
Alpine, Central-Baltic, Eastern Continental, Mediterranean |
MA |
Moderate alkalinity lakes |
0,2 – 1 |
Alpine, Central-Baltic, Eastern Continental, Mediterranean, Northern |
LA |
Low alkalinity lakes |
< 0,2 |
Northern |
Country and Type |
National classification methods intercalibrated |
Ecological Quality Ratios |
|
High-good boundary |
Good-moderate boundary |
||
HA type |
|||
Belgium (Flanders) |
Proportions of Impact-Sensitive and Impact-Associated Diatoms (PISIAD) |
0,80 |
0,60 |
Croatia |
Croatian phytobenthos-based assessment method |
0,81 |
0,62 |
Denmark |
Danish Lake Phytobenthos classification method |
0,921 |
0,76 |
Germany |
Verfahrensanleitung für die ökologische Bewertung von Seen zur Umsetzung der EG-Wasserrahmenrichtlinie: Makrophyten und Phytobenthos (PHYLIB), Modul Phytobenthos |
0,80 |
0,55 |
Hungary |
MIL – Multimetric Index for Lakes |
0,80 |
0,69 |
Ireland |
Lake Trophic Diatom Index (IE) |
0,90 |
0,63 |
Italy |
Italian national method for the evaluation of the ecological quality of lake waterbodies using benthic diatoms (EPI-L) |
0,75 |
0,5 |
Lithuania |
Lithuanian Lake Phytobenthos Index |
0,63 |
0,47 |
Poland |
PL IOJ (Multimetryczny Indeks Okrzemkowy dla Jezior = Multimetric Diatom Index for Lakes) |
0,91 |
0,76 |
Slovenia |
Metodologija vrednotenja ekološkega stanja jezer na podlagi fitobentosa in makrofitov, fitobentos |
0,80 |
0,60 |
Sweden |
IPS |
0,89 |
0,74 |
MA type |
|||
Belgium (Flanders) |
Proportions of Impact-Sensitive and Impact-Associated Diatoms (PISIAD) |
0,80 |
0,60 |
Finland |
Revised Finnish lake phytobenthos method |
0,80 |
0,60 |
Ireland |
Lake Trophic Diatom Index (IE) |
0,90 |
0,63 |
Italy |
Italian national method for the evaluation of the ecological quality of lake waterbodies using benthic diatoms (EPI-L) |
0,75 |
0,5 |
|
|
|
|
Sweden |
IPS |
0,89 |
0,74 |
LA type |
|||
Ireland |
Lake Trophic Diatom Index (IE) |
0,90 |
0,66 |
Water category |
Coastal waters |
Geographical Intercalibration Group |
Baltic Sea |
Description of types that have been intercalibrated
Type |
Surface salinity (psu) |
Bottom salinity (psu) |
Exposure |
Ice days |
Other Characteristics |
BC1 |
0,5 – 6 Oligohaline |
1 – 6 |
Exposed |
90 – 150 |
Sites in the Quark and the Bothnian Sea, extending to the Archipelago Sea (for phytoplankton the latter is excluded and integrated in type BC9). Influence of humic substances |
BC2 |
6 – 22 Mesohaline |
2 – 6 |
Very Sheltered |
|
Lagoons |
BC3 |
3 – 6 Oligohaline |
3 – 6 |
Sheltered |
90 – 150 |
Finnish and Estonian coasts of Gulf of Finland |
BC4 |
5 – 8 Lower mesohaline |
5 – 8 |
Sheltered |
< 90 |
Sites of Estonia and Latvia in the Gulf of Riga |
BC5 |
6 – 8 Lower mesohaline |
6 – 12 |
Exposed |
< 90 |
Sites in the southeastern Baltic Sea along the coast of Latvia, Lithuania, and Poland |
BC6 |
8 – 12 Mid mesohaline |
8 – 12 |
Sheltered |
< 90 |
Sites along the Western Baltic Sea at the southern Swedish coast and the southeastern Danish coast |
BC7 |
6 – 8 Mid mesohaline |
8 – 11 |
Exposed |
< 90 |
Western Polish coast and eastern German coast |
BC8 |
13 – 18 Upper mesohaline |
18 – 23 |
Sheltered |
< 90 |
Danish and German coasts in the Western Baltic Sea |
BC9 |
3 – 6 Lower mesohaline |
3 – 6 |
Moderately exposed to exposed |
90 – 150 |
Sites in the western Gulf of Finland, Archipelago Sea and Asko archipelago (only for phytoplankton) |
BALTIC SEA GEOGRAPHICAL INTERCALIBRATION GROUP RESULTS |
|
Biological Quality Element |
Phytoplankton |
Country and Type |
National classification systems intercalibrated |
Ecological Quality Ratios |
|
High-good boundary |
Good-moderate boundary |
||
BC7 |
|||
Germany |
German coastal phytoplankton method |
0,8 |
0,6 |
Poland |
Polish coastal phytoplankton method |
0,8 |
0,6 |
BC8 |
|||
Denmark |
Danish coastal phytoplankton method |
0,8 |
0,6 |
Germany |
German coastal phytoplankton method |
0,8 |
0,6 |
Results for parameter indicative of biomass (Chlorophyll-a)
Country and Type |
Ecological Quality Ratios |
Values (μg/l) |
||
High-good boundary |
Good-moderate boundary |
High-good boundary |
Good-moderate boundary |
|
BC1 |
||||
Finland (Quark outer) |
0,76 |
0,59 |
1,7 |
2,2 |
Finland (Bothnian Sea outer) |
0,78 |
0,60 |
1,6 |
2,1 |
Sweden (Quark outer) |
0,75 |
0,58 |
1,6 |
2,1 |
Sweden (Bothnian Sea outer) |
0,80 |
0,60 |
1,5 |
2,0 |
BC4 |
||||
Estonia |
0,830 |
0,670 |
2,4 |
3,0 |
Latvia |
0,82 |
0,67 |
2,2 |
2,7 |
BC5 |
||||
Latvia |
0,650 |
0,390 |
1,85 |
3,1 |
Lithuania |
0,880 |
0,600 |
2,5 |
4,9 |
BC6 |
||||
Denmark |
0,78 |
0,62 |
1,36 |
1,72 |
Sweden |
0,79 |
0,64 |
1,44 |
1,78 |
BC9 |
||||
Estonia |
0,82 |
0,67 |
2,20 |
2,70 |
Finland |
0,79 |
0,65 |
1,90 |
2,30 |
Sweden |
0,80 |
0,67 |
1,50 |
1,80 |
BALTIC SEA GEOGRAPHICAL INTERCALIBRATION GROUP RESULTS |
|
Biological Quality Element |
Macroalgae and Angiosperms |
Country and Type |
National classification systems intercalibrated |
Ecological Quality Ratios |
|
High-good boundary |
Good-moderate boundary |
||
BC3 |
|||
Estonia |
EPI – Estonian coastal water phytobenthos Index (macroalgae and angiosperms) |
0,98 |
0,86 |
Finland |
Fucus depth limit (macroalgae) |
0,92 |
0,79 |
BC4 |
|||
Estonia |
EPI – Estonian Phytobenthos Index (macroalgae and angiosperms) |
0,91 |
0,70 |
Latvia |
PEQI – Phytobenthos Ecological Quality Index |
0,90 |
0,75 |
BC5 |
|||
Latvia |
MDFLD – Maximum depth of the red alga Furcellaria lumbricalis distribution (macroalgae) |
0,90 |
0,75 |
Lithuania |
MDFLD – Lithuanian maximum depth of the red alga Furcellaria lumbricalis distribution (macroalgae) |
0,84 |
0,68 |
BALTIC SEA GEOGRAPHICAL INTERCALIBRATION GROUP RESULTS |
|
Biological Quality Element |
Benthic invertebrate fauna |
Country and Type |
National classification systems intercalibrated |
Ecological Quality Ratios |
|
High-good boundary |
Good-moderate boundary |
||
BC1 |
|||
Finland |
BBI – Finnish Brackish water Benthic Index |
0,96 |
0,56 |
Sweden |
BQI – Swedish multimetric biological quality index (soft sediment infauna) |
0,77 |
0,31 |
BC3 |
|||
Estonia |
ZKI – Estonian coastal water macrozoobenthos community index |
0,39 |
0,24 |
Finland |
BBI – Finnish Brackish water Benthic Index |
0,94 |
0,56 |
BC5 |
|||
Latvia |
BQI – Benthic quality index |
0,87 |
0,61 |
Lithuania |
BQI – Benthic quality index |
0,94 |
0,81 |
BC6 |
|||
Denmark |
Danish Quality Index version 2 (DKI ver2) |
0,84 |
0,68 |
Sweden |
BQI – Swedish multimetric biological quality index (soft sediment infauna) |
0,76 |
0,27 |
BC7 |
|||
Germany |
MarBIT- Marine Biotic Index Tool |
- |
0,60 |
Poland |
B – Macrozoobenthos BQE assessment by multimetric index |
- |
0,58 |
BC8 |
|||
Denmark |
Danish Quality Index version 2 (DKI ver2) |
0,86 |
0,72 |
Germany |
MarBIT – Marine Biotic Index Tool |
0,80 |
0,60 |
Water category |
Coastal waters |
Geographical Intercalibration Group |
North East Atlantic |
Description of types that have been intercalibrated
