COMMISSION DECISION (EU) 2018/229
of 12 February 2018
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 2013/480/EU
(notified under document C(2018) 696)
(Text with EEA relevance)
Article 1
Article 2
Article 3
ANNEX
-- PART 1 --
Water category |
Rivers |
Geographical Intercalibration Group |
Alpine rivers |
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 |
Classification française DCE Indice Biologique Global Normalisé (IBGN). AFNOR NF-T-90-350 and arrêté ministériel du 25 janvier 2010 modifié relatif aux méthodes et critères d’évaluation de l’état écologique {…} des eaux de surface |
0,93 |
0,79 |
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 (Alps) |
Classification française DCE Indice Biologique Global Normalisé (IBGN). AFNOR NF-T-90-350 and arrêté ministériel du 25 janvier 2010 modifié relatif aux méthodes et critères d’évaluation de l’état écologique {…} des eaux de surface |
0,93 |
0,71 |
France (Pyrenees) |
Classification française DCE Indice Biologique Global Normalisé (IBGN). AFNOR NF-T-90-350 and arrêté ministériel du 25 janvier 2010 modifié relatif aux méthodes et critères d’évaluation de l’état écologique {…} des eaux de surface |
0,94 |
0,81 |
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] |
0,88 |
0,56 |
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 |
0,7 |
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] |
0,88 |
0,56 |
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 |
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) |
Czech Republic |
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 |
Germany |
PERLODES — Bewertungsverfahren von Fließgewässern auf Basis des Makrozoobenthos |
0,80 |
0,60 |
France |
Classification française DCE Indice Biologique Global Normalisé (IBGN). AFNOR NF T90-350 et arrêté ministériel du 25 janvier 2010 modifié relatif aux méthodes et critères d’évaluation de l’état écologique {…} des eaux de surface |
0,94 |
0,80 |
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 (LRMI) |
0,80 |
0,60 |
Luxembourg |
Classification luxembourgeoise DCE Indice Biologique Global Normalisé (IBGN). AFNOR NF-T-90-350, AFNOR XP T 90-333 and XP T 90-388 |
0,96 |
0,72 |
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 |
Sweden |
DJ-index (Dahl & Johnson 2004) |
0,80 |
0,60 |
United Kingdom |
River Invertebrate Classification Tool (RICT)- WHPT |
0,97 |
0,86 |
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 |
Czech Republic |
Assessment method of surface running water bodies in the Czech Republic 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 |
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-C |
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 |
||
United Kingdom |
River LEAFPACS 2 |
R-C1, R-C3 and R-C4 (*1) |
0,80 |
0,60 |
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 |
0,70 |
0,42 |
All types, altitude > 500 m |
0,71 |
0,43 |
||
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 |
Czech Republic |
Czech assessment method for rivers using phytobenthos |
R-C3, R-C4, R-C5 |
0,80 |
0,63 |
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 |
Lithuania |
Lithuanian 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 |
United Kingdom |
Diatom Assessment for River Ecological Status (DARLEQ2) |
All types |
1,00 |
0,75 |
Water category |
Rivers |
Geographical Intercalibration Group |
Eastern Continental rivers |
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 |
||
Czech Republic |
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 |
0,74 |
0,58 |
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 |
||
Czech Republic |
Assessment method of surface running water bodies in the Czech Republic using biological quality element macrophytes |
R-E2, R-E3 |
0,750 |
0,500 |
Czech Republic |
Assessment method of surface running water bodies in the Czech Republic 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 |
R-E4 |
0,70 |
0,42 |
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) |
Czech Republic |
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-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 |
Type |
River characterisation |
