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 |