MS/Art8/2018/D5/Bulgaria/Black Sea — Marine Information System for Europe

Member State report / Art8 / 2018 / D5 / Bulgaria / Black Sea

Report type	Member State report to Commission
MSFD Article	Art. 8 Initial assessment (and Art. 17 updates)
Report due	2018-10-15
GES Descriptor	D5 Eutrophication
Member State	Bulgaria
Region/subregion	Black Sea
Reported by	Ministry of Environment and Water
Report date	2022-03-29
Report access	BG_ART8_GES.xml

Emine-Sozopol (BLK-BG-AA-EmineMaslennos)

Simplified table

GES component	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5
Feature	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication
Element	Dissolved ammonium nitrogen	Dissolved ammonium nitrogen	Dissolved inorganic phosphorus	Dissolved inorganic phosphorus	Dissolved nitrate nitrogen	Dissolved nitrate nitrogen	Dissolved nitrite nitrogen	Dissolved nitrite nitrogen	Chlorophyll-a	Chlorophyll-a	Molecular taxonomy of potentially toxic species	Molecular taxonomy of potentially toxic species	Noctiluca scintillans	Transparency	Transparency	Transparency	Oxygen saturation	Oxygen saturation	Benthic habitats - opportunistic macroalgae	Benthic habitats - opportunistic macroalgae	Benthic habitats - opportunistic macroalgae	Benthic habitats - opportunistic macroalgae	Benthic habitats - macrophyte communities	Benthic habitats - macrophyte communities	Benthic habitats - macrophyte communities	Benthic habitats - macrophyte communities	Benthic habitats - macrophyte communities	Benthic habitats - macrophyte communities	Benthic habitats - macrophyte communities	Benthic habitats - macrophyte communities - sensitive species	Benthic habitats - macrophyte communities - sensitive species	Benthic habitats - macrobenthic communities
Element code	DissolvedAmoniumNitrogen	DissolvedAmoniumNitrogen	DissolvedInorganicPhosphorus	DissolvedInorganicPhosphorus	DissolvedNitrateNitrogen	DissolvedNitrateNitrogen	DissolvedNitriteNitrogen	DissolvedNitriteNitrogen	EEA_3164-01-0	EEA_3164-01-0	Combined_K	Combined_K	109921	QE3-1-1	QE3-1-1	QE3-1-1	EEA_3131-01-9	EEA_3131-01-9	QE1-2-1	QE1-2-1	QE1-2-1	QE1-2-1	QE1-2-2	QE1-2-2	QE1-2-2	QE1-2-2	QE1-2-2	QE1-2-2	QE1-2-2	QE1-2-2	QE1-2-2
Element code source	Undefined	Undefined	Undefined	Undefined	Undefined	Undefined	Undefined	Undefined	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Undefined	Undefined	Species (D1) http://www.marinespecies.org/	Undefined	Eutrophication (D5)(EQRs) http://dd.eionet.europa.eu/vocabulary/wise/ObservedPropertyBiologyEQR/view	Eutrophication (D5)(EQRs) http://dd.eionet.europa.eu/vocabulary/wise/ObservedPropertyBiologyEQR/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5)(EQRs) http://dd.eionet.europa.eu/vocabulary/wise/ObservedPropertyBiologyEQR/view	Eutrophication (D5)(EQRs) http://dd.eionet.europa.eu/vocabulary/wise/ObservedPropertyBiologyEQR/view	Eutrophication (D5)(EQRs) http://dd.eionet.europa.eu/vocabulary/wise/ObservedPropertyBiologyEQR/view	Eutrophication (D5)(EQRs) http://dd.eionet.europa.eu/vocabulary/wise/ObservedPropertyBiologyEQR/view	Eutrophication (D5)(EQRs) http://dd.eionet.europa.eu/vocabulary/wise/ObservedPropertyBiologyEQR/view	Eutrophication (D5)(EQRs) http://dd.eionet.europa.eu/vocabulary/wise/ObservedPropertyBiologyEQR/view	Eutrophication (D5)(EQRs) http://dd.eionet.europa.eu/vocabulary/wise/ObservedPropertyBiologyEQR/view	Eutrophication (D5)(EQRs) http://dd.eionet.europa.eu/vocabulary/wise/ObservedPropertyBiologyEQR/view	Eutrophication (D5)(EQRs) http://dd.eionet.europa.eu/vocabulary/wise/ObservedPropertyBiologyEQR/view	Eutrophication (D5)(EQRs) http://dd.eionet.europa.eu/vocabulary/wise/ObservedPropertyBiologyEQR/view	Eutrophication (D5)(EQRs) http://dd.eionet.europa.eu/vocabulary/wise/ObservedPropertyBiologyEQR/view	Eutrophication (D5)(EQRs) http://dd.eionet.europa.eu/vocabulary/wise/ObservedPropertyBiologyEQR/view	Eutrophication (D5)(EQRs) http://dd.eionet.europa.eu/vocabulary/wise/ObservedPropertyBiologyEQR/view
Element 2
Element 2 code
Element 2 code source
Element source	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National
Criterion	D5C1	D5C1	D5C1	D5C1	D5C1	D5C1	D5C1	D5C1	D5C2	D5C2	D5C3	D5C3	D5C3	D5C3	D5C4	D5C4	D5C5	D5C5	D5C6	D5C6	D5C6	D5C6	D5C7	D5C7	D5C7	D5C7	D5C7	D5C7	D5C7	D5C7	D5C7	D5C8
Parameter	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other
Parameter other	N-NH4 concentration in the water (spring)	N-NH4 concentration in the water (summer)	DIP concentration in the water (spring)	DIP concentration in the water (summer)	N-NO3 concentration in the water (spring)	N-NO3 concentration in the water (summer)	N-NO2 concentration in the water (spring)	N-NO2 concentration in the water (summer)	Chlorophyll a concentration in the water (spring)	Chlorophyll a concentration in the water (summer)	Number of potentially toxic species	Number of sequences of potentially toxic species	Noctiluca scintillans biomass	Noctiluca scintillans biomass	Transparency of water (spring)	Transparency of water (summer)	Oxygen saturation in the surface water (spring)	Oxygen saturation in the surface water (summer)	Proportion of sensitive and tolerant macroalgae species biomass	Proportion of tolerant macroalgae species biomass	the proportion (%) of the wet biomass of the opportunistic macrolagae within a seagrass meadow	Total projected cover of macroalgae tolerant species (lower infralittoral)	Maximal depth distribution of Ericaria bosphorica (Cystoseira crinita	Maximal depth distribution of Gongolaria barbata (Cystoseira barbata	Maximal depth distribution of Phyllophora crispa and other sciophylic sensitive macroalgae (lower infralitoral)	Proportion of sensitive macroalgae species biomass	Proportion of sensitive and tolerant macroalgae species biomass	Proportion of sensitive and tolerant macroalgae species cover (Ecological index- EQR-cover)	Total projected cover of macroalgae sensitive species of Phyllophora crispa and other sciophylic sensitive macroalgae (lower infralittoral)	Ecological Index EI	the proportion (%) of the wet biomass of the sesnsitive species within a seagrass meadow	EQR M-AMBI(n)
Threshold value upper	0.9	0.7	0.15	0.15	1.0	0.3	0.3	0.12	3.4	1.5			30.0	30.0	4.7	5.2	116.0	110.0	1.0	0.4	40.0					1.0	1.0	1.0		10.0	100.0	0.68
Threshold value lower									3.4	1.5					4.7	5.2	105.0	95.0	0.644							0.6	0.644	0.664		6.0	60.0
Threshold qualitative
Threshold value source																			National		Water Framework Directive (2000/60/EC)	National	National	National	National	National	National	National	National	Water Framework Directive (2000/60/EC)	Water Framework Directive (2000/60/EC)	Water Framework Directive (2000/60/EC)
Threshold value source other
Value achieved upper	0.83	0.78	0.209	0.229	2.99	0.33	0.195	0.119	3.61	3.5					9.0	12.0	119.0	111.0			36.42									10.0	100.0	1.0
Value achieved lower	0.27	0.16	0.052	0.023	0.03	0.1	0.038	0.053	0.35	0.06					3.0	2.0	103.0	102.0												5.1	53.0	0.38
Value unit	micromole per litre	micromole per litre	micromole per litre	microgram per litre	micromole per litre	microgram per litre	micromole per litre	microgram per litre	microgram per litre	microgram per litre			percentage	percentage	metre	metre	percentage	percentage	ratio	ratio	percentage	percentage	metre	metre	metre	ratio	ratio	ratio	percentage	Other	percentage	Other
Value unit other																														score		EQR
Proportion threshold value	90.0	90.0	90.0	90.0	90.0	90.0	90.0	90.0	90.0	90.0			90.0	90.0	90.0	90.0	90.0	90.0
Proportion value achieved	100.0	100.0	82.0	78.0	80.0	97.0	100.0	99.0	100.0	88.0					60.0	92.0	68.0	98.0	89.0	89.0	12.26					89.0	89.0	89.0		12.26	12.26	74.2
Proportion threshold value unit	% area of MRU achieving threshold value	% area of MRU achieving threshold value	% area of MRU achieving threshold value	% area of MRU achieving threshold value	% area of MRU achieving threshold value	% area of MRU achieving threshold value	% area of MRU achieving threshold value	% area of MRU achieving threshold value	% area of MRU achieving threshold value	% area of MRU achieving threshold value			% area of MRU achieving threshold value	% area of MRU achieving threshold value	% area of MRU achieving threshold value	% area of MRU achieving threshold value	% area of MRU achieving threshold value	% area of MRU achieving threshold value	% of stations achieving threshold value	% of stations achieving threshold value	% area of MRU achieving threshold value	% of stations achieving threshold value	% of stations achieving threshold value	% of stations achieving threshold value	% of stations achieving threshold value	% of stations achieving threshold value	% of stations achieving threshold value	% of stations achieving threshold value	% of stations achieving threshold value	% area of MRU achieving threshold value	% area of MRU achieving threshold value	% area of MRU achieving threshold value
Trend	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Stable	Stable	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Stable	Unknown	Unknown	Unknown	Unknown	Unknown
Parameter achieved	Yes	Yes	No	No	No	Yes	Yes	Yes	Yes	No	Not assessed	Not assessed	No	No	No	Yes	No	Yes	Yes	Yes	Unknown	Not assessed	Not assessed	Not assessed	Not assessed	Yes	Yes	Yes	Not assessed	Unknown	Unknown	No