Catchment (km2) |
Geology |
Flow regime |
R-M1 |
Small Mediterranean streams |
< 100 |
Mixed (except silicious) |
Highly seasonal |
R-M2 |
Medium Mediterranean streams |
100 — 1 000 |
Mixed (except silicious) |
Highly seasonal |
R-M4 |
Mediterranean mountain streams |
|
Non-silicious |
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 |
|
|
|
France |
Classification française DCE Indice Biologique Global Normalisé (IBGN). AFNOR NF T90-350 et arrêté ministériel du 25 janvier 2010 modifié relatif aux méthodes et critères d’évaluation de l’état écologique {…} des eaux de surface |
0,940 |
0,700 |
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 |
France |
Classification française DCE Indice Biologique Global Normalisé (IBGN). AFNOR NF T90-350 et arrêté ministériel du 25 janvier 2010 modifié relatif aux méthodes et critères d’évaluation de l’état écologique {…} des eaux de surface |
0,940 |
0,700 |
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 |
Classification française DCE Indice Biologique Global Normalisé (IBGN). AFNOR NF T90-350 et arrêté ministériel du 25 janvier 2010 modifié relatif aux méthodes et critères d’évaluation de l’état écologique {…} des eaux de surface |
0,940 |
0,700 |
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 |
|
|
|
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 |
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 |
Cyprus |
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 |
IBMR — Biological Macrophyte Index for Rivers |
0,920 |
0,690 |
Slovenia |
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 |
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 |
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 |
|
|
|
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 |
Water category |
Rivers |
Geographical Intercalibration Group |
Northern rivers |
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 |
United Kingdom |
River Invertebrate Classification Tool (RICT)- WHPT |
0,97 |
0,86 |
Biological Quality Element |
Benthic invertebrate fauna (methods sensitive for acidification) |
Country |
National classification systems intercalibrated |
Ecological Quality Ratios |
|
High-Good boundary |
Good-Moderate boundary |
||
Norway |
AcidIndex2 (Modified Raddum index2) (river acidification) |
0,675 |
0,515 |
United Kingdom — Scotland |
WFD-AWIC |
0,910 |
0,830 |
United Kingdom — England and Wales |
WFD-AWIC |
0,980 |
0,890 |
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 |
United Kingdom |
WFD-AWIC |
0,930 |
0,830 |
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 |
Finnish river phytobenthos method |
0,80 |
0,60 |
Sweden |
Indice de Polluosensibilité Spécifique (IPS) |
0,89 |
0,74 |
Ireland |
Revised form of Trophic Diatom Index (TDI) |
0,93 |
0,78 |
United Kingdom |
DARLEQ 2 |
1,00 |
0,75 |
Norway |
Periphyton Index of Trophic Status (PIT) |
0,99 (Ca ≤ 1 mg/l) |
0,83 |
0,95 (Ca > 1 mg/l) |
Water category |
Rivers |
Geographical Intercalibration Groups |
All |
Biological Quality Element |
Fish fauna |
Lowland-Midland group
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 |
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 |
Nordic group
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 |
United Kingdom — Northern Ireland |
IR_FCS2 |
0,845 |
0,540 |
United Kingdom — Scotland |
FCS2 Scotland |
0,850 |
0,600 |
Mediterranean group
Country |
National classification systems intercalibrated |
Ecological Quality Ratios |
|
High-Good boundary |
Good-Moderate boundary |
||
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 |
Alpine group
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 |
Danubian group
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 |
Czech Republic |
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 |
Water Category |
Rivers |
Geographical Intercalibration Groups |
All — Very Large Rivers |
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 |
Czech Republic |
Czech system for ecological status assessment of large non-wadeable rivers using benthic macroinvertebrates |
0,80 |
0,60 |
Germany |
Germany PTI — Potamon-Typie-Index |
0,80 |
0,60 |
Estonia |