Type |
Characterisation |
Salinity (psu) Tidal range (m) Depth (m) |
Current Velocity (knots) Exposure |
Mixing Residence Time |
Type for opportunistic blooming macroalgae, seagrasses, saltmarshes, and benthic invertebrate fauna |
||||
NEA 1/26 |
Open oceanic or enclosed seas, exposed or sheltered, euhaline, shallow |
< 30 Mesotidal 1-5 < 30 |
Medium 1 – 3 Exposed or sheltered |
Fully mixed Days (to weeks in the Wadden Sea) |
Subtypes for intertidal macroalgae |
||||
NEA 1/26 A2 |
Open oceanic, exposed or sheltered, euhaline, shallow, Temperate waters (mainly, > 13 °C) and high irradiance (mainly, PAR > 29 Mol/m2 day) |
> 30 Mesotidal 1 – 5 < 30 |
Medium 1 – 3 Exposed or sheltered |
Fully mixed Days |
NEA 1/26 B21 |
Open oceanic or enclosed seas, exposed or sheltered, euhaline, shallow Cool waters (mainly, < 13 °C) and medium irradiance (mainly, PAR < 29 Mol/m2 day) |
> 30 Mainly mesotidal 1 – 5 < 30 |
Medium 1 – 3 Exposed or sheltered |
Fully mixed Days |
Subtypes for phytoplankton |
||||
NEA 1/26a |
Open oceanic, exposed or sheltered, euhaline, shallow |
> 30 Mesotidal 1 – 5 < 30 |
Medium 1 -3 Exposed or sheltered |
Fully mixed Days |
NEA 1/26b |
Enclosed seas, exposed or sheltered, euhaline, shallow |
> 30 Mesotidal 1 – 5 < 30 |
Medium 1 – 3 Exposed or sheltered |
Fully mixed Days |
NEA 1/26c |
Enclosed seas, enclosed or sheltered, partly stratified |
> 30 Microtidal/Mesotidal < 1 – 5 < 30 |
Medium 1 – 3 Exposed or sheltered |
Partly stratified Days to weeks |
NEA 1/26d |
Scandinavian coast, exposed or sheltered, shallow |
> 30 Microtidal < 1 < 30 |
Low < 1 Exposed or moderately exposed |
Partly stratified Days to weeks |
NEA 1/26e |
Areas of upwelling, exposed or sheltered, euhaline, shallow |
> 30 Mesotidal < 1 < 30 |
Medium 1 – 3 Exposed or sheltered |
Fully mixed Days |
Types for phytoplankton, macroalgae, seagrasses, saltmarshes, benthic invertebrate fauna |
||||
NEA 5 |
Helgoland (German Bight), rocky, exposed and partly stratified |
> 30 Mesotidal < 30 |
Medium 1 – 3 Exposed |
Partly stratified Days |
NEA 3/4 |
Polyhaline, Exposed or moderately exposed (Wadden Sea type) |
Polyhaline 18 – 30 Mesotidal 1 – 5 < 30 |
Medium 1 – 3 Exposed or moderately exposed |
Fully mixed Days |
NEA 7 |
Deep fjordic and sea loch systems |
> 30 Mesotidal 1 -5 > 30 |
Low < 1 Sheltered |
Fully mixed Days |
NEA 8a |
Skagerrak Inner Arc Type, polyhaline, microtidal, moderately exposed, shallow |
Polyhaline 25 – 30 Microtidal < 1 > 30 |
Low < 1 Moderately exposed |
Fully mixed Days to weeks |
NEA 8b |
Skagerrak Inner Arc Type, polyhaline, microtidal, moderately sheltered, shallow |
Polyhaline 10 – 30 Microtidal < 1 < 30 |
Low < 1 Sheltered to moderately exposed |
Partly stratified Days to weeks |
NEA 9 |
Fjord with a shallow sill at the mouth with a very deep maximum depth in the central basin with poor deepwater exchange |
Polyhaline 25 – 30 Microtidal < 1 > 30 |
Low < 1 Sheltered |
Partly stratified Weeks |
NEA 10 |
Skagerrak Outer Arc Type, polyhaline, microtidal, exposed, deep |
Polyhaline 25 – 30 Microtidal < 1 > 30 |
Low < 1 Exposed |
Partly stratified Days |
NORTH EAST ATLANTIC GEOGRAPHICAL INTERCALIBRATION GROUP RESULTS |
|
Biological Quality Element |
Phytoplankton |
Phytoplankton: parameter indicative of biomass parameter (Chlorophyll a) |
Country and Type |
Ecological Quality Ratios |
Values (μg/l) |
||
High-good boundary |
Good-moderate boundary |
High-good boundary |
Good-moderate boundary |
|
NEA 1/26a |
||||
France |
0,76 |
0,33 |
4,40 |
10,00 |
Ireland |
0,82 |
0,60 |
9,90 |
15,00 |
Norway |
0,67 |
0,33 |
2,50 |
5,00 |
Spain (Eastern Cantabrian coast) |
0,67 |
0,33 |
1,50 |
3,00 |
Spain (Western-Central Cantabrian Coast) |
0,67 |
0,33 |
3,00 |
6,00 |
Spain (Gulf of Cadiz coast) |
0,67 |
0,33 |
5,00 |
10,00 |
NEA 1/26b |
||||
Belgium |
0,80 |
0,67 |
12,50 |
15,00 |
France |
0,67 |
0,44 |
10,00 |
15,00 |
Netherlands |
0,67 |
0,44 |
10,00 |
15,00 |
NEA 1/26c |
|
|
|
|
Germany |
0,67 |
0,44 |
5,0 |
7,5 |
Denmark |
0,67 |
0,44 |
5,0 |
7,5 |
NEA 1/26e |
||||
Portugal (Iberian strong upwelling-A5) |
0,670 |
0,440 |
8,000 |
12,000 |
Portugal (upwelling-A6, A7) |
0,880 |
0,490 |
4,500 |
8,200 |
Spain (Western Iberian upwelling coast) |
0,67 |
0,44 |
6,00 |
9,00 |
Spain (Western Iberian upwelling coast – rías) |
0,67 |
0,44 |
8,00 |
12,00 |
NEA 3/4 |
||||
Germany (Eems Dollard) |
0,80 |
0,60 |
7,00 |
11,00 |
Germany (Wadden Sea) |
0,80 |
0,60 |
7,00 |
11,00 |
Netherlands (Eems Dollard) |
0,80 |
0,60 |
6,75 |
10,13 |
Netherlands (Wadden Sea) |
0,80 |
0,60 |
9,60 |
14,40 |
Netherlands (North Sea) |
0,80 |
0,60 |
11,25 |
16,88 |
NEA 8a |
||||
Norway |
0,79 |
0,57 |
3,95 |
5,53 |
Sweden |
0,75 |
0,49 |
1,54 |
2,35 |
NEA 8b (The Sound) |
||||
Denmark |
0,79 |
0,59 |
1,22 |
1,63 |
Sweden |
0,80 |
0,60 |
1,18 |
1,56 |
NEA 8b (The Kattegat and Great Belt) |
||||
Denmark |
0,83 |
0,64 |
1,22 |
1,58 |
Sweden |
0,84 |
0,65 |
1,18 |
1,52 |
NEA 9 |
||||
Norway |
0,76 |
0,43 |
3,92 |
6,90 |
Sweden |
0,73 |
0,38 |
1,89 |
3,60 |
NEA 10 |
||||
Norway |
0,73 |
0,49 |
3,53 |
5,26 |
Sweden |
0,71 |
0,46 |
1,39 |
2,14 |
NORTH EAST ATLANTIC GEOGRAPHICAL INTERCALIBRATION GROUP RESULTS |
|
Biological Quality Element |
Macroalgae and Angiosperms |
Sub-Biological Quality Element |
Macroalgae |
Intertidal or subtidal macroalgae rocky bottom
Country and Type |
National classification systems intercalibrated |
Ecological Quality Ratios |
|
High-good boundary |
Good-moderate boundary |
||
Type NEA1/26 A2 intertidal macroalgae |
|||
France |
CCO – Cover, Characteristic species, Opportunistic species on intertidal rocky bottoms |
0,80 |
0,60 |
Portugal |
PMarMAT – Marine Macroalgae Assessment Tool |
0,80 |
0,61 |
Spain |
CFR – Quality of Rocky Bottoms |
0,81 |
0,60 |
Spain |
RICQI – Rocky Intertidal Community Quality Index |
0,82 |
0,60 |
Spain |
RSL – Reduced Species List |
0,75 |
0,48 |
Type NEA1/26 B21 intertidal macroalgae |
|||
Ireland |
RSL – Rocky Shore Reduced Species List |
0,80 |
0,60 |
Norway |
RSLA – Rocky Shore Reduced Species List with Abundance |
0,80 |
0,60 |
Type NEA 7 intertidal macroalgae |
|
||
Norway |
RSLA – Rocky Shore Reduced Species List with Abundance |
0,80 |
0,60 |
Type NEA8a/9/10 subtidal macroalgae |
|||
Norway |
MSMDI – Multi Species Maximum Depth Index |
0,80 |
0,60 |
Sweden |
MSMDI – Multi Species Maximum Depth Index |
0,80 |
0,60 |
NORTH EAST ATLANTIC GEOGRAPHICAL INTERCALIBRATION GROUP RESULTS |
|
Biological Quality Element |
Macroalgae and Angiosperms |
Sub-Biological Quality Element |
Macroalgae |
Intertidal blooming macroalgae soft bottom, indicative of abundance
Country and Type |
National classification systems intercalibrated |
Ecological Quality Ratios |
|
High-good boundary |
Good-moderate boundary |
||
Type NEA 1/26 |
|||
Germany |
OMAI – Opportunistic Macroalgae-cover/acreage on soft sediment intertidal in coastal waters |
0,78 |
0,59 |
France |