Description parameter																			Not all of polygons from the MSFD program are investigated.		The assessment is based on point data. It is assumed that the assessment of the one point (0-3 m) for each meadow is relevant for the whole 0-3 m depth strip of each meadow. The proportion of the MRU assessment is based only on results for some of the meadows monitored during the assessment period (i.e. not all available meadows have been assessed). Trend analysis is not possible for seagrass meadows due to the lack of relevant data from the previous assessment period (before 2012) and due to the low sampling frequency per meadow during this period (2012-2017).	This indicator was not assessed, due to insufficient data.	This parameter was not assessed due to unsufficient data.	This parameter was not assessed due to unsufficient data.	This parameter was not assessed due to unsufficient data.	The proportion of the MRU assessment is based only on the results for some of the stations (polygons) monitored during the assessment period (not all stations (polygons) from the monitoring program have been assessed). .	The proportion of the MRU assessment is based only on the results for some of the stations (polygons) monitored during the assessment period (not all stations (polygons) from the monitoring program have been assessed). .		This parameter was not assessed due to unsufficient data.	The assessment is based on point data. It is assumed that the assessment of the one point (0-3 m) for each meadow is relevant for the whole 0-3 m depth strip of each meadow. The proportion of the MRU assessment is based only on results for some of the meadows monitored during the assessment period (i.e. not all available meadows have been assessed). Trend analysis is not possible for seagrass meadows due to the lack of relevant data from the previous assessment period (before 2012) and due to the low sampling frequency per meadow during this period (2012-2017).	The assessment is based on point data. It is assumed that the assessment of the one point (0-3 m) for each meadow is relevant for the whole 0-3 m depth strip of each meadow. The proportion of the MRU assessment is based only on results for some of the meadows monitored during the assessment period (i.e. not all available meadows have been assessed). Trend analysis is not possible for seagrass meadows due to the lack of relevant data from the previous assessment period (before 2012) and due to the low sampling frequency per meadow during this period (2012-2017).	Although specific proportion threshold is not set for D5C8, the proportion 74.2 % of the seabed over which the EQR threshold value set has been achieved is insufficient to reach the overall GES proportion threshold of 90 %.
Related indicator	Nutrients concentration	Nutrients concentration	Nutrients concentration	Nutrients concentration	Nutrients concentration	Nutrients concentration	Nutrients concentration	Nutrients concentration	Chlorophyll a concentration in water column	Chlorophyll a concentration in water column	Potentially toxic phytoplankton - metabarcoding	Potentially toxic phytoplankton - metabarcoding	Noctiluca scintillans biomass (%)	Noctiluca scintillans biomass (%)	Transparency	Transparency	Oxygen Saturation	Oxygen Saturation	BLK-BG-D5C6-EI_biom (Ecological index_EQR biomass)	Proportin of tolerant macroalgae species biomass	BLK_BG_D5C6_Extent of seagrass habitat assessment based on opportunistic macroalgae biomass	Total projected cover of macroalgae tolerant species -lower infralitoral	BLK_BG_D5C7- Max_depth_distr_E.bosph	BLK_BG_D5C7- Max_depth_distr_G.barb	BLK_BG_D5C7- Max_depth_distr_sens_sp	BLK_BG_D5C7- Prop_sens-sp_biom	BLK_BG_D5C7-EI _biom (Ecological index - biomass)	BLK_BG_D5C7- EI_cov	BLK_BG_D5C7- Cov_sens_sp_low_inf	BLK_BG_D5C7_Extent of seagrass habitat assessment based on EI value	BLK_BG_D5C7_Extent of seagrass habitat assessment based on ESG I value	M-AMBI(n)
Criteria status	Good	Good	Not good	Not good	Not good	Not good	Good	Good	Not good	Not good	Not assessed	Not assessed	Unknown	Unknown	Not good	Not good	Not good	Not good	Good	Good	Good	Good	Good	Good	Good	Good	Good	Good	Good	Unknown	Unknown	Not good
Description criteria																			The assessment is valid only for the 0 to 3 m depth strip of the seagrass meadows. It is based on point data (1 point per habitat). The status of the areas below the 3 m depth boundary is not assessed.	The assessment is valid only for the 0 to 3 m depth strip of the seagrass meadows. It is based on point data (1 point per habitat). The status of the areas below the 3 m depth boundary is not assessed.	The assessment is valid only for the 0 to 3 m depth strip of the seagrass meadows. It is based on point data (1 point per habitat). The status of the areas below the 3 m depth boundary is not assessed.	The assessment is valid only for the 0 to 3 m depth strip of the seagrass meadows. It is based on point data (1 point per habitat). The status of the areas below the 3 m depth boundary is not assessed.								The assessment is valid only for the 0 to 3 m depth strip of the seagrass meadows. It is based on point data (1 point per habitat). The status of the areas below the 3 m depth boundary is not assessed.	The assessment is valid only for the 0 to 3 m depth strip of the seagrass meadows. It is based on point data (1 point per habitat). The status of the areas below the 3 m depth boundary is not assessed.
Element status	Good	Good	Not good	Not good	Not good	Not good	Good	Good	Not good	Not good	Not assessed	Not assessed	Not good	Not assessed	Not good	Not good	Not good	Not good	Good	Good	Good	Good	Good	Good	Good	Good	Good	Good	Good	Unknown	Unknown	Not good
Description element														The annual average transparency within seagrass habitats is not assessed due to the lack of relevant data.					The assessment is valid only for the 0 to 3 m depth strip of the seagrass meadows. It is based on point data (1 point per habitat). The status of the areas below the 3 m depth boundary is not assessed.	The assessment is valid only for the 0 to 3 m depth strip of the seagrass meadows. It is based on point data (1 point per habitat). The status of the areas below the 3 m depth boundary is not assessed.	The assessment is valid only for the 0 to 3 m depth strip of the seagrass meadows. It is based on point data (1 point per habitat). The status of the areas below the 3 m depth boundary is not assessed.	The assessment is valid only for the 0 to 3 m depth strip of the seagrass meadows. It is based on point data (1 point per habitat). The status of the areas below the 3 m depth boundary is not assessed.								The assessment is valid only for the 0 to 3 m depth strip of the seagrass meadows. It is based on point data (1 point per habitat). The status of the areas below the 3 m depth boundary is not assessed.	The assessment is valid only for the 0 to 3 m depth strip of the seagrass meadows. It is based on point data (1 point per habitat). The status of the areas below the 3 m depth boundary is not assessed.
Integration rule type parameter
Integration rule description parameter
Integration rule type criteria	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO
Integration rule description criteria	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.
GES extent threshold	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00
GES extent achieved	56.00	56.00	56.00	56.00	56.00	56.00	56.00	56.00	56.00	56.00	56.00	56.00	56.00	56.00	56.00	56.00	56.00	56.00	56.00	56.00	56.00	56.00	56.00	56.00	56.00	56.00	56.00	56.00	56.00	56.00	56.00	56.00
GES extent unit	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status
GES achieved	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported
Description overall status
Assessments period	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017
Related pressures	Changes to hydrological conditions Input of nutrients - diffuse sources, point sources, atmospheric deposition Input of organic matter - diffuse sources and point sources Loss of, or change to, natural biological communities due to cultivation of animal or plant species Physical disturbance to seabed	Changes to hydrological conditions Input of nutrients - diffuse sources, point sources, atmospheric deposition Input of organic matter - diffuse sources and point sources Loss of, or change to, natural biological communities due to cultivation of animal or plant species Physical disturbance to seabed	Changes to hydrological conditions Input of nutrients - diffuse sources, point sources, atmospheric deposition Input of organic matter - diffuse sources and point sources Loss of, or change to, natural biological communities due to cultivation of animal or plant species Physical disturbance to seabed	Changes to hydrological conditions Input of nutrients - diffuse sources, point sources, atmospheric deposition Input of organic matter - diffuse sources and point sources Loss of, or change to, natural biological communities due to cultivation of animal or plant species Physical disturbance to seabed	Changes to hydrological conditions Input of nutrients - diffuse sources, point sources, atmospheric deposition Input of organic matter - diffuse sources and point sources Loss of, or change to, natural biological communities due to cultivation of animal or plant species Physical disturbance to seabed	Changes to hydrological conditions Input of nutrients - diffuse sources, point sources, atmospheric deposition Input of organic matter - diffuse sources and point sources Loss of, or change to, natural biological communities due to cultivation of animal or plant species Physical disturbance to seabed	Changes to hydrological conditions Input of nutrients - diffuse sources, point sources, atmospheric deposition Input of organic matter - diffuse sources and point sources Loss of, or change to, natural biological communities due to cultivation of animal or plant species Physical disturbance to seabed	Changes to hydrological conditions Input of nutrients - diffuse sources, point sources, atmospheric deposition Input of organic matter - diffuse sources and point sources Loss of, or change to, natural biological communities due to cultivation of animal or plant species Physical disturbance to seabed	Changes to hydrological conditions Input of nutrients - diffuse sources, point sources, atmospheric deposition Input of organic matter - diffuse sources and point sources Loss of, or change to, natural biological communities due to cultivation of animal or plant species Physical disturbance to seabed	Changes to hydrological conditions Input of nutrients - diffuse sources, point sources, atmospheric deposition Input of organic matter - diffuse sources and point sources Loss of, or change to, natural biological communities due to cultivation of animal or plant species Physical disturbance to seabed	Changes to hydrological conditions Input of nutrients - diffuse sources, point sources, atmospheric deposition Input of organic matter - diffuse sources and point sources Loss of, or change to, natural biological communities due to cultivation of animal or plant species Physical disturbance to seabed	Changes to hydrological conditions Input of nutrients - diffuse sources, point sources, atmospheric deposition Input of organic matter - diffuse sources and point sources Loss of, or change to, natural biological communities due to cultivation of animal or plant species Physical disturbance to seabed	Changes to hydrological conditions Input of nutrients - diffuse sources, point sources, atmospheric deposition Input of organic matter - diffuse sources and point sources Loss of, or change to, natural biological communities due to cultivation of animal or plant species Physical disturbance to seabed	Changes to hydrological conditions Input of nutrients - diffuse sources, point sources, atmospheric