Estonian surface water ecological quality assessment _ large river macroinvertebrates |
0,90 |
0,70 |
Spain |
IBMWP — Iberian Biological Monitoring Working Party |
0,79 |
0,48 |
Finland |
Revised Finnish river invertebrate fauna assessment method |
0,80 |
0,60 |
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 |
Lithuania |
Lithuanian River Macroinvertebrate Index |
0,80 |
0,60 |
Latvia |
LRMI — Latvian large River Macroinvertebrate Index |
0,88 |
0,63 |
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 |
Romania |
ECO-BENT — Assessment method for ecological status of water bodies based on macroinvertebrates |
0,79 |
0,53 |
Sweden |
Average Score Per Taxon (ASPT) and DJ-index |
0,80 |
0,60 |
Slovenia |
Metodologija vrednotenja ekološkega stanja vodotokov na podlagi bentoških nevretenčarjev |
0,80 |
0,60 |
Slovakia |
Slovak assessment of benthic invertebrates in large rivers |
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 |
Czech Republic |
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 |
Lithuania |
German PhytoFluss-Index for lowland rivers of type 15.2 |
0,80 |
0,60 |
Latvia |
Latvian Large River Phytoplankton Index |
0,80 |
0,60 |
Poland |
IFPL metric — Method for large rivers assessment using phytoplankton |
1,08 |
0,92 |
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 |
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 |
Czech Republic |
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 |
Spain |
IPS (Coste in Cemagref, 1982) |
0,68 |
0,48 |
Germany |
Verfahrensanleitung für die ökologische Bewertung von Fließgewässern zur Umsetzung der EG-Wasserrahmenrichtlinie: Makrophyten und Phytobenthos (PHYLIB), Modul Diatomeen |
0,725 |
0,55 |
Croatia |
Ecological status assessment system for phytobenthos in rivers based on diatoms |
0,8 |
0,61 |
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) |
||
Netherlands |
WFD-metrics for natural water types |
0,80 |
0,60 |
Portugal |
IPS — Specific Pollution Sensitivity Index |
0,90 (national type R_GRS/Guadiana river) |
0,67 (national type R_GRS/Guadiana river) |
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 |
Water category |
Lakes |
Geographical Intercalibration Group |
Alpine lakes |
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 |
||
Slovenia |
Metodologija vrednotenja ekološkega stanja jezer na podlagi bentoških nevretenčarjev |
0,80 |
0,60 |
Germany |
AESHNA — Bewertungsverfahren für das eulitorale Makrozoobenthos in Seen zur Umsetzung der EG-Wasserrahmenrichtlinie in Deutschland |
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 |
Water category |
Lakes |
Geographical Intercalibration Group |
Central/Baltic lakes |
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 Phytoplankton Index (PSI) |
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 |
UK |
Phytoplankton Lake Assessment Tool with Uncertainty Module (PLUTO) |
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 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 |
UK |
Lake LEAFPACS 2 (*2) |
All types |
0,80 |
0,66 |
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 |
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 |
UK |
Chironomid Pupal Exuvial Technique (CPET) |
0,77 |
0,64 |
CENTRAL-BALTIC LAKES GEOGRAPHICAL INTERCALIBRATION GROUP RESULTS |
|
Biological Quality Element |
Fish fauna |
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 |
||
Czech Republic |
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 |
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 |
EASTERN LAKES GEOGRAPHICAL INTERCALIBRATION GROUP |
|
Biological Quality Element |
Fish fauna |
Water category |
Lakes |
Geographical Intercalibration Group |
Mediterranean lakes |
Type |
Lake characterization |
Altitude (m) |
Annual mean precipitation (mm) and T ( oC) |
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. (*3) |
0,60 |
Greece |
New Mediterranean Assessment System for Reservoirs (NMASRP) |
n.d. (*3) |
0,60 |
Italy |
New Italian Method (NITMET) |
n.d. (*3) |
0,60 |
Portugal |
Reservoirs Biological Quality Assessment Method — Phytoplankton (New Mediterranean Assessment System for Reservoirs Phytoplankton: NMASRP). |