CWOGA – Macroalgal Bloom Assessment |
0,825 |
0,617 |
Ireland |
OGA tool – Opportunistic Green Macroalgal Abundance |
0,80 |
0,60 |
NORTH EAST ATLANTIC GEOGRAPHICAL INTERCALIBRATION GROUP RESULTS |
|
Biological Quality Element |
Macroalgae and Angiosperms |
Sub-Biological Quality Element |
Angiosperms |
Seagrasses
Country and Type |
National classification systems intercalibrated |
Ecological Quality Ratios |
|
High-good boundary |
Good-moderate boundary |
||
Type NEA 1/26 |
|||
Germany |
SG – Assessment tool for intertidal seagrass in coastal and transitional waters |
0,80 |
0,60 |
France |
SBQ – Seagrass beds quality in coastal and transitional water bodies |
0,80 |
0,645 |
Ireland |
Intertidal Seagrass tool |
0,80 |
0,61 |
Netherlands |
SG – Monitoring beds of SG per waterbody using aerial photographs, ground truth and specifying surface & density per species |
0,80 |
0,60 |
Portugal |
SQI – Seagrass quality index |
0,80 |
0,60 |
Type NEA 3/4 |
|
|
|
Germany |
SG – Bewertungssystem für Makroalgen und Seegräser der Küsten- und Übergangsgewässer zur Umsetzung der EG-Wasserrahmenrichtlinie in Deutschland |
0,80 |
0,60 |
Netherlands |
Monitoring beds of SG per waterbody using aerial photographs, ground truth and specifying surface and density per species |
0,80 |
0,60 |
NORTH EAST ATLANTIC GEOGRAPHICAL INTERCALIBRATION GROUP RESULTS |
|
Biological Quality Element |
Benthic invertebrate fauna |
Country and Type |
National classification systems intercalibrated |
Ecological Quality Ratios |
|
High-good boundary |
Good-moderate boundary |
||
Type NEA 1/26 |
|||
Belgium |
BEQI – Benthic Ecosystem Quality Index |
0,80 |
0,60 |
Denmark |
Danish Quality Index (DKI) |
0,80 |
0,60 |
Germany |
M-AMBI – Multivariate AZTI’s Marine Biotic Index |
0,85 |
0,70 |
France |
M-AMBI – Multivariate AZTI’s Marine Biotic Index |
0,77 |
0,53 |
Ireland |
IQI – Infaunal Quality Index |
0,75 |
0,64 |
Netherlands |
BEQI2 -Benthic Ecosystem Quality Index 2 |
0,80 |
0,60 |
Norway |
NQI – Norwegian Quality Index |
0,72 |
0,63 |
Portugal |
BAT – Benthic Assessment Tool |
0,79 |
0,58 |
Spain |
M-AMBI – Multivariate AZTI’s Marine Biotic Index |
0,77 |
0,63 |
Type NEA 3/4 |
|||
Germany |
M-AMBI – Multivariate AZTI’s Marine Biotic Index |
0,85 |
0,70 |
Netherlands |
BEQI2 – Benthic Ecosystem Quality Index 2 |
0,80 |
0,60 |
Type NEA 7 |
|||
Norway |
NQI – Norwegian Quality Index |
0,72 |
0,63 |
Type NEA 8b |
|||
Denmark |
Danish Quality Index (DKI) |
0,84 |
0,68 |
Sweden |
BQI – Swedish multimetric biological quality index (soft sediment infauna) |
0,71 |
0,54 |
Type NEA 8a/9/10 |
|||
Norway |
NQI – Norwegian Quality Index |
0,82 |
0,63 |
Sweden |
BQI – Swedish multimetric biological quality index (soft sediment infauna) |
0,71 |
0,54 |
Water category |
Coastal waters |
Geographical Intercalibration Group |
Mediterranean Sea |
Description of types that have been intercalibrated (for phytoplankton only)
Type |
Description |
Density (kg/m3) |
Annual mean salinity (psu) |
Type I |
Highly influenced by freshwater input |
< 25 |
< 34,5 |
Type IIA, IIA Adriatic |
Moderately influenced by freshwater input (continent influence) |
25 – 27 |
34,5 – 37,5 |
Type IIIW |
Continental coast, not influenced by freshwater input (Western Basin), |
> 27 |
> 37,5 |
Type IIIE |
Not influenced by freshwater input (Eastern Basin) |
> 27 |
> 37,5 |
Type Island-W* |
Island coast (Western Basin) |
All range |
All range |
MEDITERRANEAN SEA GEOGRAPHICAL INTERCALIBRATION GROUP RESULTS |
|
Biological Quality Element |
Phytoplankton |
Phytoplankton: parameter indicative of biomass parameter (Chlorophyll a)
Country and Type |
Ecological Quality Ratios |
Values (μg/l) |
||
High-good boundary |
Good-moderate boundary |
High-good boundary |
Good-moderate boundary |
|
Type II A |
||||
France |
0,67 |
0,37 |
1,92 |
3,50 |
Spain |
0,67 |
0,37 |
1,92 |
3,50 |
Type II A Adriatic |
||||
Croatia |
0,82 |
0,61 |
1,70 |
4,00 |
Italy |
0,82 |
0,61 |
1,70 |
4,00 |
Slovenia |
0,82 |
0,61 |
1,70 |
4,00 |
Type IIIW |
||||
France |
0,67 |
0,42 |
1,18 |
1,89 |
Spain |
0,67 |
0,42 |
1,18 |
1,89 |
Type IIIE |
||||
Cyprus |
0,66 |
0,37 |
0,29 |
0,53 |
Greece |
0,66 |
0,37 |
0,29 |
0,53 |
Malta |
0,66 |
0,37 |
0,29 |
0,53 |
MEDITERRANEAN SEA GEOGRAPHICAL INTERCALIBRATION GROUP RESULTS |
|
Biological Quality Element |
Macroalgae and Angiosperms |
Sub-Biological Quality Element |
Macroalgae |
Country |
National classification systems intercalibrated |
Ecological Quality Ratios |
|
High-good boundary |
Good-moderate boundary |
||
Cyprus |
EEI-c – Ecological Evaluation Index |
0,76 |
0,48 |
France |
CARLIT – Cartography of Littoral and upper-sublittoral rocky-shore communities |
0,75 |
0,60 |
Greece |
EEI-c – Ecological Evaluation Index |
0,76 |
0,48 |
Croatia |
CARLIT – Cartography of Littoral and upper-sublittoral rocky-shore communities |
0,75 |
0,60 |
Italy |
CARLIT – Cartography of Littoral and upper-sublittoral rocky-shore communities |
0,75 |
0,60 |
Malta |
CARLIT – Cartography of Littoral and upper-sublittoral rocky-shore communities |
0,75 |
0,60 |
Slovenia |
Metodologija vrednotenja ekološkega stanja obalnega morja na podlagi makroalg |
0,76 |
0,48 |
Spain |
CARLIT – Cartography of Littoral and upper-sublittoral rocky-shore communities |
0,75 |
0,60 |
MEDITERRANEAN SEA GEOGRAPHICAL INTERCALIBRATION GROUP RESULTS |
|
Biological Quality Element |
Macroalgae and Angiosperms |
Sub-Biological Quality Element |
Angiosperms |
Country |
National classification systems intercalibrated |
Ecological Quality Ratios |
|
High-good boundary |
Good-moderate boundary |
||
Croatia |
POMI – Posidonia oceanica Multivariate Index |
0,775 |
0,55 |
Cyprus |
PREI – Posidonia oceanica Rapid Easy Index |
0,775 |
0,55 |
France |
PREI – Posidonia oceanica Rapid Easy Index |
0,775 |
0,55 |
Greece |
WePOSI- Weighted Posidonia oceanica Index |
0,775 |
0,55 |
Italy |
PREI – Posidonia oceanica Rapid Easy Index |
0,775 |
0,55 |
Malta |
PREI – Posidonia oceanica Rapid Easy Index |
0,775 |
0,55 |
Spain |
POMI – Posidonia oceanica Multivariate Index |
0,775 |
0,55 |
Spain |
Valencian-CS |
0,775 |
0,55 |
MEDITERRANEAN SEA GEOGRAPHICAL INTERCALIBRATION GROUP RESULTS |
|
Biological Quality Element |
Benthic invertebrate fauna |
Biological Quality Element
Country |
National classification systems intercalibrated |
Ecological Quality Ratios |
|
High-good boundary |
Good-moderate boundary |
||
Italy |
M-AMBI – Multivariate AZTI’s Marine Biotic Index |
0,81 |
0,61 |
Slovenia |
Metodologija vrednotenja ekološkega stanja obalnega morja na podlagi bentoških nevretenčarjev |
0,83 |
0,62 |
Croatia |
M-AMBI – Multivariate AZTI’s Marine Biotic Index |
0,83 |
0,62 |
Cyprus |
Bentix |
0,75 |
0,58 |
France |
AMBI |
0,83 |
0,58 |
Greece |
Bentix |
0,75 |
0,58 |
Malta |
Bentix |
0,75 |
0,58 |
Spain |
BOPA |
0,95 |
0,54 |
Spain |
MEDOCC |
0,73 |
0,47 |
Water category |
Coastal waters |