deposition Input of organic matter - diffuse sources and point sources Loss of, or change to, natural biological communities due to cultivation of animal or plant species Physical disturbance to seabed	Changes to hydrological conditions Input of nutrients - diffuse sources, point sources, atmospheric deposition Input of organic matter - diffuse sources and point sources Loss of, or change to, natural biological communities due to cultivation of animal or plant species Physical disturbance to seabed	Changes to hydrological conditions Input of nutrients - diffuse sources, point sources, atmospheric deposition Input of organic matter - diffuse sources and point sources Loss of, or change to, natural biological communities due to cultivation of animal or plant species Physical disturbance to seabed	Changes to hydrological conditions Input of nutrients - diffuse sources, point sources, atmospheric deposition Input of organic matter - diffuse sources and point sources Loss of, or change to, natural biological communities due to cultivation of animal or plant species Physical disturbance to seabed	Changes to hydrological conditions Input of nutrients - diffuse sources, point sources, atmospheric deposition Input of organic matter - diffuse sources and point sources Loss of, or change to, natural biological communities due to cultivation of animal or plant species Physical disturbance to seabed	Changes to hydrological conditions Input of nutrients - diffuse sources, point sources, atmospheric deposition Input of organic matter - diffuse sources and point sources Loss of, or change to, natural biological communities due to cultivation of animal or plant species Physical disturbance to seabed	Changes to hydrological conditions Input of nutrients - diffuse sources, point sources, atmospheric deposition Input of organic matter - diffuse sources and point sources Loss of, or change to, natural biological communities due to cultivation of animal or plant species Physical disturbance to seabed	Changes to hydrological conditions Input of nutrients - diffuse sources, point sources, atmospheric deposition Input of organic matter - diffuse sources and point sources Loss of, or change to, natural biological communities due to cultivation of animal or plant species Physical disturbance to seabed	Changes to hydrological conditions Input of nutrients - diffuse sources, point sources, atmospheric deposition Input of organic matter - diffuse sources and point sources Loss of, or change to, natural biological communities due to cultivation of animal or plant species Physical disturbance to seabed	Changes to hydrological conditions Input of nutrients - diffuse sources, point sources, atmospheric deposition Input of organic matter - diffuse sources and point sources Loss of, or change to, natural biological communities due to cultivation of animal or plant species Physical disturbance to seabed	Changes to hydrological conditions Input of nutrients - diffuse sources, point sources, atmospheric deposition Input of organic matter - diffuse sources and point sources Loss of, or change to, natural biological communities due to cultivation of animal or plant species Physical disturbance to seabed	Changes to hydrological conditions Input of nutrients - diffuse sources, point sources, atmospheric deposition Input of organic matter - diffuse sources and point sources Loss of, or change to, natural biological communities due to cultivation of animal or plant species Physical disturbance to seabed	Changes to hydrological conditions Input of nutrients - diffuse sources, point sources, atmospheric deposition Input of organic matter - diffuse sources and point sources Loss of, or change to, natural biological communities due to cultivation of animal or plant species Physical disturbance to seabed	Changes to hydrological conditions Input of nutrients - diffuse sources, point sources, atmospheric deposition Input of organic matter - diffuse sources and point sources Loss of, or change to, natural biological communities due to cultivation of animal or plant species Physical disturbance to seabed	Changes to hydrological conditions Input of nutrients - diffuse sources, point sources, atmospheric deposition Input of organic matter - diffuse sources and point sources Loss of, or change to, natural biological communities due to cultivation of animal or plant species Physical disturbance to seabed	Changes to hydrological conditions Input of nutrients - diffuse sources, point sources, atmospheric deposition Input of organic matter - diffuse sources and point sources Loss of, or change to, natural biological communities due to cultivation of animal or plant species Physical disturbance to seabed	Changes to hydrological conditions Input of nutrients - diffuse sources, point sources, atmospheric deposition Input of organic matter - diffuse sources and point sources Loss of, or change to, natural biological communities due to cultivation of animal or plant species Physical disturbance to seabed	Changes to hydrological conditions Input of nutrients - diffuse sources, point sources, atmospheric deposition Input of organic matter - diffuse sources and point sources Loss of, or change to, natural biological communities due to cultivation of animal or plant species Physical disturbance to seabed	Changes to hydrological conditions Input of nutrients - diffuse sources, point sources, atmospheric deposition Input of organic matter - diffuse sources and point sources Loss of, or change to, natural biological communities due to cultivation of animal or plant species Physical disturbance to seabed
Related targets	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS Т_BLK_BG_D5C4_Seagrass Т_BLK_BG_D5C6_Seagrass Т_BLK_BG_D5C7_Segrass_EI Т_BLK_BG_D5C7_Segrass_ESGI	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS Т_BLK_BG_D5C4_Seagrass Т_BLK_BG_D5C6_Seagrass Т_BLK_BG_D5C7_Segrass_EI Т_BLK_BG_D5C7_Segrass_ESGI	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS Т_BLK_BG_D5C4_Seagrass Т_BLK_BG_D5C6_Seagrass Т_BLK_BG_D5C7_Segrass_EI Т_BLK_BG_D5C7_Segrass_ESGI	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS Т_BLK_BG_D5C4_Seagrass Т_BLK_BG_D5C6_Seagrass Т_BLK_BG_D5C7_Segrass_EI Т_BLK_BG_D5C7_Segrass_ESGI	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS Т_BLK_BG_D5C4_Seagrass Т_BLK_BG_D5C6_Seagrass Т_BLK_BG_D5C7_Segrass_EI Т_BLK_BG_D5C7_Segrass_ESGI	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS Т_BLK_BG_D5C4_Seagrass Т_BLK_BG_D5C6_Seagrass Т_BLK_BG_D5C7_Segrass_EI Т_BLK_BG_D5C7_Segrass_ESGI	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS Т_BLK_BG_D5C4_Seagrass Т_BLK_BG_D5C6_Seagrass Т_BLK_BG_D5C7_Segrass_EI Т_BLK_BG_D5C7_Segrass_ESGI	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS Т_BLK_BG_D5C4_Seagrass Т_BLK_BG_D5C6_Seagrass Т_BLK_BG_D5C7_Segrass_EI Т_BLK_BG_D5C7_Segrass_ESGI	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS Т_BLK_BG_D5C4_Seagrass Т_BLK_BG_D5C6_Seagrass Т_BLK_BG_D5C7_Segrass_EI Т_BLK_BG_D5C7_Segrass_ESGI	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS Т_BLK_BG_D5C4_Seagrass Т_BLK_BG_D5C6_Seagrass Т_BLK_BG_D5C7_Segrass_EI Т_BLK_BG_D5C7_Segrass_ESGI	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS Т_BLK_BG_D5C4_Seagrass Т_BLK_BG_D5C6_Seagrass Т_BLK_BG_D5C7_Segrass_EI Т_BLK_BG_D5C7_Segrass_ESGI	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS Т_BLK_BG_D5C4_Seagrass Т_BLK_BG_D5C6_Seagrass Т_BLK_BG_D5C7_Segrass_EI Т_BLK_BG_D5C7_Segrass_ESGI	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS Т_BLK_BG_D5C4_Seagrass Т_BLK_BG_D5C6_Seagrass Т_BLK_BG_D5C7_Segrass_EI Т_BLK_BG_D5C7_Segrass_ESGI	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS Т_BLK_BG_D5C4_Seagrass Т_BLK_BG_D5C6_Seagrass Т_BLK_BG_D5C7_Segrass_EI Т_BLK_BG_D5C7_Segrass_ESGI	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS Т_BLK_BG_D5C4_Seagrass Т_BLK_BG_D5C6_Seagrass Т_BLK_BG_D5C7_Segrass_EI Т_BLK_BG_D5C7_Segrass_ESGI	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS Т_BLK_BG_D5C4_Seagrass Т_BLK_BG_D5C6_Seagrass Т_BLK_BG_D5C7_Segrass_EI Т_BLK_BG_D5C7_Segrass_ESGI	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS Т_BLK_BG_D5C4_Seagrass Т_BLK_BG_D5C6_Seagrass Т_BLK_BG_D5C7_Segrass_EI Т_BLK_BG_D5C7_Segrass_ESGI	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS Т_BLK_BG_D5C4_Seagrass Т_BLK_BG_D5C6_Seagrass Т_BLK_BG_D5C7_Segrass_EI Т_BLK_BG_D5C7_Segrass_ESGI	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS Т_BLK_BG_D5C4_Seagrass Т_BLK_BG_D5C6_Seagrass Т_BLK_BG_D5C7_Segrass_EI Т_BLK_BG_D5C7_Segrass_ESGI	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS Т_BLK_BG_D5C4_Seagrass Т_BLK_BG_D5C6_Seagrass Т_BLK_BG_D5C7_Segrass_EI Т_BLK_BG_D5C7_Segrass_ESGI	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS Т_BLK_BG_D5C4_Seagrass Т_BLK_BG_D5C6_Seagrass Т_BLK_BG_D5C7_Segrass_EI Т_BLK_BG_D5C7_Segrass_ESGI	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS Т_BLK_BG_D5C4_Seagrass Т_BLK_BG_D5C6_Seagrass Т_BLK_BG_D5C7_Segrass_EI Т_BLK_BG_D5C7_Segrass_ESGI	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS Т_BLK_BG_D5C4_Seagrass Т_BLK_BG_D5C6_Seagrass Т_BLK_BG_D5C7_Segrass_EI Т_BLK_BG_D5C7_Segrass_ESGI	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS Т_BLK_BG_D5C4_Seagrass Т_BLK_BG_D5C6_Seagrass Т_BLK_BG_D5C7_Segrass_EI Т_BLK_BG_D5C7_Segrass_ESGI	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS Т_BLK_BG_D5C4_Seagrass Т_BLK_BG_D5C6_Seagrass Т_BLK_BG_D5C7_Segrass_EI Т_BLK_BG_D5C7_Segrass_ESGI	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS Т_BLK_BG_D5C4_Seagrass Т_BLK_BG_D5C6_Seagrass Т_BLK_BG_D5C7_Segrass_EI Т_BLK_BG_D5C7_Segrass_ESGI	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS Т_BLK_BG_D5C4_Seagrass Т_BLK_BG_D5C6_Seagrass Т_BLK_BG_D5C7_Segrass_EI Т_BLK_BG_D5C7_Segrass_ESGI	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS Т_BLK_BG_D5C4_Seagrass Т_BLK_BG_D5C6_Seagrass Т_BLK_BG_D5C7_Segrass_EI Т_BLK_BG_D5C7_Segrass_ESGI	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS Т_BLK_BG_D5C4_Seagrass Т_BLK_BG_D5C6_Seagrass Т_BLK_BG_D5C7_Segrass_EI Т_BLK_BG_D5C7_Segrass_ESGI	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS Т_BLK_BG_D5C4_Seagrass Т_BLK_BG_D5C6_Seagrass Т_BLK_BG_D5C7_Segrass_EI Т_BLK_BG_D5C7_Segrass_ESGI	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS Т_BLK_BG_D5C4_Seagrass Т_BLK_BG_D5C6_Seagrass Т_BLK_BG_D5C7_Segrass_EI Т_BLK_BG_D5C7_Segrass_ESGI	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS Т_BLK_BG_D5C4_Seagrass Т_BLK_BG_D5C6_Seagrass Т_BLK_BG_D5C7_Segrass_EI Т_BLK_BG_D5C7_Segrass_ESGI