n.d. (*3) |
0,60 |
Spain |
Mediterranean Assessment System for Reservoirs Phytoplankton (MASRP). |
n.d. (*3) |
0,58 |
L-M8 |
|||
Cyprus |
New Mediterranean Assessment System for Reservoirs Phytoplankton (NMASRP). |
n.d. (*3) |
0,60 |
France |
Phytoplankton Index for Lakes (IPLAC): Indice Phytoplancton Lacustre |
n.d. (*3) |
0,60 |
Greece |
New Mediterranean Assessment System for Reservoirs (NMASRP) |
n.d. (*3) |
0,60 |
Italy |
New Italian Method (NITMET) |
n.d. (*3) |
0,60 |
Spain |
Mediterranean Assessment System for Reservoirs Phytoplankton (MASRP). |
n.d. (*3) |
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 |
UK |
Phytoplankton Lake Assessment Tool with Uncertainty Module (PLUTO) |
0,80 |
0,60 |
NORTHERN LAKES GEOGRAPHICAL INTERCALIBRATION GROUP RESULTS |
|
Biological Quality Element |
Macrophytes and Phytobenthos |
Sub-Biological Quality Element |
Macrophytes |
Type |
Lake characterisation |
Alkalinity (meq/l) |
Color(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 |
UK |
Lake LEAFPACS 2 (*4) |
0,8 (all types) |
0,66 (all types) |
UK |
Free Macrophyte Index (*5) |
0,9 (all types) |
0,68 (all types) |
NORTHERN LAKES GEOGRAPHICAL INTERCALIBRATION GROUP RESULTS |
|
Biological Quality Element |
Benthic invertebrates Fauna |
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 |
|
|
Norway |
MultiClear: Multimetric Invertebrate Index for Clear Lakes |
0,95 |
0,74 |
Sweden |
MILA: Multimetric Invertebrate Lake Acidification index |
0,85 |
0,60 |
UK |
LAMM (Lake Acidification Macroinvertebrate Metric) |
0,86 |
0,70 |
|
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 |
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 |
UK (Northern 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 |
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 a 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 |
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 |
Sweden |
IPS |
0,89 |
0,74 |
Slovenia |
Metodologija vrednotenja ekološkega stanja jezer na podlagi fitobentosa in makrofitov, fitobentos |
0,80 |
0,60 |
UK |
DARLEQ 2 |
0,92 |
0,70 |
MA type |
|||
Belgium (Flanders) |
Proportions of Impact-Sensitive and Impact-Associated Diatoms (PISIAD) |
0,80 |
0,60 |
Finland |
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 |
Romania |
National (Romanian) Assessment Method for Natural Lakes Ecological Status based on Phytobenthos (Diatoms) RO-AMLP |
0,80 |
0,60 |
Sweden |
IPS |
0,89 |
0,74 |
UK |
DARLEQ 2 |
0,93 |
0,66 |
LA type |
|||
Ireland |
Lake Trophic Diatom Index (IE) |
0,90 |
0,66 |
UK |
DARLEQ 2 |
0,92 |
0,70 |
Water category |
Coastal waters |
Geographical Intercalibration Group |
Baltic Sea |
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 |
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 — Lithuanian 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 |
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 oC) 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 oC) 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 |
||
|
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 |
United Kingdom |
0,80 |
0,60 |
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 |
United Kingdom (south) |
0,82 |
0,63 |
9,80 |
14,30 |
United Kingdom (north) |
0,80 |
0,60 |
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 |
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 |
United Kingdom |
RSL — Rocky Shore Reduced Species List |
0,80 |
0,60 |
Type NEA 7 intertidal macroalgae |
|
||
Norway |
RSLA — Rocky Shore Reduced Species List with Abundance |
0,80 |
0,60 |
United Kingdom |
RSL — Rocky Shore Reduced Species List |
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 |
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 |
United Kingdom |
OMBT — Opportunistic macroalgal blooming tool |
0,80 |
0,60 |
NORTH EAST ATLANTIC GEOGRAPHICAL INTERCALIBRATION GROUP RESULTS |
|
Biological Quality Element |
Macroalgae and Angiosperms |
Sub-Biological Quality Element |
Angiosperms |
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 |
United Kingdom |
Intertidal Seagrass tool |
0,80 |
0,61 |