Geographical Intercalibration Group |
Black Sea |
Description of types that have been intercalibrated
Type |
Description |
CW-BL1 |
Mesohaline, microtidal (< 1 m), shallow (< 30 m), moderately exposed to very exposed, mixed substratum (fine sand for zoobenthos) |
Countries sharing types that have been intercalibrated
:
Bulgaria and Romania
BLACK SEA GEOGRAPHICAL INTERCALIBRATION GROUP RESULTS |
|
Biological Quality Element |
Phytoplankton |
Country |
National classification systems intercalibrated |
Ecological Quality Ratios |
|
High-good boundary |
Good-moderate boundary |
||
Bulgaria |
IBI |
0,80 |
0,63 |
Romania |
IBI |
0,80 |
0,63 |
BLACK SEA GEOGRAPHICAL INTERCALIBRATION GROUP RESULTS |
|
Biological Quality Element |
Macroalgae and Angiosperms |
Country |
National classification systems intercalibrated |
Ecological Quality Ratios |
|
High-good boundary |
Good-moderate boundary |
||
Bulgaria |
EI-Ecological index |
0,837 |
0,644 |
Romania |
EI-Ecological index |
0,837 |
0,644 |
BLACK SEA GEOGRAPHICAL INTERCALIBRATION GROUP RESULTS |
|
Biological Quality Element |
Benthic Invertebrate fauna |
Country |
National classification systems intercalibrated |
Ecological Quality Ratios |
|
High-good boundary |
Good-moderate boundary |
||
Bulgaria |
M-AMBI(n) – Multivariate AZTI’s Marine Biotic Index Normalized |
0,90 |
0,68 |
Romania |
M-AMBI(n) – Multivariate AZTI’s Marine Biotic Index Normalized |
0,90 |
0,68 |
Water category |
Transitional waters |
Geographical Intercalibration Group |
Baltic Sea GIG |
Description of types that have been intercalibrated
Type |
Surface salinity psu |
Bottom salinity (psu) |
Exposure |
Ice days |
Other Characteristics |
BT1 |
0 – 8 Oligohaline |
0 – 8 |
Very sheltered |
- |
Polish Vistula lagoon and Lithuanian Curonian lagoon |
BALTIC SEA GEOGRAPHICAL INTERCALIBRATION GROUP RESULTS |
|
Biological Quality Element |
Phytoplankton |
Results for parameter indicative of biomass (Chrophyll a)
Country |
Ecological Quality Ratios |
Values (μg/l) |
||
High-good boundary |
Good-moderate boundary |
High-good boundary |
Good-moderate boundary |
|
Lithuania |
0,83 |
0,57 |
31,70 |
46,60 |
Poland |
0,77 |
0,61 |
33,46 |
42,20 |
Water category |
Transitional waters |
Geographical Intercalibration Group |
North East Atlantic |
Description of types that have been intercalibrated
Type |
Characterisation |
Salinity (psu), Tidal range (m), Depth (m) |
Current Velocity (knots), Exposure |
Mixing Residence Time |
NEA 11 |
Transitional Waters |
0 – 35 Micro to macrotidal < 30 |
Variable Sheltered or moderately exposed |
Partly permanently stratified Days to weeks |
Description of sub common intercalibration types for Biological quality element Benthic Invertebrate Fauna:
Sub type |
Characterisation |
MS sharing sub-type |
A |
Lagoons |
Ireland, Spain |
B |
Freshwater-oligohaline, medium river flow |
Ireland, Spain |
C |
Mesotidal estuary with irregular river flow |
Portugal, Spain |
D |
Large estuaries |
Germany, France, Ireland, Netherlands, Portugal, Spain |
E |
Small-medium estuary with > 50 % intertidal area |
France, Ireland, Germany, Spain |
F |
Small-medium estuary with < 50 % intertidal area |
France, Ireland, Portugal, Spain |
NORTH EAST ATLANTIC GEOGRAPHICAL INTERCALIBRATION GROUP RESULTS |
|
Biological Quality Element: |
Phytoplankton |
Phytoplankton: parameter indicative of biomass parameter (Chlorophyll a)
Country |
Ecological Quality Ratios |
Values (μg/l) |
||
High-good boundary |
Good-moderate boundary |
High-good boundary |
Good-moderate boundary |
|
France |
0,67 |
0,397 |
5,33 |
8,88 |
Ireland |
0,80 |
0,60 |
12,96 |
25,96 |
Netherlands |
0,80 |
0,60 |
12,00 |
18,00 |
Portugal-North |
0,667 |
0,467 |
10,000 |
14,288 |
Spain – Central Cantabrian and Galician estuaries – Mixing zone (*2) |
0,67 |
0,44 |
8,00 |
12,00 |
Spain – Central Cantabrian and Galician estuaries – Euhaline (*2) |
0,67 |
0,33 |
4,00 |
8,00 |
Spain – East Cantabrian estuaries – Euhaline (*2) |
0,67 |
0,33 |
1,95 |
3,90 |
Spain – East Cantabrian estuaries – Polyhaline (*2) |
0,67 |
0,33 |
3,30 |
6,60 |
Spain – East Cantabrian estuaries – Mesohaline (*2) |
0,67 |
0,33 |
5,10 |
10,20 |
Spain – East Cantabrian estuaries – Oligohaline (*2) |
0,67 |
0,33 |
6,60 |
13,20 |
Spain – Gulf of Cádiz estuaries – Mixing zone |
0,67 |
0,33 |
3,75 |
7,50 |
Spain – Gulf of Cádiz estuaries – Euhaline (*2) |
0,67 |
0,33 |
3,00 |
6,00 |
NORTH EAST ATLANTIC GEOGRAPHICAL INTERCALIBRATION GROUP RESULTS |
|
Biological Quality Element: |
Macroalgae and Angiosperms |
Sub-Biological Quality Element |
Macroalgae |
Intertidal blooming macroalgae soft bottom, indicative of abundance
Country |
National classification systems intercalibrated |
Ecological Quality Ratios |
|
High-good boundary |
Good-moderate boundary |
||
France |
TWOGA – Macroalgal Bloom Assessment |
0,80 |
0,60 |
Ireland |
OGA Tool – Opportunistic Green Macroalgal Abundance |
0,80 |
0,60 |
Portugal |
BMI-Blooming macroalgae Index |
0,770 |
0,590 |
NORTH EAST ATLANTIC GEOGRAPHICAL INTERCALIBRATION GROUP RESULTS |
|
Biological Quality Element: |
Macroalgae and Angiosperms |
Sub-Biological Quality Element |
Angiosperms |
Seagrasses
Country |
National classification systems intercalibrated |
Ecological Quality Ratios |
|
High-good boundary |
Good-moderate boundary |
||
Germany |
SG-Assessment tool for intertidal seagrass in coastal and transitional waters |
0,80 |
0,60 |
France |
SBQ-Seagrass beds quality in coastal and transitional water bodies |
0,80 |
0,645 |
Ireland |
Intertidal Seagrass tool |
0,80 |
0,61 |
Netherlands |
SG- Monitoring beds of SG per waterbody using aerial photographs, ground truth and specifying surface & density per species |
0,80 |
0,60 |
Portugal |
SQI-Seagrass quality index |
0,800 |
0,600 |
NORTH EAST ATLANTIC GEOGRAPHICAL INTERCALIBRATION GROUP RESULTS |
|
Biological Quality Element: |
Macroalgae and Angiosperms |
Sub-Biological Quality Element |
Angiosperms |
Saltmarshes
Country |
National classification systems intercalibrated |
Ecological Quality Ratios |
|
High-good boundary |
Good-moderate boundary |
||
France |
|
|
|
Spain – Cantabria |
AQI – Angiosperm Quality Index |
0,88 |
0,73 |
Portugal |
AQuA – Angiosperm Quality Assessment Index |
0,800 |
0,600 |
Country |
National classification systems intercalibrated |
Ecological Quality Ratios |
|
High-good boundary |
Good-moderate boundary |
||
Sub type D |
|||
France |
BEQI-FR |
0,870 |
0,670 |
Germany |
M-AMBI – Multivariate AZTI’s Marine Biotic Index |
0,850 |
0,700 |
Netherlands |
BEQI2 – Benthic Ecosystem Quality Index 2 |
0,800 |
0,600 |
Spain |
M-AMBI – Multivariate AZTI’s Marine Biotic Index |
0,770 |
0,530 |
Portugal |
BAT – Benthic Assessment Tool |
0,84 |
0,60 |
Sub type E |
|||
France |
BEQI-FR |
0,830 |
0,620 |
Spain |
M-AMBI – Multivariate AZTI’s Marine Biotic Index |
0,770 |
0,530 |
Spain |
QSB – Quality of Soft Bottoms |
0,800 |
0,600 |
Sub type F |