Galata-Emine (BLK-BG-AA-GalataEmine)

Simplified table

GES component	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5
Feature	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication
Element	Dissolved ammonium nitrogen	Dissolved ammonium nitrogen	Dissolved inorganic phosphorus	Dissolved inorganic phosphorus	Dissolved nitrate nitrogen	Dissolved nitrate nitrogen	Dissolved nitrite nitrogen	Dissolved nitrite nitrogen	Chlorophyll-a	Chlorophyll-a	Molecular taxonomy of potentially toxic species	Molecular taxonomy of potentially toxic species	Noctiluca scintillans	Transparency	Transparency	Transparency	Oxygen saturation	Oxygen saturation	Benthic habitats - opportunistic macroalgae	Benthic habitats - opportunistic macroalgae	Benthic habitats - opportunistic macroalgae	Benthic habitats - opportunistic macroalgae	Benthic habitats - macrophyte communities	Benthic habitats - macrophyte communities	Benthic habitats - macrophyte communities	Benthic habitats - macrophyte communities	Benthic habitats - macrophyte communities	Benthic habitats - macrophyte communities	Benthic habitats - macrophyte communities	Benthic habitats - macrophyte communities - sensitive species	Benthic habitats - macrophyte communities - sensitive species	Benthic habitats - macrobenthic communities
Element code	DissolvedAmoniumNitrogen	DissolvedAmoniumNitrogen	DissolvedInorganicPhosphorus	DissolvedInorganicPhosphorus	DissolvedNitrateNitrogen	DissolvedNitrateNitrogen	DissolvedNitriteNitrogen	DissolvedNitriteNitrogen	EEA_3164-01-0	EEA_3164-01-0	Combined_K	Combined_K	109921	QE3-1-1	QE3-1-1	QE3-1-1	EEA_3131-01-9	EEA_3131-01-9	QE1-2-1	QE1-2-1	QE1-2-1	QE1-2-1	QE1-2-2	QE1-2-2	QE1-2-2	QE1-2-2	QE1-2-2	QE1-2-2	QE1-2-2	QE1-2-2	QE1-2-2
Element code source	Undefined	Undefined	Undefined	Undefined	Undefined	Undefined	Undefined	Undefined	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Undefined	Undefined	Species (D1) http://www.marinespecies.org/	Undefined	Eutrophication (D5)(EQRs) http://dd.eionet.europa.eu/vocabulary/wise/ObservedPropertyBiologyEQR/view	Eutrophication (D5)(EQRs) http://dd.eionet.europa.eu/vocabulary/wise/ObservedPropertyBiologyEQR/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5)(EQRs) http://dd.eionet.europa.eu/vocabulary/wise/ObservedPropertyBiologyEQR/view	Eutrophication (D5)(EQRs) http://dd.eionet.europa.eu/vocabulary/wise/ObservedPropertyBiologyEQR/view	Eutrophication (D5)(EQRs) http://dd.eionet.europa.eu/vocabulary/wise/ObservedPropertyBiologyEQR/view	Eutrophication (D5)(EQRs) http://dd.eionet.europa.eu/vocabulary/wise/ObservedPropertyBiologyEQR/view	Eutrophication (D5)(EQRs) http://dd.eionet.europa.eu/vocabulary/wise/ObservedPropertyBiologyEQR/view	Eutrophication (D5)(EQRs) http://dd.eionet.europa.eu/vocabulary/wise/ObservedPropertyBiologyEQR/view	Eutrophication (D5)(EQRs) http://dd.eionet.europa.eu/vocabulary/wise/ObservedPropertyBiologyEQR/view	Eutrophication (D5)(EQRs) http://dd.eionet.europa.eu/vocabulary/wise/ObservedPropertyBiologyEQR/view	Eutrophication (D5)(EQRs) http://dd.eionet.europa.eu/vocabulary/wise/ObservedPropertyBiologyEQR/view	Eutrophication (D5)(EQRs) http://dd.eionet.europa.eu/vocabulary/wise/ObservedPropertyBiologyEQR/view	Eutrophication (D5)(EQRs) http://dd.eionet.europa.eu/vocabulary/wise/ObservedPropertyBiologyEQR/view	Eutrophication (D5)(EQRs) http://dd.eionet.europa.eu/vocabulary/wise/ObservedPropertyBiologyEQR/view	Eutrophication (D5)(EQRs) http://dd.eionet.europa.eu/vocabulary/wise/ObservedPropertyBiologyEQR/view
Element 2
Element 2 code
Element 2 code source
Element source	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National
Criterion	D5C1	D5C1	D5C1	D5C1	D5C1	D5C1	D5C1	D5C1	D5C2	D5C2	D5C3	D5C3	D5C3	D5C3	D5C4	D5C4	D5C5	D5C5	D5C6	D5C6	D5C6	D5C6	D5C7	D5C7	D5C7	D5C7	D5C7	D5C7	D5C7	D5C7	D5C7	D5C8
Parameter	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other
Parameter other	N-NH4 concentration in the water (spring)	N-NH4 concentration in the water (summer)	DIP concentration in the water (spring)	DIP concentration in the water (summer)	N-NO3 concentration in the water (spring)	N-NO3 concentration in the water (summer)	N-NO2 concentration in the water (spring)	N-NO2 concentration in the water (summer)	Chlorophyll a concentration in the water (spring)	Chlorophyll a concentration in the water (summer)	Number of potentially toxic species	Number of sequences of potentially toxic species	Noctiluca scintillans biomass	Noctiluca scintillans biomass	Transparency of water (spring)	Transparency of water (summer)	Oxygen saturation in the surface water (spring)	Oxygen saturation in the surface water (summer)	Proportion of sensitive and tolerant macroalgae species biomass	Proportion of tolerant macroalgae species biomass	the proportion (%) of the wet biomass of the opportunistic macrolagae within a seagrass meadow	Total projected cover of macroalgae tolerant species (lower infralittoral)	Maximal depth distribution of Ericaria bosphorica (Cystoseira crinita	Maximal depth distribution of Gongolaria barbata (Cystoseira barbata	Maximal depth distribution of Phyllophora crispa and other sciophylic sensitive macroalgae (lower infralitoral)	Proportion of sensitive macroalgae species biomass	Proportion of sensitive and tolerant macroalgae species biomass	Proportion of sensitive and tolerant macroalgae species cover (Ecological index- EQR-cover)	Total projected cover of macroalgae sensitive species of Phyllophora crispa and other sciophylic sensitive macroalgae (lower infralittoral)	Ecological Index EI	the proportion (%) of the wet biomass of the sesnsitive species within a seagrass meadow	EQR M-AMBI(n)
Threshold value upper	0.9	0.7	0.15	0.15	1.0	0.3	0.3	0.12	3.4	1.5			30.0	30.0	4.7	5.2	116.0	110.0	1.0	0.4	40.0					1.0	1.0	1.0		10.0	100.0	0.68
Threshold value lower									3.4	1.5					4.7	5.2	105.0	95.0	0.644							0.6	0.644	0.664		6.0	60.0
Threshold qualitative
Threshold value source																			National		Water Framework Directive (2000/60/EC)	National	National	National	National	National	National	National	National	Water Framework Directive (2000/60/EC)	Water Framework Directive (2000/60/EC)	Water Framework Directive (2000/60/EC)
Threshold value source other
Value achieved upper	0.62	1.41	0.42	0.202	1.32	0.43	0.204	0.093	6.6	3.4					7.0	13.0	119.0	106.0			10.0									8.0	100.0	1.0
Value achieved lower	0.44	0.1	0.109	0.046	0.19	0.21	0.138	0.036	0.59	0.24					0.5	4.0	114.0	103.0													88.0	0.4
Value unit	micromole per litre	micromole per litre	micromole per litre	microgram per litre	micromole per litre	microgram per litre	micromole per litre	microgram per litre	microgram per litre	microgram per litre			percentage	percentage	metre	metre	percentage	percentage	ratio	ratio	percentage	percentage	metre	metre	metre	ratio	ratio	ratio	percentage	Other	percentage	Other
Value unit other																														score		EQR
Proportion threshold value	90.0	90.0	90.0	90.0	90.0	90.0	90.0	90.0	90.0	90.0			90.0	90.0	90.0	90.0	90.0	90.0
Proportion value achieved	100.0	72.0	6.0	17.0	60.0	28.0	100.0	100.0	100.0	93.0			3.0		8.0	90.0	35.0	100.0	80.0	80.0	22.28					80.0	80.0	40.0		22.28	22.28	48.6
Proportion threshold value unit	% area of MRU achieving threshold value	% area of MRU achieving threshold value	% area of MRU achieving threshold value	% area of MRU achieving threshold value	% area of MRU achieving threshold value	% area of MRU achieving threshold value	% area of MRU achieving threshold value	% area of MRU achieving threshold value	% area of MRU achieving threshold value	% area of MRU achieving threshold value			% area of MRU achieving threshold value	% area of MRU achieving threshold value	% area of MRU achieving threshold value	% area of MRU achieving threshold value	% area of MRU achieving threshold value	% area of MRU achieving threshold value	% of stations achieving threshold value	% of stations achieving threshold value	% area of MRU achieving threshold value	% of stations achieving threshold value	% of stations achieving threshold value	% of stations achieving threshold value	% of stations achieving threshold value	% of stations achieving threshold value	% of stations achieving threshold value	% of stations achieving threshold value	% of stations achieving threshold value	% area of MRU achieving threshold value	% area of MRU achieving threshold value	% area of MRU achieving threshold value
Trend	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Stable	Stable	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Stable	Unknown	Unknown	Unknown	Unknown	Unknown
Parameter achieved	Yes	No	No	No	No	No	Yes	Yes	Yes	Yes	Not assessed	Not assessed	No	No	No	Yes	No	Yes	Yes	Yes	Unknown	Not assessed	Not assessed	Not assessed	Not assessed	Yes	Yes	No	Not assessed	Unknown	Unknown	No
Description parameter																			Not all of polygons from the MSFD program are investigated.		The assessment is based on point data. It is assumed that the assessment of the one point (0-3 m) for each meadow is relevant for the whole 0-3 m depth strip of each meadow. The proportion of the MRU assessment is based only on results for some of the meadows monitored during the assessment period (i.e. not all available meadows have been assessed). Trend analysis is not possible for seagrass meadows due to the lack of relevant data from the previous assessment period (before 2012) and due to the low sampling frequency per meadow during this period (2012-2017).	This indicator was not assessed, due to insufficient data.	This parameter was not assessed due to unsufficient data.	This parameter was not assessed due to unsufficient data.	This parameter was not assessed due to unsufficient data.	The proportion of the MRU assessment is based only on the results for some of the stations (polygons) monitored during the assessment period (not all stations (polygons) from the monitoring program have been assessed). .	The proportion of the MRU assessment is based only on the results for some of the stations (polygons) monitored during the assessment period (not all stations (polygons) from the monitoring program have been assessed). .		This parameter was not assessed due to unsufficient data.	The assessment is based on point data. It is assumed that the assessment of the one point (0-3 m) for each meadow is relevant for the whole 0-3 m depth strip of each meadow. The proportion of the MRU assessment is based only on results for some of the meadows monitored during the assessment period (i.e. not all available meadows have been assessed). Trend analysis is not possible for seagrass meadows due to the lack of relevant data from the previous assessment period (before 2012) and due to the low sampling frequency per meadow during this period (2012-2017).	The assessment is based on point data. It is assumed that the assessment of the one point (0-3 m) for each meadow is relevant for the whole 0-3 m depth strip of each meadow. The proportion of the MRU assessment is based only on results for some of the meadows monitored during the assessment period (i.e. not all available meadows have been assessed). Trend analysis is not possible for seagrass meadows due to the lack of relevant data from the previous assessment period (before 2012) and due to the low sampling frequency per meadow during this period (2012-2017).	Although specific proportion threshold is not set for D5C8, the proportion 48.6 % of the seabed over which the EQR threshold value set has been achieved is insufficient to reach the overall GES proportion threshold of 90 %.