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 |
United Kingdom |
IQI — Infaunal Quality Index |
0,75 |
0,64 |
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 |
United Kingdom |
IQI — Infaunal Quality Index |
0,75 |
0,64 |
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 |
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 |
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 |
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 |
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 |
Cyprus |
Bentix |
0,75 |
0,58 |
France |
AMBI |
0,83 |
0,58 |
Greece |
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 |
Type |
Description |
CW-BL1 |
Mesohaline, microtidal (< 1 m), shallow (< 30 m), moderately exposed to very exposed, mixed substratum (fine sand for zoobenthos) |
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 |
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 |
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 |
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 |
Sub type |
Characterisation |
MS sharing sub-type |
A |
Lagoons |
Ireland, Spain, United Kingdom |
B |
Freshwater-oligohaline, medium river flow |
Ireland, Spain, United Kingdom |
C |
Mesotidal estuary with irregular river flow |
Portugal, Spain |
D |
Large estuaries |
Germany, Ireland, Netherlands, Portugal, Spain, United Kingdom |
E |
Small-medium estuary with > 50 % intertidal area |
Ireland, Germany, Spain, United Kingdom |
F |
Small-medium estuary with < 50 % intertidal area |
Ireland, Portugal, Spain, United Kingdom |
NORTH EAST ATLANTIC GEOGRAPHICAL INTERCALIBRATION GROUP RESULTS |
|
Biological Quality Element: |
Phytoplankton |
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 (*6) |
0,67 |
0,44 |
8,00 |
12,00 |
Spain — Central Cantabrian and Galician estuaries — Euhaline (*6) |
0,67 |
0,33 |
4,00 |
8,00 |
Spain — East Cantabrian estuaries — Euhaline (*6) |
0,67 |
0,33 |
1,95 |
3,90 |
Spain — East Cantabrian estuaries — Polyhaline (*6) |
0,67 |
0,33 |
3,30 |
6,60 |
Spain — East Cantabrian estuaries — Mesohaline (*6) |
0,67 |
0,33 |
5,10 |
10,20 |
Spain — East Cantabrian estuaries — Oligohaline (*6) |
0,67 |
0,33 |
6,60 |
13,20 |
Spain — Gulf of Cádiz estuaries — Mixing zone (*6) |
0,67 |
0,33 |
3,75 |
7,50 |
Spain — Gulf of Cádiz estuaries — Euhaline (*6) |
0,67 |
0,33 |
3,00 |
6,00 |
United Kingdom |
0,80 |
0,60 |
10,00 |
15,00 |
NORTH EAST ATLANTIC 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 |
||
France |
TWOGA — Macroalgal Bloom Assessment |
0,80 |
0,60 |
Ireland |
OGA Tool — Opportunistic Green Macroalgal Abundance |
0,80 |
0,60 |
United Kingdom |
OMBT- Opportunistic macroalgal blooming tool |
0,80 |
0,60 |
NORTH EAST ATLANTIC 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 |
||
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 |
United Kingdom |
Intertidal Seagrass tool |
0,80 |
0,61 |
NORTH EAST ATLANTIC 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 |
||
Spain — Cantabria |
AQI — Angiosperm Quality Index |
0,88 |
0,73 |
Portugal |
AQuA — Angiosperm Quality Assessment Index |
0,800 |
0,600 |
United Kingdom |
SM — UK Saltmarsh Tool |
0,800 |
0,600 |
NORTH EAST ATLANTIC GEOGRAPHICAL INTERCALIBRATION GROUP RESULTS |
|
Biological Quality Element: |
Benthic invertebrate fauna |
Country |
National classification systems intercalibrated |
Ecological Quality Ratios |
|
High-good boundary |
Good-moderate boundary |
||
Sub type D |
|||
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 |
0,838 |
0,582 |
Sub type E |
|||
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 |
|||
Spain |
M-AMBI — Multivariate AZTI’s Marine Biotic Index |
0,770 |
0,530 |
Portugal |
BAT- Benthic Assessment Tool |
0,806 |
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 |
United Kingdom |
TFCI — Transitional Fish Classification Index |
0,810 |
0,580 |
United Kingdom |
EMFI — Estuarine Multi-metric Fish Index |
0,920 |
0,650 |
Water category |
Transitional waters |
Geographical Intercalibration Group |
Mediterranean Sea |
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 |
National classification systems intercalibrated |
Ecological Quality Ratios |
|