|||
France |
BEQI-FR |
0,840 |
0,630 |
Spain |
M-AMBI – Multivariate AZTI’s Marine Biotic Index |
0,770 |
0,530 |
Portugal |
BAT- Benthic Assessment Tool |
0,79 |
0,580 |
NORTH EAST ATLANTIC GEOGRAPHICAL INTERCALIBRATION GROUP RESULTS |
|
Biological Quality Element: |
Fish fauna |
Country |
National classification systems intercalibrated |
Ecological Quality Ratios |
|
High-good boundary |
Good-moderate boundary |
||
Belgium |
EBI – Zeeschelde Estuarine Biotic Index |
0,850 |
0,615 |
France |
ELFI – Estuarine and Lagoon Fish Index |
0,910 |
0,675 |
Germany |
FAT – TW – Fischbasiertes Bewertungswerkzeug für Übergangsgewässer der norddeutschen Ästuare |
0,840 |
0,620 |
Ireland |
TFCI – Transitional Fish Classification Index |
0,810 |
0,580 |
Ireland |
EMFI – Estuarine Multi-metric Fish Index |
0,920 |
0,650 |
Netherlands |
FAT – TW – WFD Fish index for transitional waters. type O2 |
0,800 |
0,600 |
Portugal |
EFAI – Estuarine Fish Assessment Index |
0,865 |
0,700 |
Spain |
AFI – AZTI’s Fish Index |
0,780 |
0,550 |
Spain |
TFCI – Transitional Fish Classification Index |
0,900 |
0,650 |
Water category |
Transitional waters |
Geographical Intercalibration Group |
Mediterranean Sea |
Description of types that have been intercalibrated
Common IC type |
Type characteristics |
MS sharing IC common type |
CL-Oligohaline |
Coastal lagoons (Salinity < 5 psu) |
Spain, France, Italy |
CL-Mesohaline chocked and restricted |
Coastal lagoons (Salinity 5 – 18 psu) |
|
CL-Polyhaline chocked and restricted |
Coastal lagoons (Salinity 18 – 40 psu) |
|
Hyperhalines (Salinity > 40 psu), |
Hyperhalines (Salinity > 40 psu) |
Spain |
Estuaries |
Estuaries (salt wedge type) |
Spain, Croatia |
MEDITERRANEAN SEA GEOGRAPHICAL INTERCALIBRATION GROUP RESULTS |
|
Biological Quality Element: |
Phytoplankton |
Country and type |
National classification systems intercalibrated |
Ecological Quality Ratios |
|
High-good boundary |
Good-moderate boundary |
||
Coastal lagoons Polyhaline chocked |
|||
France |
PhIL – Phytoplankton index for Mediterranean polyhaline lagoons |
0,710 |
0,390 |
Greece |
MPI – Multimetric Phytoplankton Index |
0,780 |
0,510 |
Italy |
MPI – Multimetric Phytoplankton Index |
0,780 |
0,510 |
Coastal lagoons Polyhaline restricted |
|||
France |
PhIL – Phytoplankton index for Mediterranean polyhaline lagoons |
0,710 |
0,390 |
Greece |
MPI – Multimetric Phytoplankton Index |
0,820 |
0,540 |
Italy |
MPI – Multimetric Phytoplankton Index |
0,820 |
0,540 |
MEDITERRANEAN SEA GEOGRAPHICAL INTERCALIBRATION GROUP RESULTS |
|
Biological Quality Element: |
Macroalgae and Angiosperms |
Country and Type |
National classification systems intercalibrated |
Ecological Quality Ratios |
|
High-good boundary |
Good-moderate boundary |
||
Meso. poly and euhaline coastal lagoons (> 5 ‰) either chocked or restricted |
|||
France |
Exclame |
0,8 |
0,6 |
Greece |
EEI-c – Ecological Evaluation Index |
0,7 |
0,4 |
Italy |
MaQI – Macrophyte Quality Index |
0,8 |
0,6 |
MEDITERRANEAN SEA GEOGRAPHICAL INTERCALIBRATION GROUP RESULTS |
|
Biological Quality Element: |
Benthic invertebrate fauna |
Country and Type |
National classification systems intercalibrated |
Ecological Quality Ratios |
|
High-good boundary |
Good-moderate boundary |
||
Coastal lagoons Polyhaline restricted |
|||
France |
M-AMBI – Multivariate AZTI’s Marine Biotic Index |
0,84 |
0,63 |
Italy |
M-AMBI – Multivariate AZTI’s Marine Biotic Index |
0,96 |
0,71 |
Greece |
M-AMBI – Multivariate AZTI’s Marine Biotic Index |
0,83 |
0,62 |
Coastal lagoons-Mesohaline chocked and restricted |
|||
Italy |
M-AMBI – Multivariate AZTI’s Marine Biotic Index |
- |
0,71 |
Greece |
M-AMBI – Multivariate AZTI’s Marine Biotic Index |
- |
0,62 |
Part 2
Water category |
Rivers |
Geographical Intercalibration Group |
Cross-GIG |
Biological Quality Element |
Fish fauna |
Ecological quality ratios of national classification methods
Country |
National classification systems intercalibrated |
Ecological Quality Ratios |
|
High-Good boundary |
Good-Moderate boundary |
||
Danubian group |
|||
Hungary |
Hungarian Multimetric Fish Index HMMFI |
0,80 |
0,60 |
Mediterranean group |
|||
Bulgaria |
TsBRI (Type Specific Bulgarian Fish Index) |
0,860 |
0,650 |
Italy |
NISECI index (New Index of Ecological Status of Fish Communities) |
0,80 |
0,60 |
Water category |
Rivers |
Geographical Intercalibration Group |
Cross-GIG Very Large Rivers |
Biological Quality Element |
Macrophytes and Phytobenthos |
Sub-biological Quality Element |
Phytobenthos |
Ecological quality ratios of national classification methods intercalibrated
–
Type R-L2
Country |
National classification systems intercalibrated |
Ecological Quality Ratios |
|
High-Good boundary |
Good-Moderate boundary |
||
Belgium (Flanders) |
PISIAD index (Proportions of Impact-Sensitive and Impact-Associated Diatoms) |
0,80 |
0,60 |
Water category |
Lakes |
Geographical Intercalibration Group |
Alpine lakes |
Biological Quality Element |
Benthic invertebrates |
Country |
National classification systems |
Ecological Quality Ratios |
|
High-good boundary |
Good-moderate boundary |
||
Italy |
BQIES (Benthic Quality Index Expected Species number) |
0,88 |
0,76 |
Biological Quality Element |
Fish fauna |
Country |
National classification systems |
Ecological Quality Ratios |
|
High-good boundary |
Good-moderate boundary |
||
France |
ELFI (European Lake Fish Index): Indice Ichtyofaune Lacustre (IIL) |
0,73 |
0,49 |
Water category |
Lakes |
Geographical Intercalibration Group |
Central-Baltic lakes |
Biological Quality Element |
Phytoplankton |
Country |
National classification methods |
Ecological Quality Ratios |
|
High-good boundary |
Good-moderate boundary |
||
France |
Phytoplankton Index for Lakes (IPLAC): Indice Phytoplancton Lacustre |
0,80 |
0,60 |
Biological Quality Element |
Macrophytes and Phytobenthos |
Sub-biological Quality Element |
Macrophytes |
Country |
National classification methods |
Ecological Quality Ratios |
|
High-good boundary |
Good-moderate boundary |
||
France |
French Macrophyte Index for Lakes (IBML): Indice Biologique Macrophytique en Lacs |
0,80 |
0,60 |
Biological Quality Element |
Fish fauna |
Country |
National classification methods |
Ecological Quality Ratios |
|
High-good boundary |
Good-moderate boundary |
||
Belgium (Flanders) |
Fish-based index for lakes and reservoirs in Flanders (Belgium) |
0,80 |
0,60 |
Water category |
Lakes |
Geographical Intercalibration Group |
Mediterranean lakes |
Biological Quality Element |
Phytoplankton |
Country |
National classification methods |
Ecological Quality Ratios |
|
High-good boundary |
Good-moderate boundary |
||
Croatia |
Hungarian lake phytoplankton index (HLPI) |
0,80 |
0,60 |
France |
Phytoplankton Index for Lakes (IPLAC): Indice Phytoplancton Lacustre |
0,80 |
0,60 |
Greece |
HeLPhy – Hellenic Lake Phytoplankton Assessment Method |
0,80 |