Related indicator	Nutrients concentration	Nutrients concentration	Nutrients concentration	Nutrients concentration	Nutrients concentration	Nutrients concentration	Nutrients concentration	Nutrients concentration	Chlorophyll a concentration in water column	Chlorophyll a concentration in water column	Potentially toxic phytoplankton - metabarcoding	Potentially toxic phytoplankton - metabarcoding	Noctiluca scintillans biomass (%)	Noctiluca scintillans biomass (%)	Transparency	Transparency	Oxygen Saturation	Oxygen Saturation	BLK-BG-D5C6-EI_biom (Ecological index_EQR biomass)	Proportin of tolerant macroalgae species biomass	BLK_BG_D5C6_Extent of seagrass habitat assessment based on opportunistic macroalgae biomass	Total projected cover of macroalgae tolerant species -lower infralitoral	BLK_BG_D5C7- Max_depth_distr_E.bosph	BLK_BG_D5C7- Max_depth_distr_G.barb	BLK_BG_D5C7- Max_depth_distr_sens_sp_low._inf.	BLK_BG_D5C7- Prop_sens-sp_biom	BLK_BG_D5C7-EI _biom (Ecological index - biomass)	BLK_BG_D5C7- EI_cov	BLK_BG_D5C7- Cov_sens_sp_low_inf	BLK_BG_D5C7_Extent of seagrass habitat assessment based on EI value	BLK_BG_D5C7_Extent of seagrass habitat assessment based on ESG I value
Criteria status	Not good	Not good	Not good	Not good	Not good	Not good	Good	Good	Good	Good	Not assessed	Not assessed	Unknown	Unknown	Not good	Not good	Not good	Not good	Good	Good	Good	Good	Good	Good	Good	Good	Good	Good	Good	Unknown	Unknown	Not good
Description criteria																			The assessment is valid only for the 0 to 3 m depth strip of the seagrass meadows. It is based on point data (1 point per habitat). The status of the areas below the 3 m depth boundary is not assessed.	The assessment is valid only for the 0 to 3 m depth strip of the seagrass meadows. It is based on point data (1 point per habitat). The status of the areas below the 3 m depth boundary is not assessed.	The assessment is valid only for the 0 to 3 m depth strip of the seagrass meadows. It is based on point data (1 point per habitat). The status of the areas below the 3 m depth boundary is not assessed.	The assessment is valid only for the 0 to 3 m depth strip of the seagrass meadows. It is based on point data (1 point per habitat). The status of the areas below the 3 m depth boundary is not assessed.								The assessment is valid only for the 0 to 3 m depth strip of the seagrass meadows. It is based on point data (1 point per habitat). The status of the areas below the 3 m depth boundary is not assessed.	The assessment is valid only for the 0 to 3 m depth strip of the seagrass meadows. It is based on point data (1 point per habitat). The status of the areas below the 3 m depth boundary is not assessed.
Element status	Not good	Not good	Not good	Not good	Not good	Not good	Good	Good	Good	Good	Not assessed	Not assessed	Not good	Not assessed	Not good	Not good	Not good	Not good	Good	Good	Good	Good	Good	Good	Good	Good	Good	Good	Good	Unknown	Unknown	Not good
Description element														The annual average transparency within seagrass habitats is not assessed due to the lack of relevant data.					The assessment is valid only for the 0 to 3 m depth strip of the seagrass meadows. It is based on point data (1 point per habitat). The status of the areas below the 3 m depth boundary is not assessed.	The assessment is valid only for the 0 to 3 m depth strip of the seagrass meadows. It is based on point data (1 point per habitat). The status of the areas below the 3 m depth boundary is not assessed.	The assessment is valid only for the 0 to 3 m depth strip of the seagrass meadows. It is based on point data (1 point per habitat). The status of the areas below the 3 m depth boundary is not assessed.	The assessment is valid only for the 0 to 3 m depth strip of the seagrass meadows. It is based on point data (1 point per habitat). The status of the areas below the 3 m depth boundary is not assessed.								The assessment is valid only for the 0 to 3 m depth strip of the seagrass meadows. It is based on point data (1 point per habitat). The status of the areas below the 3 m depth boundary is not assessed.	The assessment is valid only for the 0 to 3 m depth strip of the seagrass meadows. It is based on point data (1 point per habitat). The status of the areas below the 3 m depth boundary is not assessed.
Integration rule type parameter
Integration rule description parameter
Integration rule type criteria	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO
Integration rule description criteria	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.
GES extent threshold	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00
GES extent achieved	6.00	6.00	6.00	6.00	6.00	6.00	6.00	6.00	6.00	6.00	6.00	6.00	6.00	6.00	6.00	6.00	6.00	6.00	6.00	6.00	6.00	6.00	6.00	6.00	6.00	6.00	6.00	6.00	6.00	6.00	6.00	6.00
GES extent unit	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status
GES achieved	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported
Description overall status
Assessments period	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017
Related pressures	Changes to hydrological conditions Input of nutrients - diffuse sources, point sources, atmospheric deposition Input of organic matter - diffuse sources and point sources Loss of, or change to, natural biological communities due to cultivation of animal or plant species Physical disturbance to seabed	Changes to hydrological conditions Input of nutrients - diffuse sources, point sources, atmospheric deposition Input of organic matter - diffuse sources and point sources Loss of, or change to, natural biological communities due to cultivation of animal or plant species Physical disturbance to seabed	Changes to hydrological conditions Input of nutrients - diffuse sources, point sources, atmospheric deposition Input of organic matter - diffuse sources and point sources Loss of, or change to, natural biological communities due to cultivation of animal or plant species Physical disturbance to seabed	Changes to hydrological conditions Input of nutrients - diffuse sources, point sources, atmospheric deposition Input of organic matter - diffuse sources and point sources Loss of, or change to, natural biological communities due to cultivation of animal or plant species Physical disturbance to seabed	Changes to hydrological conditions Input of nutrients - diffuse sources, point sources, atmospheric deposition Input of organic matter - diffuse sources and point sources Loss of, or change to, natural biological communities due to cultivation of animal or plant species Physical disturbance to seabed	Changes to hydrological conditions Input of nutrients - diffuse sources, point sources, atmospheric deposition Input of organic matter - diffuse sources and point sources Loss of, or change to, natural biological communities due to cultivation of animal or plant species Physical disturbance to seabed	Changes to hydrological conditions Input of nutrients - diffuse sources, point sources, atmospheric deposition Input of organic matter - diffuse sources and point sources Loss of, or change to, natural biological communities due to cultivation of animal or plant species Physical disturbance to seabed	Changes to hydrological conditions Input of nutrients - diffuse sources, point sources, atmospheric deposition Input of organic matter - diffuse sources and point sources Loss of, or change to, natural biological communities due to cultivation of animal or plant species Physical disturbance to seabed	Changes to hydrological conditions Input of nutrients - diffuse sources, point sources, atmospheric deposition Input of organic matter - diffuse sources and point sources Loss of, or change to, natural biological communities due to cultivation of animal or plant species Physical disturbance to seabed	Changes to hydrological conditions Input of nutrients - diffuse sources, point sources, atmospheric deposition Input of organic matter - diffuse sources and point sources Loss of, or change to, natural biological communities due to cultivation of animal or plant species Physical disturbance to seabed	Changes to hydrological conditions Input of nutrients - diffuse sources, point sources, atmospheric deposition Input of organic matter - diffuse sources and point sources Loss of, or change to, natural biological communities due to cultivation of animal or plant species Physical disturbance to seabed	Changes to hydrological conditions Input of nutrients - diffuse sources, point sources, atmospheric deposition Input of organic matter - diffuse sources and point sources Loss of, or change to, natural biological communities due to cultivation of animal or plant species Physical disturbance to seabed	Changes to hydrological conditions Input of nutrients - diffuse sources, point sources, atmospheric deposition Input of organic matter - diffuse sources and point sources Loss of, or change to, natural biological communities due to cultivation of animal or plant species Physical disturbance to seabed	Changes to hydrological conditions Input of nutrients - diffuse sources, point sources, atmospheric deposition Input of organic matter - diffuse sources and point sources Loss of, or change to, natural biological communities due to cultivation of animal or plant