High-good boundary |
Good-moderate boundary |
||
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 |
CL-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 River fish fauna |
Biological Quality Element |
Fish fauna |
Country |
National classification systems intercalibrated |
Ecological Quality Ratios |
|
High-Good boundary |
Good-Moderate boundary |
||
Italy |
NISECI index (New Index of Ecological Status of Fish Communities) |
0,80 |
0,60 |
Bulgaria |
TsBRI (Type Specific Bulgarian Fish Index) |
0,860 |
0,650 |
Water category |
Rivers |
Geographical Intercalibration Group |
Cross-GIG Very Large Rivers |
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 |
||
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 fauna |
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 |
||
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 |
||
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 |
Biological Quality Element |
Benthic Invertebrate fauna |
Country |
National classification methods |
Ecological Quality Ratios |
|
High-good boundary |
Good-moderate boundary |
||
Greece |
GLBiI — Greek Lake Benthic invertebrate Index |
0,80 |
0,60 |
Italy |
BQIES (Benthic Quality Index Expected Species number) |
0,88 |
0,76 |
Biological Quality Element |
Fish fauna |
Country |
National classification methods |
Ecological Quality Ratios |
|
High-good boundary |
Good-moderate boundary |
||
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 |
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 |
Water category |
Coastal waters |
Geographical Intercalibration Group |
Baltic Sea |
Biological Quality Element |
Phytoplankton |
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 eelgrass, Zostera marina (angiosperm) |
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 |
Country and Type |
Ecological Quality Ratios |
Parameter values/ranges Depth limit (m) Eelgrass Zoster marina |
||
High-good boundary |
Good-moderate boundary |
High-good boundary |
Good-moderate boundary |
|
BC8 |
||||
Denmark Open coast |
0,90 |
0,74 |
8,5 |
7 |
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 |
Country and Type |
National classification systems |
Ecological Quality Ratios |
|
High-good boundary |
Good-moderate boundary |
||
NEA 7 |
|||
United Kingdom |
Phytoplankton tool |
0,80 |
0,60 |
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 |
United Kingdom (inshore/North Sea) |
0,67 |
0,33 |
10,00 |
15,00 |
United Kingdom (Atlantic) |
0,67 |
0,33 |
5,00 |
10,00 |
Biological Quality Element |
Macroalgae and Angiosperms |
Sub-Biological Quality Element |
Macroalgae |
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 |
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 |
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 |
United Kingdom |
SM — UK Saltmarsh Tool |
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 eelgrass Zostera marina (angiosperm) |
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 |
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 (*8) |
Type III W Tyrrhenian |
||||
Italy |
|
|
|
1,17 (*8) |
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 |
0,5 |
Water category |
Transitional waters |
Geographical Intercalibration Group |
North East Atlantic |
Biological Quality Element |
Phytoplankton |
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 |
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 |
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 |
United Kingdom |
IQI — Infaunal Quality Index |
0,75 |
0,64 |
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 |
United Kingdom |
IQI — Infaunal Quality Index |
0,75 |
0,64 |
Sub type F |
|||
Ireland |
IQI — Infaunal Quality Index |
0,75 |
0,64 |
Spain |
TasBEM — Taxonomically Sufficient Benthic Multimetric |
0,79 |
0,66 |
United Kingdom |
IQI — Infaunal Quality Index |
0,75 |
0,64 |
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 |
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 |
Estuaries |
|||
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 |
||
Italy |
HFBI — Habitat Fish Bio-Indicator |
0,94 |
0,55 |
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 |