0,60 |
Italy |
Italian phytoplankton assessment method (IPAM) |
0,80 |
0,60 |
Biological Quality Element |
Macrophytes and Phytobenthos |
Sub-biological Quality Element |
Macrophytes |
Country |
National classification methods |
Ecological Quality Ratios |
|
High-good boundary |
Good-moderate boundary |
||
Croatia |
Biocenological index (BMHR) |
0,90 |
0,70 |
France |
French Macrophyte Index for Lakes (IBML): Indice Biologique Macrophytique en Lacs |
0,80 |
0,60 |
Greece |
HeLM – Hellenic Lake Macrophytes Assessment Method |
0,80 |
0,60 |
Italy |
VLMMI – Volcanic Lakes Multimetric Macrophyte Index |
0,70 |
0,50 |
Spain |
Spanish Macrophyte method to assess the ecological status of Lakes OFALAM 1: Coverage of eutrophic macrophytes National lake types: L-T01, L-T02, L-T03, L-T04, L-T05, L-T06, L-T07, L-T08, L-T10, L-T11, L-T12, L-T14, L-T15, L-T16, L-T17, L-T18, L-T19, L-T20, L-T21, L-T22, L-T23, L-T24, L-T25, L-T26, L-T2, L-T28, L-T29 |
0,99 |
0,90 |
Spain |
Spanish Macrophyte method to assess the ecological status of Lakes OFALAM 2: Exotic macrophytes coverage National lake types: L-T01, L-T02, L-T03, L-T04, L-T05, L-T06, L-T07, L-T08, L-T10, L-T11, L-T12, L-T14, L-T15, L-T16, L-T17, L-T18, L-T19, L-T20, L-T21, L-T22, L-T23, L-T24, L-T25, L-T26, L-T2, L-T28, L-T29 |
1,00 |
0,95 |
Spain |
Spanish Macrophyte method to assess the ecological status of Lakes OFALAM 3 National lake types (specifying the applied metric) |
|
|
Total cover of hydrophytes |
|
|
|
L-T10, L-T14, L-T15, L-T16, L-T25 |
0,83 |
0,55 |
|
L-T11 |
0,86 |
0,57 |
|
L-T18 |
0,88 |
0,62 |
|
L-T20, L-T21, L-T22, L-T23, L-T29 |
0,92 |
0,61 |
|
L-T12, L-T24, L-T26, L-T27, L-T28 |
0,94 |
0,62 |
|
Presence/absence of hydrophytes |
|
|
|
L-T01, L-T02, L-T03, L-T04, L-T05, L-T06, L-T07, L-T08 |
Presence |
Absence |
|
Spain |
Spanish Macrophyte method to assess the ecological status of Lakes OFALAM 4 National lake types (specifying the applied metric): |
|
|
Helophytes coverage |
|
|
|
L-T20, L-T21, L-T22, L-T23 |
0,86 |
0,50 |
|
L-T12, L-T14, L-T15, L-T25, L-T29 |
0,88 |
0,75 |
|
L-T10, L-T11, L-T16, L-T18, L-T24, L-T26, L-T27, L-T28 |
0,90 |
0,75 |
|
Total coverage of macrophytes |
|
|
|
L-T17 |
0,90 |
0,75 |
|
L-T19 |
0,83 |
0,55 |
|
Spain |
Spanish Macrophyte method to assess the ecological status of Lakes OFALAM 5: Macrophytes richness National lake types: |
|
|
L-T18; L-T25 |
- |
0,48 |
|
L-T16, L-T17, L-T19 |
- |
0,50 |
|
L-T27, L-T28 |
- |
0,53 |
|
L-T29 |
- |
0,56 |
|
L-T24 |
- |
0,60 |
|
L-T11; L-T26 |
- |
0,62 |
|
L-T10 |
- |
0,64 |
|
L-T12 |
- |
0,70 |
|
L-T14, L-T15 |
- |
0,78 |
Biological Quality Element |
Benthic invertebrates |
Country |
National classification methods |
Ecological Quality Ratios |
|
High-good boundary |
Good-moderate boundary |
||
Croatia |
Croatian lake benthic macroinvertebrates classification method |
0,80 |
0,60 |
Greece |
GLBiI – Greek Lake Benthic invertebrate Index |
0,80 |
0,60 |
Greece |
HeLLBI – Hellenic assessment method for Lake Littoral Benthic invertebrate fauna |
0,80 |
0,60 |
Italy |
BQIES (Benthic Quality Index Expected Species number) |
0,88 |
0,76 |
Spain |
Spanish Invertebrates Index for Lakes IBCAEL National lake types |
|
|
L-T01, L-T02, L-T03, L-T04, L-T05, L-T09 |
0,92 |
0,69 |
|
L-T06, L-T07, L-T08, L-T10, L-T11, L-T12 |
0,93 |
0,69 |
|
L-T13, L-T17, L-T30 |
0,89 |
0,68 |
|
L-T14, L-T15, L-T24, L-T25, L-T26, L-T27, L-T29 |
0,78 |
0,59 |
|
L-T16, L-T18 |
0,86 |
0,58 |
|
L-T19, L-T21 |
0,80 |
0,60 |
|
L-T20, L-T28 |
0,80 |
0,60 |
|
L-T22 |
0,9 |
0,67 |
|
L-T23 |
0,84 |
0,63 |
|
Spain |
QAELS2010 index |
|
|
shallow permanent ponds |
0,86 |
0,58 |
|
shallow temporary ponds |
0,89 |
0,68 |
Biological Quality Element |
Fish fauna |
Country |
National classification methods |
Ecological Quality Ratios |
|
High-good boundary |
Good-moderate boundary |
||
Croatia |
Croatian fish index for natural lakes (CFIL) |
0,80 |
0,60 |
France |
ELFI (European Lake Fish Index): Indice Ichtyofaune Lacustre (IIL) |
0,73 |
0,49 |
Greece |
GLFI – Greek Lake Fish Index |
0,80 |
0,60 |
Italy |
Lake Fish Index (LFI) |
0,82 |
0,64 |
Water category |
Lakes |
Geographical Intercalibration Group |
Eastern Continental lakes |
Biological Quality Element |
Macrophytes and phytobenthos |
Sub-biological Quality Element |
Phytobenthos |
Country |
National classification methods |
Ecological Quality Ratios |
|
High-good boundary |
Good-moderate boundary |
||
Romania |
RO-AMLP – Romanian Assessment Method for Natural Lakes Ecological Status based on Phytobenthos (Diatoms) |
0,80 |
0,60 |
Biological Quality Element |
Fish fauna |
Country |
National classification methods |
Ecological Quality Ratios |
|
High-good boundary |
Good-moderate boundary |
||
Bulgaria |
Bulgarian fish based method for ecological classification and monitoring of lakes |
0,76 |
0,52 |
Hungary |
Hungarian Multimetric Fish Index for Oxbow lakes (HMMFIfO) |
0,80 |
0,60 |
Hungary |
The Balaton fish index (BFI) |
0,80 |
0,60 |
Water category |
Coastal waters |
Geographical Intercalibration Group |
Baltic Sea |
Biological Quality Element |
Phytoplankton |
Phytoplankton: parameter indicative of biomass parameter (Chlorophyll a)
Country and Type |
Ecological Quality Ratios |
Values (μg/l) |
||
High-good boundary |
Good-moderate boundary |
High-good boundary |
Good-moderate boundary |
|
BC2 (including German national types B1. B2a. B2b) |
||||
Germany (B1) |
0,91 |
0,67 |
9,30 |
12,70 |
Germany (B2a) |
0,89 |
0,67 |
1,80 |
2,40 |
Germany (B2b) |
0,93 |
0,67 |
1,40 |
1,95 |
Biological Quality Element |
Macroalgae and Angiosperms |
Country and Type |
National classification systems |
Ecological Quality Ratios |
|
High-good boundary |
Good-moderate boundary |
||
BC2 |
|||
Germany |
PHYBIBCO – PHYtoBenthic Index for Baltic inner coastal waters |
0,80 |
0,60 |
BC1 |
|||
Finland |
Fucus depth limit(macroalgae) |
0,90 |
0,74 |
Sweden |
MSMDI (macroalgae and angiosperms) |
0,60 |
0,40 |
BC6 |
|||
Denmark |
Depth limit of angiosperms |
0,90 |
0,74 |
Sweden |
MSMDI (macroalgae and angiosperms) |
0,60 |
0,40 |
BC7 |
|||
Germany |
Balcosis – Baltic ALgae COmmunity AnalySIs System (macroalgae and angiosperms) |
0,80 |
0,60 |
Poland |
MQAI – Macrophyte Quality Assessment Index |
0,90 |
0,70 |
BC8 |
|||
Germany |
Balcosis – Baltic ALgae COmmunity AnalySIs System (macroalgae and angiosperms) |
0,80 |
0,60 |
Denmark |
Depth limit of angiosperms |
0,90 |
0,74 |
Biological Quality Element |
Benthic Invertebrate fauna |
Country and Type |
National classification systems |
Ecological Quality Ratios |
|
High-good boundary |
Good-moderate boundary |
||
BC2 |
|||
Germany |
MarBIT- Marine Biotic Index Tool |
0,80 |
0,60 |
BC4 |
|||
Estonia |
ZKI – Estonian coastal water macrozoobenthos community index |
0,39 |
0,24 |
Latvia |
BQI – Benthic quality index |
0,88 |
0,75 |
Water category |
Coastal waters |
Geographical Intercalibration Group |