species Physical disturbance to seabed	Changes to hydrological conditions Input of nutrients - diffuse sources, point sources, atmospheric deposition Input of organic matter - diffuse sources and point sources Loss of, or change to, natural biological communities due to cultivation of animal or plant species Physical disturbance to seabed	Changes to hydrological conditions Input of nutrients - diffuse sources, point sources, atmospheric deposition Input of organic matter - diffuse sources and point sources Loss of, or change to, natural biological communities due to cultivation of animal or plant species Physical disturbance to seabed	Changes to hydrological conditions Input of nutrients - diffuse sources, point sources, atmospheric deposition Input of organic matter - diffuse sources and point sources Loss of, or change to, natural biological communities due to cultivation of animal or plant species Physical disturbance to seabed	Changes to hydrological conditions Input of nutrients - diffuse sources, point sources, atmospheric deposition Input of organic matter - diffuse sources and point sources Loss of, or change to, natural biological communities due to cultivation of animal or plant species Physical disturbance to seabed	Changes to hydrological conditions Input of nutrients - diffuse sources, point sources, atmospheric deposition Input of organic matter - diffuse sources and point sources Loss of, or change to, natural biological communities due to cultivation of animal or plant species Physical disturbance to seabed	Changes to hydrological conditions Input of nutrients - diffuse sources, point sources, atmospheric deposition Input of organic matter - diffuse sources and point sources Loss of, or change to, natural biological communities due to cultivation of animal or plant species Physical disturbance to seabed	Changes to hydrological conditions Input of nutrients - diffuse sources, point sources, atmospheric deposition Input of organic matter - diffuse sources and point sources Loss of, or change to, natural biological communities due to cultivation of animal or plant species Physical disturbance to seabed	Changes to hydrological conditions Input of nutrients - diffuse sources, point sources, atmospheric deposition Input of organic matter - diffuse sources and point sources Loss of, or change to, natural biological communities due to cultivation of animal or plant species Physical disturbance to seabed	Changes to hydrological conditions Input of nutrients - diffuse sources, point sources, atmospheric deposition Input of organic matter - diffuse sources and point sources Loss of, or change to, natural biological communities due to cultivation of animal or plant species Physical disturbance to seabed	Changes to hydrological conditions Input of nutrients - diffuse sources, point sources, atmospheric deposition Input of organic matter - diffuse sources and point sources Loss of, or change to, natural biological communities due to cultivation of animal or plant species Physical disturbance to seabed	Changes to hydrological conditions Input of nutrients - diffuse sources, point sources, atmospheric deposition Input of organic matter - diffuse sources and point sources Loss of, or change to, natural biological communities due to cultivation of animal or plant species Physical disturbance to seabed	Changes to hydrological conditions Input of nutrients - diffuse sources, point sources, atmospheric deposition Input of organic matter - diffuse sources and point sources Loss of, or change to, natural biological communities due to cultivation of animal or plant species Physical disturbance to seabed	Changes to hydrological conditions Input of nutrients - diffuse sources, point sources, atmospheric deposition Input of organic matter - diffuse sources and point sources Loss of, or change to, natural biological communities due to cultivation of animal or plant species Physical disturbance to seabed	Changes to hydrological conditions Input of nutrients - diffuse sources, point sources, atmospheric deposition Input of organic matter - diffuse sources and point sources Loss of, or change to, natural biological communities due to cultivation of animal or plant species Physical disturbance to seabed	Changes to hydrological conditions Input of nutrients - diffuse sources, point sources, atmospheric deposition Input of organic matter - diffuse sources and point sources Loss of, or change to, natural biological communities due to cultivation of animal or plant species Physical disturbance to seabed	Changes to hydrological conditions Input of nutrients - diffuse sources, point sources, atmospheric deposition Input of organic matter - diffuse sources and point sources Loss of, or change to, natural biological communities due to cultivation of animal or plant species Physical disturbance to seabed	Changes to hydrological conditions Input of nutrients - diffuse sources, point sources, atmospheric deposition Input of organic matter - diffuse sources and point sources Loss of, or change to, natural biological communities due to cultivation of animal or plant species Physical disturbance to seabed	Changes to hydrological conditions Input of nutrients - diffuse sources, point sources, atmospheric deposition Input of organic matter - diffuse sources and point sources Loss of, or change to, natural biological communities due to cultivation of animal or plant species Physical disturbance to seabed
Related targets	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS Т_BLK_BG_D5C4_Seagrass Т_BLK_BG_D5C6_Seagrass Т_BLK_BG_D5C7_Segrass_EI Т_BLK_BG_D5C7_Segrass_ESGI	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS Т_BLK_BG_D5C4_Seagrass Т_BLK_BG_D5C6_Seagrass Т_BLK_BG_D5C7_Segrass_EI Т_BLK_BG_D5C7_Segrass_ESGI	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS Т_BLK_BG_D5C4_Seagrass Т_BLK_BG_D5C6_Seagrass Т_BLK_BG_D5C7_Segrass_EI Т_BLK_BG_D5C7_Segrass_ESGI	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS Т_BLK_BG_D5C4_Seagrass Т_BLK_BG_D5C6_Seagrass Т_BLK_BG_D5C7_Segrass_EI Т_BLK_BG_D5C7_Segrass_ESGI	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS Т_BLK_BG_D5C4_Seagrass Т_BLK_BG_D5C6_Seagrass Т_BLK_BG_D5C7_Segrass_EI Т_BLK_BG_D5C7_Segrass_ESGI	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS Т_BLK_BG_D5C4_Seagrass Т_BLK_BG_D5C6_Seagrass Т_BLK_BG_D5C7_Segrass_EI Т_BLK_BG_D5C7_Segrass_ESGI	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS Т_BLK_BG_D5C4_Seagrass Т_BLK_BG_D5C6_Seagrass Т_BLK_BG_D5C7_Segrass_EI Т_BLK_BG_D5C7_Segrass_ESGI	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS Т_BLK_BG_D5C4_Seagrass Т_BLK_BG_D5C6_Seagrass Т_BLK_BG_D5C7_Segrass_EI Т_BLK_BG_D5C7_Segrass_ESGI	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS Т_BLK_BG_D5C4_Seagrass Т_BLK_BG_D5C6_Seagrass Т_BLK_BG_D5C7_Segrass_EI Т_BLK_BG_D5C7_Segrass_ESGI	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS Т_BLK_BG_D5C4_Seagrass Т_BLK_BG_D5C6_Seagrass Т_BLK_BG_D5C7_Segrass_EI Т_BLK_BG_D5C7_Segrass_ESGI	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS Т_BLK_BG_D5C4_Seagrass Т_BLK_BG_D5C6_Seagrass Т_BLK_BG_D5C7_Segrass_EI Т_BLK_BG_D5C7_Segrass_ESGI	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS Т_BLK_BG_D5C4_Seagrass Т_BLK_BG_D5C6_Seagrass Т_BLK_BG_D5C7_Segrass_EI Т_BLK_BG_D5C7_Segrass_ESGI	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS Т_BLK_BG_D5C4_Seagrass Т_BLK_BG_D5C6_Seagrass Т_BLK_BG_D5C7_Segrass_EI Т_BLK_BG_D5C7_Segrass_ESGI	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS Т_BLK_BG_D5C4_Seagrass Т_BLK_BG_D5C6_Seagrass Т_BLK_BG_D5C7_Segrass_EI Т_BLK_BG_D5C7_Segrass_ESGI	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS Т_BLK_BG_D5C4_Seagrass Т_BLK_BG_D5C6_Seagrass Т_BLK_BG_D5C7_Segrass_EI Т_BLK_BG_D5C7_Segrass_ESGI	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS Т_BLK_BG_D5C4_Seagrass Т_BLK_BG_D5C6_Seagrass Т_BLK_BG_D5C7_Segrass_EI Т_BLK_BG_D5C7_Segrass_ESGI	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS Т_BLK_BG_D5C4_Seagrass Т_BLK_BG_D5C6_Seagrass Т_BLK_BG_D5C7_Segrass_EI Т_BLK_BG_D5C7_Segrass_ESGI	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS Т_BLK_BG_D5C4_Seagrass Т_BLK_BG_D5C6_Seagrass Т_BLK_BG_D5C7_Segrass_EI Т_BLK_BG_D5C7_Segrass_ESGI	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS Т_BLK_BG_D5C4_Seagrass Т_BLK_BG_D5C6_Seagrass Т_BLK_BG_D5C7_Segrass_EI Т_BLK_BG_D5C7_Segrass_ESGI	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS Т_BLK_BG_D5C4_Seagrass Т_BLK_BG_D5C6_Seagrass Т_BLK_BG_D5C7_Segrass_EI Т_BLK_BG_D5C7_Segrass_ESGI	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS Т_BLK_BG_D5C4_Seagrass Т_BLK_BG_D5C6_Seagrass Т_BLK_BG_D5C7_Segrass_EI Т_BLK_BG_D5C7_Segrass_ESGI	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS Т_BLK_BG_D5C4_Seagrass Т_BLK_BG_D5C6_Seagrass Т_BLK_BG_D5C7_Segrass_EI Т_BLK_BG_D5C7_Segrass_ESGI	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS Т_BLK_BG_D5C4_Seagrass Т_BLK_BG_D5C6_Seagrass Т_BLK_BG_D5C7_Segrass_EI Т_BLK_BG_D5C7_Segrass_ESGI	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS Т_BLK_BG_D5C4_Seagrass Т_BLK_BG_D5C6_Seagrass Т_BLK_BG_D5C7_Segrass_EI Т_BLK_BG_D5C7_Segrass_ESGI	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS Т_BLK_BG_D5C4_Seagrass Т_BLK_BG_D5C6_Seagrass Т_BLK_BG_D5C7_Segrass_EI Т_BLK_BG_D5C7_Segrass_ESGI	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS Т_BLK_BG_D5C4_Seagrass Т_BLK_BG_D5C6_Seagrass Т_BLK_BG_D5C7_Segrass_EI Т_BLK_BG_D5C7_Segrass_ESGI	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS Т_BLK_BG_D5C4_Seagrass Т_BLK_BG_D5C6_Seagrass Т_BLK_BG_D5C7_Segrass_EI Т_BLK_BG_D5C7_Segrass_ESGI	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS Т_BLK_BG_D5C4_Seagrass Т_BLK_BG_D5C6_Seagrass Т_BLK_BG_D5C7_Segrass_EI Т_BLK_BG_D5C7_Segrass_ESGI	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS Т_BLK_BG_D5C4_Seagrass Т_BLK_BG_D5C6_Seagrass Т_BLK_BG_D5C7_Segrass_EI Т_BLK_BG_D5C7_Segrass_ESGI	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS Т_BLK_BG_D5C4_Seagrass Т_BLK_BG_D5C6_Seagrass Т_BLK_BG_D5C7_Segrass_EI Т_BLK_BG_D5C7_Segrass_ESGI	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS Т_BLK_BG_D5C4_Seagrass Т_BLK_BG_D5C6_Seagrass Т_BLK_BG_D5C7_Segrass_EI Т_BLK_BG_D5C7_Segrass_ESGI	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS Т_BLK_BG_D5C4_Seagrass Т_BLK_BG_D5C6_Seagrass Т_BLK_BG_D5C7_Segrass_EI Т_BLK_BG_D5C7_Segrass_ESGI