North East Atlantic |
Biological Quality Element |
Phytoplankton |
Phytoplankton: parameter indicative of biomass parameter (Chlorophyll a)
Country and Type |
Ecological Quality Ratios |
Values (μg/l) |
||
High-good boundary |
Good-moderate boundary |
High-good boundary |
Good-moderate boundary |
|
NEA 1/26d |
||||
Denmark |
0,66 |
0,50 |
3,00 |
4,00 |
NEA 5 |
||||
Germany |
0,67 |
0,44 |
5,00 |
7,50 |
NEA 7 |
||||
Norway |
0,67 |
0,33 |
2,50 |
5,00 |
Biological Quality Element |
Macroalgae and Angiosperms |
Sub-Biological Quality Element |
Macroalgae |
Intertidal or subtidal macroalgae rocky bottom
Country and Type |
National classification systems |
Ecological Quality Ratios |
|
High-good boundary |
Good-moderate boundary |
||
Type NEA 5 |
|||
Germany |
HPI – Helgoland Phytobenthic Index |
0,80 |
0,60 |
Biological Quality Element |
Macroalgae and Angiosperms |
Sub-Biological Quality Element |
Macroalgae |
Intertidal blooming macroalgae soft bottom, indicative of abundance
Country |
National classification systems |
Ecological Quality Ratios |
|
High-good boundary |
Good-moderate boundary |
||
NEA 3/4 |
|||
Germany |
OMAI – Opportunistic Macroalgae-cover/acreage on soft sediment intertidal in coastal waters |
0,80 |
0,60 |
Biological Quality Element |
Macroalgae and Angiosperms |
Sub-Biological Quality Element |
Angiosperms |
Saltmarshes
Country |
National classification systems |
Ecological Quality Ratios |
|
High-good boundary |
Good-moderate boundary |
||
Germany |
EM – Assessment of saltmarsh vegetation in coastal and transitional waters |
0,80 |
0,60 |
Ireland |
SMAATIE – Saltmarsh Angiosperm Assessment Tool for Ireland |
0,80 |
0,60 |
Netherlands |
TSM – WFD-metrics for natural watertypes: tidal salt marsh |
0,80 |
0,60 |
Biological Quality Element |
Macroalgae and Angiosperms |
Country and Type |
National classification systems |
Ecological Quality Ratios |
|
High-good boundary |
Good-moderate boundary |
||
Type NEA 8b |
|||
Sweden |
MSMDI (macroalgae and angiosperms) |
0,80 |
0,60 |
Denmark |
Depth limit of angiosperms |
0,90 |
0,74 |
Biological Quality Element |
Benthic Invertebrate fauna |
Country and Type |
National classification systems |
Ecological Quality Ratios |
|
High-good boundary |
Good-moderate boundary |
||
Type NEA 1/26 |
|||
Portugal |
RAT – Rocky Shore Assessment Tool |
0,800 |
0,600 |
Spain |
BO2A – Benthic Opportunistic polychaetes/amphipods index |
0,83 |
0,50 |
Type NEA 5* |
|||
Germany |
MarBIT – Marine Biotic Index Tool |
0,80 |
0,60 |
Water category |
Coastal waters |
Geographical Intercalibration Group |
Mediterranean Sea |
Biological Quality Element |
Phytoplankton |
Phytoplankton: parameter indicative of biomass parameter (Chlorophyll a)
Country and Type |
Ecological Quality Ratios |
Values (μg/l) |
||
High-good boundary |
Good-moderate boundary |
High-good boundary |
Good-moderate boundary |
|
Type I |
||||
France |
0,670 |
0,330 |
4,925 |
10,000 |
Italy |
0,850 |
0,620 |
5,600 |
14,100 |
Type II A Tyrrhenian |
|
|
|
|
Italy |
0,84 |
0,62 |
1,17 |
2,90 |
Type III W Adriatic |
||||
Italy |
|
|
|
1,7 (*4) |
Croatia |
|
|
|
1,7 (*4) |
Type III W Tyrrhenian |
||||
Italy |
|
|
|
1,17 (*4) |
Biological Quality Element |
Macroalgae and Angiosperms |
Sub-Biological Quality Element |
Angiosperms |
Country |
National classification systems |
Ecological Quality Ratios |
|
High-good boundary |
Good-moderate boundary |
||
Greece |
CymoSkew |
0,75 |
0,50 |
Water category |
Transitional waters |
Geographical Intercalibration Group |
Baltic Sea |
Biological Quality Element |
Phytoplankton |
Phytoplankton: parameter indicative of biomass parameter (Chlorophyll a)
Country |
Ecological Quality Ratios |
Values (μg/l) |
||
High-good boundary |
Good-moderate boundary |
High-good boundary |
Good-moderate boundary |
|
Latvia |
0,83 |
0,67 |
2,4 |
3,0 |
Biological Quality Element |
Macroalgae and Angiosperms |
Sub-Biological Quality Element |
Angiosperms |
Country |
National classification systems |
Ecological Quality Ratios |
|
High-good boundary |
Good-moderate boundary |
||
Latvia |
Not applicable |
||
Poland |
ESMIz-Ecological State Macrophyte index for lagoon |
0,68 |
0,41 |
Biological Quality Element |
Benthic Invertebrate fauna |
Country |
National classification systems |
Ecological Quality Ratios |
|
High-good boundary |
Good-moderate boundary |
||
Latvia |
BQI-Benthic Quality Index |
0,784 |
0,588 |
Poland |
B-Macrozoobenthos BQE assessment by multimetric index |
0,765 |
0,647 |
Biological Quality Element |
Fish fauna |
Country |
National classification systems |
Ecological Quality Ratios |
|
High-good boundary |
Good-moderate boundary |
||
Poland |
PMFI-Polish Multimetric Fish Index |
0,80 |
0,60 |
Water category |
Transitional waters |
Geographical Intercalibration Group |
North East Atlantic |
Biological Quality Element |
Phytoplankton |
Phytoplankton: parameter indicative of biomass parameter (Chlorophyll a)
Country |
Ecological Quality Ratios |
Values (μg/l) |
||
High-good boundary |
Good-moderate boundary |
High-good boundary |
Good-moderate boundary |
|
Belgium |
1,00 |
0,60 |
100 |
200 |
Biological Quality Element |
Macroalgae and Angiosperms |
Sub-Biological Quality Element |
Angiosperms |
Saltmarshes
Country |
National classification systems |
Ecological Quality Ratios |
|
High-good boundary |
Good-moderate boundary |
||
Belgium |
TMQI -Tidal Marsh Quality Index |
0,85 |
0,75 |
Germany |
EM – Assessment of saltmarsh vegetation in coastal and transitional waters |
0,80 |
0,60 |
Ireland |
SMAATIE – Saltmarsh Angiosperm Assessment Tool for Ireland |
0,80 |
0,60 |
Netherlands |
TSM – WFD-metrics for natural watertypes: tidal salt marsh |
0,80 |
0,60 |
Biological Quality Element |
Macroalgae and Angiosperms |
Sub-Biological Quality Element |
Angiosperms |
Seagrasses
Country |
National classification systems |
Ecological Quality Ratios |
|
High-good boundary |
Good-moderate boundary |
||
Spain – Cantabria |
AQI – Angiosperms Quality Index |
0,850 |
0,700 |
Biological Quality Element |
Benthic Invertebrate fauna |
Country and Type |
National classification systems |
Ecological Quality Ratios |
|
High-good boundary |
Good-moderate boundary |
||
Belgium |
BEQI – Benthic Ecosystem Quality Index |
0,75 |
0,5 |
Sub type D |
|||
Germany |
AeTV – Aestuar Type Verfahren |
0,80 |
0,60 |
Ireland |
IQI – Infaunal Quality Index |
0,75 |
0,64 |
Spain |
TasBEM – Taxonomically Sufficient Benthic Multimetric |
0,79 |
0,66 |
Sub type E |
|||
Germany |
AeTV – Aestuar Type Verfahren |
0,80 |
0,60 |
Germany |
M-AMBI |
0,85 |
0,70 |
Ireland |
IQI – Infaunal Quality Index |
0,75 |
0,64 |
Spain |
TasBEM – Taxonomically Sufficient Benthic Multimetric |
0,79 |
0,66 |
Sub type F |
|||
Ireland |
IQI – Infaunal Quality Index |
0,75 |
0,64 |
Spain |
TasBEM – Taxonomically Sufficient Benthic Multimetric |
0,79 |
0,66 |
Water category |
Transitional waters |