Kaliakra-Galata (BLK-BG-AA-KaliakraGalata)

Simplified table

GES component	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5
Feature	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication
Element	Dissolved ammonium nitrogen	Dissolved ammonium nitrogen	Dissolved inorganic phosphorus	Dissolved inorganic phosphorus	Dissolved nitrate nitrogen	Dissolved nitrate nitrogen	Dissolved nitrite nitrogen	Dissolved nitrite nitrogen	Chlorophyll-a	Chlorophyll-a	Molecular taxonomy of potentially toxic species	Molecular taxonomy of potentially toxic species	Noctiluca scintillans	Transparency	Transparency	Oxygen saturation	Oxygen saturation	Benthic habitats - opportunistic macroalgae	Benthic habitats - opportunistic macroalgae	Benthic habitats - opportunistic macroalgae	Benthic habitats - macrophyte communities	Benthic habitats - macrophyte communities	Benthic habitats - macrophyte communities	Benthic habitats - macrophyte communities	Benthic habitats - macrophyte communities	Benthic habitats - macrophyte communities	Benthic habitats - macrophyte communities	Benthic habitats - macrobenthic communities
Element code	DissolvedAmoniumNitrogen	DissolvedAmoniumNitrogen	DissolvedInorganicPhosphorus	DissolvedInorganicPhosphorus	DissolvedNitrateNitrogen	DissolvedNitrateNitrogen	DissolvedNitriteNitrogen	DissolvedNitriteNitrogen	EEA_3164-01-0	EEA_3164-01-0	Combined_K	Combined_K	109921	QE3-1-1	QE3-1-1	EEA_3131-01-9	EEA_3131-01-9	QE1-2-1	QE1-2-1	QE1-2-1	QE1-2-2	QE1-2-2	QE1-2-2	QE1-2-2	QE1-2-2	QE1-2-2	QE1-2-2
Element code source	Undefined	Undefined	Undefined	Undefined	Undefined	Undefined	Undefined	Undefined	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Undefined	Undefined	Species (D1) http://www.marinespecies.org/	Eutrophication (D5)(EQRs) http://dd.eionet.europa.eu/vocabulary/wise/ObservedPropertyBiologyEQR/view	Eutrophication (D5)(EQRs) http://dd.eionet.europa.eu/vocabulary/wise/ObservedPropertyBiologyEQR/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5)(EQRs) http://dd.eionet.europa.eu/vocabulary/wise/ObservedPropertyBiologyEQR/view	Eutrophication (D5)(EQRs) http://dd.eionet.europa.eu/vocabulary/wise/ObservedPropertyBiologyEQR/view	Eutrophication (D5)(EQRs) http://dd.eionet.europa.eu/vocabulary/wise/ObservedPropertyBiologyEQR/view	Eutrophication (D5)(EQRs) http://dd.eionet.europa.eu/vocabulary/wise/ObservedPropertyBiologyEQR/view	Eutrophication (D5)(EQRs) http://dd.eionet.europa.eu/vocabulary/wise/ObservedPropertyBiologyEQR/view	Eutrophication (D5)(EQRs) http://dd.eionet.europa.eu/vocabulary/wise/ObservedPropertyBiologyEQR/view	Eutrophication (D5)(EQRs) http://dd.eionet.europa.eu/vocabulary/wise/ObservedPropertyBiologyEQR/view	Eutrophication (D5)(EQRs) http://dd.eionet.europa.eu/vocabulary/wise/ObservedPropertyBiologyEQR/view	Eutrophication (D5)(EQRs) http://dd.eionet.europa.eu/vocabulary/wise/ObservedPropertyBiologyEQR/view	Eutrophication (D5)(EQRs) http://dd.eionet.europa.eu/vocabulary/wise/ObservedPropertyBiologyEQR/view
Element 2
Element 2 code
Element 2 code source
Element source	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National
Criterion	D5C1	D5C1	D5C1	D5C1	D5C1	D5C1	D5C1	D5C1	D5C2	D5C2	D5C3	D5C3	D5C3	D5C4	D5C4	D5C5	D5C5	D5C6	D5C6	D5C6	D5C7	D5C7	D5C7	D5C7	D5C7	D5C7	D5C7	D5C8
Parameter	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other
Parameter other	N-NH4 concentration in the water (spring)	N-NH4 concentration in the water (summer)	DIP concentration in the water (spring)	DIP concentration in the water (summer)	N-NO3 concentration in the water (spring)	N-NO3 concentration in the water (summer)	N-NO2 concentration in the water (spring)	N-NO2 concentration in the water (summer)	Chlorophyll a concentration in the water (spring)	Chlorophyll a concentration in the water (summer)	Number of potentially toxic species	Number of sequences of potentially toxic species	Noctiluca scintillans biomass	Transparency of water (spring)	Transparency of water (summer)	Oxygen saturation in the surface water (spring)	Oxygen saturation in the surface water (summer)	Proportion of sensitive and tolerant macroalgae species biomass	Proportion of tolerant macroalgae species biomass	Total projected cover of macroalgae tolerant species (lower infralittoral)	Maximal depth distribution of Ericaria bosphorica (Cystoseira crinita f.bosphorica	Maximal depth distribution of Gongolaria barbata(Cystoseira barbata	Maximal depth distribution of Phyllophora crispa and other sciophylic sensitive macroalgae (lower infralitoral)	Proportion of sensitive macroalgae species biomass	Proportion of sensitive and tolerant macroalgae species biomass	Proportion of sensitive and tolerant macroalgae species cover (Ecological index- EQR-cover)	Total projected cover of macroalgae sensitive species of Phyllophora crispa and other sciophylic sensitive macroalgae (lower infralittoral)	EQR M-AMBI(n)
Threshold value upper	0.9	0.7	0.15	0.15	1.0	0.3	0.3	0.12	3.4	1.5			30.0	4.7	5.2	116.0	110.0	1.0	0.4					1.0	1.0	1.0		0.68
Threshold value lower									3.4	1.5				4.7	5.2	105.0	95.0	0.644						0.6	0.644	0.664
Threshold qualitative
Threshold value source																		National		National	National	National	National	National	National	National	National	Water Framework Directive (2000/60/EC)
Threshold value source other
Value achieved upper	0.88	5.76	0.319	0.221	1.67	1.76	0.483	0.117	22.11	13.08				8.0	12.0	125.0	110.0											1.0
Value achieved lower	0.22	0.13	0.095	0.06	0.3	0.36	0.079	0.056	0.37	0.1				2.5	1.0	94.0	100.0											0.32
Value unit	micromole per litre	micromole per litre	micromole per litre	microgram per litre	micromole per litre	microgram per litre	micromole per litre	microgram per litre	microgram per litre	microgram per litre			percentage	metre	metre	percentage	percentage	ratio	ratio	percentage	metre	metre	metre	ratio	ratio	ratio	percentage	Other
Value unit other																												EQR
Proportion threshold value	90.0	90.0	90.0	90.0	90.0	90.0	90.0	90.0	90.0	90.0			90.0	90.0	90.0	90.0	90.0
Proportion value achieved	100.0	44.0	24.0	72.0	53.0	1.0	57.0	94.0	94.0	94.0				33.0	96.0	64.0	99.0	63.0	63.0					63.0	63.0	40.0		42.9
Proportion threshold value unit	% area of MRU achieving threshold value	% area of MRU achieving threshold value	% area of MRU achieving threshold value	% area of MRU achieving threshold value	% area of MRU achieving threshold value	% area of MRU achieving threshold value	% area of MRU achieving threshold value	% area of MRU achieving threshold value	% area of MRU achieving threshold value				% area of MRU achieving threshold value	% area of MRU achieving threshold value	% area of MRU achieving threshold value	% area of MRU achieving threshold value	% area of MRU achieving threshold value	% of stations achieving threshold value	% of stations achieving threshold value	% of stations achieving threshold value	% of stations achieving threshold value	% of stations achieving threshold value	% of stations achieving threshold value	% of stations achieving threshold value	% of stations achieving threshold value	% of stations achieving threshold value	% of stations achieving threshold value	% area of MRU achieving threshold value
Trend	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown
Parameter achieved	Yes	No	No	No	No	No	No	Yes	Yes	Yes	Not assessed	Not assessed	No	No	Yes	No	Yes	No	No	Not assessed	Not assessed	Not assessed	Not assessed	No	No	No	Not assessed	No
Description parameter																				This indicator was not assessed, due to insufficient data.	This parameter was not assessed due to unsufficient data.	This parameter was not assessed due to insufficient data.	This parameter was not assessed due to unsufficient data.	The proportion of the MRU assessment is based only on the results for some of the stations (polygons) monitored during the assessment period (not all stations (polygons) from the monitoring program have been assessed). .	The proportion of the MRU assessment is based only on the results for some of the stations (polygons) monitored during the assessment period (not all stations (polygons) from the monitoring program have been assessed). .		This parameter was not assessed due to unsufficient data.	Although specific proportion threshold is not set for D5C8, the proportion 42.9 % of the seabed over which the EQR threshold value set has been achieved is insufficient to reach the overall GES proportion threshold of 90 %.
Related indicator	Nutrients concentration	Nutrients concentration	Nutrients concentration	Nutrients concentration	Nutrients concentration	Nutrients concentration	Nutrients concentration	Nutrients concentration	Chlorophyll a concentration in water column	Chlorophyll a concentration in water column	Potentially toxic phytoplankton - metabarcoding	Potentially toxic phytoplankton - metabarcoding	Noctiluca scintillans biomass (%)	Transparency	Transparency	Oxygen Saturation	Oxygen Saturation	BLK-BG-D5C6-EI_biom (Ecological index-EQR biomass)	Proportin of tolerant macroalgae species biomass	Total projected cover of macroalgae tolerant species -lower infralitoral	BLK_BG_D5C7- Max_depth_distr_E.bosph.	BLK_BG_D5C7- Max_depth_distr_G.barb	BLK_BG_D5C7- Max_depth_distr_sens_sp_low.inf.	BLK_BG_D5C7- Prop_sens-sp_biom	BLK_BG_D5C7-EI _biom (Ecological index - biomass)	BLK_BG_D5C7- EI_cov	BLK_BG_D5C7- Cov_sens_sp_low_inf	M-AMBI(n)
Criteria status	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Good	Good	Not assessed	Not assessed	Unknown	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good
Description criteria
Element status	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Good	Good	Not assessed	Not assessed	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good
Description element
Integration rule type parameter
Integration rule description parameter
Integration rule type criteria	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO
Integration rule description criteria	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.
GES extent threshold	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00
GES extent achieved	10.00	10.00	10.00	10.00	10.00	10.00	10.00	10.00	10.00	10.00	10.00	10.00	10.00	10.00	10.00	10.00	10.00	10.00	10.00	10.00	10.00	10.00	10.00	10.00	10.00	10.00	10.00	10.00
GES extent unit	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status
GES achieved	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported
Description overall status
Assessments period	2012-2107	2012-2107	2012-2107	2012-2107	2012-2107	2012-2107	2012-2107	2012-2107	2012-2107	2012-2107	2012-2107	2012-2107	2012-2107	2012-2107	2012-2107	2012-2107	2012-2107	2012-2107	2012-2107	2012-2107	2012-2107	2012-2107	2012-2107	2012-2107	2012-2107	2012-2107	2012-2107	2012-2107
Related pressures
Related targets	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS

Sozopol-Rezovo (BLK-BG-AA-MaslennosRezovo)