Geographical Intercalibration Group |
Mediterranean Sea |
Biological Quality Element |
Phytoplankton |
Country and Type |
National classification systems |
Ecological Quality Ratios |
|
High-good boundary |
Good-moderate boundary |
||
Coastal lagoons oligohaline and mesohaline |
|||
Spain (Balearic Islands) |
FITOHMIB |
0,93 |
0,73 |
Estuaries |
|||
Spain (Southern Coast) |
TWIf – Phytoplankton index for transitional waters |
0,50 |
0,36 |
Croatia |
MPI – Multimetric Phytoplankton Index |
0,80 |
0,60 |
Biological Quality Element |
Macroalgae and Angiosperms |
Sub Biological Quality Element |
Angiosperms |
Country and Type |
National classification systems |
Ecological Quality Ratios |
|
High-good boundary |
Good-moderate boundary |
||
Estuaries |
|||
Croatia |
ZonoMI index – Zostera noltei multivariate index |
0,775 |
0,550 |
Biological Quality Element |
Benthic invertebrate fauna |
Country and Type |
National classification systems |
Ecological Quality Ratios |
|
High-good boundary |
Good-moderate boundary |
||
Coastal lagoons Oligohaline. Mesohaline and Polyhaline |
|||
Spain (Balearic Islands) |
INVHMIB |
0,93 |
0,73 |
Coastal lagoons Oligohaline |
|||
Spain (Northeastern Coast) |
QAELS |
0,86 |
0,58 |
Coastal lagoons Mesohaline |
|||
Spain (Northeastern Coast) |
QAELS |
0,72 |
0,62 |
Estuarie s |
|||
Croatia |
AMBI |
0,80 |
0,60 |
Spain (without salt wedge – Southern Coast) |
BO2A |
0,87 |
0,45 |
Spain (with salt wedge – Southern Coast) |
BO2A |
0,87 |
0,52 |
Biological Quality Element |
Fish fauna |
Country |
National classification systems |
Ecological Quality Ratios |
|
High-good boundary |
Good-moderate boundary |
||
Coastal lagoons Mesohaline and Polyhaline chocked and restricted |
|||
Italy |
HFBI – Habitat Fish Bio-Indicator |
0,94 |
0,55 |
Estuaries |
|||
Croatia |
M-EFI – Modified Estuarine Fish Index |
0,80 |
0,60 |
Water category |
Transitional waters |
Geographical Intercalibration Group |
Black Sea |
Biological Quality Element |
Phytoplankton |
Country |
National classification systems |
Ecological Quality Ratios |
|
High-good boundary |
Good-moderate boundary |
||
Romania |
IBI – Integrated Biological Index |
0,70 |
0,42 |
Biological Quality Element |
Benthic invertebrate fauna |
Country |
National classification systems |
Ecological Quality Ratios |
|
High-good boundary |
Good-moderate boundary |
||
Romania |
M-AMBI(n) – Multivariate AZTI’s Marine Biotic Index Normalized |
0,90 |
0,68 |
Part 3
Water category |
Rivers |
Geographical Intercalibration Group |
Alpine |
Country |
Type |
Biological Quality Element |
Austria |
R-A1 and R-A2 |
Macrophytes |
France |
Macrophytes |
|
Germany |
Macrophytes |
|
Italy |
Macrophytes |
|
Slovenia |
Macrophytes |
|
Spain |
Macrophytes |
Water category |
Rivers |
Geographical Intercalibration Groups |
Mediterranean |
Country |
Type |
Biological Quality Element |
Cyprus |
National river types |
Fish fauna |
Water Category |
Rivers |
Geographical Intercalibration Groups |
Very Large Rivers |
Country |
Type |
Biological Quality Element |
Finland |
R-L1 |
Phytoplankton |
Italy |
R-L2 |
Phytoplankton |
Norway |
R-L1 |
Phytoplankton |
Sweden |
R-L1 |
Phytoplankton |
Water Category |
Lakes |
Geographical Intercalibration Groups |
Cross-GIG |
Country |
Type |
Biological Quality Element |
Austria |
All national lake types |
Phytobenthos |
Estonia |
Phytobenthos |
|
Latvia |
Phytobenthos |
|
Netherlands |
Phytobenthos |
|
Norway |
Phytobenthos |
|
Spain |
Phytobenthos |
Water category |
Lakes |
Geographical Intercalibration Groups |
Mediterranean |
Country |
Type |
Biological Quality Element |
Cyprus |
National lake types |
Fish fauna |
Spain |
Fish fauna |
Water category |
Coastal waters |
Geographical Intercalibration Group |
Baltic Sea |
Country |
Type |
Biological Quality Element |
Finland |
BC1, BC3 |
Sub-Biological Quality element Angiosperms |
Poland |
BC5 |
Macroalgae and angiosperms |
Water category |
Transitional waters |
Geographical Intercalibration Group |
Baltic Sea |
Country |
Type |
Biological Quality Element |
Latvia |
National types |
Macroalgae and angiosperms |
Water category |
Transitional waters |
Geographical Intercalibration Group |
North East Atlantic |
Country |
Type |
Biological Quality Element |
Germany |
NEA 11 |
Phytoplankton |
Water category |
Transitional waters |
Geographical Intercalibration Group |
Mediterranean sea |
Country |
Type |
Biological Quality Element |
Croatia |
Estuaries |
Sub-Biological Quality element Macroalgae |
Water category |
Transitional waters |
Geographical Intercalibration Group |
Black Sea |
Country |
Type |
Biological Quality Element |
Romania |
National types |
Macroalgae and angiosperms |
ANNEX 2
1. RIVERS
Name of the Geographical Intercalibration Group |
Countries participating in Geographical Intercalibration |
Northern |
Finland |
|
Ireland |
|
Norway |
|
Sweden |
|
|
Central/Baltic |
Austria |
|
Belgium |
|
Czechiac |
|
Denmark |
|
Estonia |
|
France |
|
Germany |
|
Ireland |
|
Italy |
|
Latvia |
|
Lithuania |
|
Luxembourg |
|
Netherlands |
|
Poland |
|
Spain |
|
Sweden |
|
|
Alpine |
Austria |
|
France |
|
Germany |
|
Italy |
|
Slovenia |
|
Spain |
|
|
Eastern Continental |
Austria |
|
Bulgaria |
|
Croatia |
|
Czechia |
|
Greece |
|
Hungary |
|
Romania |
|
Slovakia |
|
Slovenia |
Mediterranean |
Bulgaria |
|
Croatia |
|
Cyprus |
|
France |
|
Greece |
|
Italy |
|
Malta |
|
Portugal |
|
Slovenia |
|
Spain |
2. LAKES
Name of the Geographical Intercalibration Group |
Countries participating in Geographical Intercalibration |
Northern |
Finland |
|
Ireland |
|
Norway |
|
Sweden |
|
|
Central/Baltic |
Belgium |
|
Czechia |
|
Denmark |
|
Estonia |
|
France |
|
Germany |
|
Ireland |
|
Latvia |
|
Lithuania |
|
Netherlands |
|
Poland |
|
|
Alpine |
Austria |
|
France |
|
Germany |
|
Italy |
|
Slovenia |
|
|
Eastern Continental |
Bulgaria |
|
Hungary |
|
Romania |
|
|
Mediterranean |
Croatia |
|
Cyprus |
|
France |
|
Greece |
|
Italy |
|
Portugal |
|
Spain |
3. COASTAL WATERS
Name of the Geographical Intercalibration Group |
Countries participating in Geographical Intercalibration |
Baltic |
Denmark |
|
Estonia |
|
Finland |
|
Germany |
|
Latvia |
|
Lithuania |
|
Poland |
|
Sweden |
|
|
North Atlantic |
Belgium |
|
Denmark |
|
France |
|
Germany |
|
Ireland |
|
Netherlands |
|
Norway |
|
Portugal |
|
Spain |
|
Sweden |
|
|
Mediterranean |
Croatia |
|
Cyprus |
|
France |
|
Greece |
|
Italy |
|
Malta |
|
Slovenia |
|
Spain |
|
|
Black Sea |
Bulgaria |
|
Romania |
4. TRANSITIONAL WATERS
Name of the Geographical Intercalibration Group |
Countries participating in Geographical Intercalibration |
Baltic |
Latvia |
|
Lithuania |
|
Poland |
|
Sweden |
|
|
North Atlantic |
Belgium |
|
France |
|
Germany |
|
Ireland |
|
Netherlands |
|
Portugal |
|
Spain |
|
Sweden |
|
|
Mediterranean |
Croatia |
|
France |
|
Greece |
|
Italy |
|
Spain |
|
|
Black Sea |
Bulgaria |
|
Romania |