Simplified table

GES component	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5
Feature	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication
Element	Dissolved ammonium nitrogen	Dissolved ammonium nitrogen	Dissolved inorganic phosphorus	Dissolved inorganic phosphorus	Dissolved nitrate nitrogen	Dissolved nitrate nitrogen	Dissolved nitrite nitrogen	Dissolved nitrite nitrogen	Chlorophyll-a	Chlorophyll-a	Molecular taxonomy of potentially toxic species	Molecular taxonomy of potentially toxic species	Noctiluca scintillans	Transparency	Transparency	Oxygen saturation	Oxygen saturation	Benthic habitats - opportunistic macroalgae	Benthic habitats - opportunistic macroalgae	Benthic habitats - opportunistic macroalgae	Benthic habitats - macrophyte communities	Benthic habitats - macrophyte communities	Benthic habitats - macrophyte communities	Benthic habitats - macrophyte communities	Benthic habitats - macrophyte communities	Benthic habitats - macrophyte communities	Benthic habitats - macrophyte communities	Benthic habitats - macrobenthic communities
Element code	DissolvedAmoniumNitrogen	DissolvedAmoniumNitrogen	DissolvedInorganicPhosphorus	DissolvedInorganicPhosphorus	DissolvedNitrateNitrogen	DissolvedNitrateNitrogen	DissolvedNitriteNitrogen	DissolvedNitriteNitrogen	EEA_3164-01-0	EEA_3164-01-0	Combined_K	Combined_K	109921	QE3-1-1	QE3-1-1	EEA_3131-01-9	EEA_3131-01-9	QE1-2-1	QE1-2-1	QE1-2-1	QE1-2-2	QE1-2-2	QE1-2-2	QE1-2-2	QE1-2-2	QE1-2-2	QE1-2-2
Element code source	Undefined	Undefined	Undefined	Undefined	Undefined	Undefined	Undefined	Undefined	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Undefined	Undefined	Species (D1) http://www.marinespecies.org/	Eutrophication (D5)(EQRs) http://dd.eionet.europa.eu/vocabulary/wise/ObservedPropertyBiologyEQR/view	Eutrophication (D5)(EQRs) http://dd.eionet.europa.eu/vocabulary/wise/ObservedPropertyBiologyEQR/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5)(EQRs) http://dd.eionet.europa.eu/vocabulary/wise/ObservedPropertyBiologyEQR/view	Eutrophication (D5)(EQRs) http://dd.eionet.europa.eu/vocabulary/wise/ObservedPropertyBiologyEQR/view	Eutrophication (D5)(EQRs) http://dd.eionet.europa.eu/vocabulary/wise/ObservedPropertyBiologyEQR/view	Eutrophication (D5)(EQRs) http://dd.eionet.europa.eu/vocabulary/wise/ObservedPropertyBiologyEQR/view	Eutrophication (D5)(EQRs) http://dd.eionet.europa.eu/vocabulary/wise/ObservedPropertyBiologyEQR/view	Eutrophication (D5)(EQRs) http://dd.eionet.europa.eu/vocabulary/wise/ObservedPropertyBiologyEQR/view	Eutrophication (D5)(EQRs) http://dd.eionet.europa.eu/vocabulary/wise/ObservedPropertyBiologyEQR/view	Eutrophication (D5)(EQRs) http://dd.eionet.europa.eu/vocabulary/wise/ObservedPropertyBiologyEQR/view	Eutrophication (D5)(EQRs) http://dd.eionet.europa.eu/vocabulary/wise/ObservedPropertyBiologyEQR/view	Eutrophication (D5)(EQRs) http://dd.eionet.europa.eu/vocabulary/wise/ObservedPropertyBiologyEQR/view
Element 2
Element 2 code
Element 2 code source
Element source	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National
Criterion	D5C1	D5C1	D5C1	D5C1	D5C1	D5C1	D5C1	D5C1	D5C2	D5C2	D5C3	D5C3	D5C3	D5C4	D5C4	D5C5	D5C5	D5C6	D5C6	D5C6	D5C7	D5C7	D5C7	D5C7	D5C7	D5C7	D5C7	D5C8
Parameter	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other
Parameter other	N-NH4 concentration in the water (spring)	N-NH4 concentration in the water (summer)	DIP concentration in the water (spring)	DIP concentration in the water (summer)	N-NO3 concentration in the water (spring)	N-NO3 concentration in the water (summer)	N-NO2 concentration in the water (spring)	N-NO2 concentration in the water (summer)	Chlorophyll a concentration in the water (spring)	Chlorophyll a concentration in the water (summer)	Number of potentially toxic species	Number of sequences of potentially toxic species	Noctiluca scintillans biomass	Transparency of water (spring)	Transparency of water (summer)	Oxygen saturation in the surface water (spring)	Oxygen saturation in the surface water (summer)	Proportion of sensitive and tolerant macroalgae species biomass	Proportion of tolerant macroalgae species biomass	Total projected cover of macroalgae tolerant species (lower infralittoral)	Maximal depth distribution of Ericaria bosphoric (Cystoseira crinita F.bosphorica	Maximal depth distribution of Gongolaria barbata (Cystoseira barbata	Maximal depth distribution of Phyllophora crispa and other sciophylic sensitive macroalgae (lower infralitoral)	Proportion of sensitive macroalgae species biomass	Proportion of sensitive and tolerant macroalgae species biomass	Proportion of sensitive and tolerant macroalgae species cover (Ecological index- EQR-cover)	Total projected cover of macroalgae sensitive species of Phyllophora crispa and other sciophylic sensitive macroalgae (lower infralittoral)	EQR M-AMBI(n)
Threshold value upper	0.9	0.7	0.15	0.15	1.0	0.3	0.3	0.12	3.4	1.5			30.0	4.7	5.2	116.0	110.0	1.0	0.4					1.0	1.0	1.0		0.68
Threshold value lower									3.4	1.57				4.7	5.2	105.0	95.0	0.644						0.6	0.644	0.664
Threshold qualitative
Threshold value source																		National		National	National	National	National	National	National	National	National	Water Framework Directive (2000/60/EC)
Threshold value source other
Value achieved upper	0.45	0.4	0.166	0.188	0.43	0.36	0.088	0.068	1.89					8.0	13.0	117.0	109.0											1.0
Value achieved lower	0.18	0.05	0.054	0.052	0.13	0.3	0.033	0.056	0.6					3.0	6.0	116.0	103.0											0.53
Value unit	micromole per litre	micromole per litre	micromole per litre	microgram per litre	micromole per litre	microgram per litre	micromole per litre	microgram per litre	microgram per litre	microgram per litre			percentage	metre	metre	percentage	percentage	ratio	ratio	percentage	metre	metre	metre	ratio	ratio	ratio	percentage	Other
Value unit other																												EQR
Proportion threshold value	90.0	90.0	90.0	90.0	90.0	90.0	90.0	90.0	90.0	90.0			90.0	90.0	90.0	90.0	90.0
Proportion value achieved	100.0	100.0	6.0	38.0	100.0	31.0	100.0	100.0	100.0	100.0				55.0	100.0	15.0	100.0	100.0	100.0					100.0	100.0	100.0		84.1
Proportion threshold value unit	% area of MRU achieving threshold value	% area of MRU achieving threshold value	% area of MRU achieving threshold value	% area of MRU achieving threshold value	% area of MRU achieving threshold value	% area of MRU achieving threshold value	% area of MRU achieving threshold value	% area of MRU achieving threshold value	% area of MRU achieving threshold value	% area of MRU achieving threshold value			% area of MRU achieving threshold value	% area of MRU achieving threshold value	% area of MRU achieving threshold value	% area of MRU achieving threshold value	% area of MRU achieving threshold value	% of stations achieving threshold value	% of stations achieving threshold value	% of stations achieving threshold value	% of stations achieving threshold value	% of stations achieving threshold value	% of stations achieving threshold value	% of stations achieving threshold value	% of stations achieving threshold value	% of stations achieving threshold value	% of stations achieving threshold value
Trend	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown
Parameter achieved	Yes	Yes	No	No	Yes	No	Yes	Yes	Yes	Yes	Not assessed	Not assessed	No	No	Yes	No	Yes	Yes	Yes	Not assessed	Not assessed	Not assessed	Not assessed	Yes	Yes	Yes	Not assessed	No
Description parameter																				This indicator was not assessed, due to insufficient data.	This parameter was not assessed due to unsufficient data.	This parameter was not assessed due to insufficient data.	This parameter was not assessed due to unsufficient data.	The proportion of the MRU assessment is based only on the results for some of the stations (polygons) monitored during the assessment period (not all stations (polygons) from the monitoring program have been assessed). .	The proportion of the MRU assessment is based only on the results for some of the stations (polygons) monitored during the assessment period (not all stations (polygons) from the monitoring program have been assessed). .		This parameter was not assessed due to unsufficient data.	Although specific proportion threshold is not set for D5C8, the proportion 84.1 % of the seabed over which the EQR threshold value set has been achieved is insufficient to reach the overall GES proportion threshold of 90 %.
Related indicator	Nutrients concentration	Nutrients concentration	Nutrients concentration	Nutrients concentration	Nutrients concentration	Nutrients concentration	Nutrients concentration	Nutrients concentration	Chlorophyll a concentration in water column	Chlorophyll a concentration in water column	Potentially toxic phytoplankton - metabarcoding	Potentially toxic phytoplankton - metabarcoding	Noctiluca scintillans biomass (%)	Transparency	Transparency	Oxygen Saturation	Oxygen Saturation	BLK-BG-D5C6-EI_biom (Ecological index-EQR biomass)	Proportin of tolerant macroalgae species biomass	Total projected cover of macroalgae tolerant species -lower infralitoral	BLK_BG_D5C7- Max_depth_distr_E. bosph.	BLK_BG_D5C7- Max_depth_distr_G.barb.	BLK_BG_D5C7- Max_depth_distr_sens_sp_low_inf	BLK_BG_D5C7- Prop_sens-sp_biom	BLK_BG_D5C7-EI _biom (Ecological index - biomass)	BLK_BG_D5C7- EI_cov	BLK_BG_D5C7- Cov_sens_sp_low_inf	M-AMBI(n)
Criteria status	Good	Good	Not good	Not good	Not good	Not good	Good	Good	Good	Good	Not assessed	Not assessed	Unknown	Not good	Not good	Not good	Not good	Good	Good	Good	Good	Good	Good	Good	Good	Good	Good	Not good
Description criteria
Element status	Good	Good	Not good	Not good	Not good	Not good	Good	Good	Good	Good	Not assessed	Not assessed	Not good	Not good	Not good	Not good	Not good	Good	Good	Good	Good	Good	Good	Good	Good	Good	Good	Not good
Description element
Integration rule type parameter
Integration rule description parameter
Integration rule type criteria	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO
Integration rule description criteria	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.
GES extent threshold	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00
GES extent achieved	72.00	72.00	72.00	72.00	72.00	72.00	72.00	72.00	72.00	72.00	72.00	72.00	72.00	72.00	72.00	72.00	72.00	72.00	72.00	72.00	72.00	72.00	72.00	72.00	72.00	72.00	72.00	72.00
GES extent unit	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status
GES achieved	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported
Description overall status
Assessments period	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017
Related pressures
Related targets	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS

Open sea (BLK-BG-AA-OpenSea)

Simplified table

GES component	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5
Feature	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication
Element	Dissolved ammonium nitrogen	Dissolved ammonium nitrogen	Dissolved inorganic phosphorus	Dissolved inorganic phosphorus	Dissolved nitrate nitrogen	Dissolved nitrate nitrogen	Dissolved nitrite nitrogen	Dissolved nitrite nitrogen	Chlorophyll-a	Chlorophyll-a	Molecular taxonomy of potentially toxic species	Molecular taxonomy of potentially toxic species	Noctiluca scintillans	Transparency	Transparency
Element code	DissolvedAmoniumNitrogen	DissolvedAmoniumNitrogen	DissolvedInorganicPhosphorus	DissolvedInorganicPhosphorus	DissolvedNitrateNitrogen	DissolvedNitrateNitrogen	DissolvedNitriteNitrogen	DissolvedNitriteNitrogen	EEA_3164-01-0	EEA_3164-01-0	Combined_K	Combined_K	109921	QE3-1-1	QE3-1-1
Element code source	Undefined	Undefined	Undefined	Undefined	Undefined	Undefined	Undefined	Undefined	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Undefined	Undefined	Species (D1) http://www.marinespecies.org/	Eutrophication (D5)(EQRs) http://dd.eionet.europa.eu/vocabulary/wise/ObservedPropertyBiologyEQR/view	Eutrophication (D5)(EQRs) http://dd.eionet.europa.eu/vocabulary/wise/ObservedPropertyBiologyEQR/view
Element 2
Element 2 code
Element 2 code source
Element source	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National
Criterion	D5C1	D5C1	D5C1	D5C1	D5C1	D5C1	D5C1	D5C1	D5C2	D5C2	D5C3	D5C3	D5C3	D5C4	D5C4
Parameter	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other
Parameter other	N-NH4 concentration in the water (spring)	N-NH4 concentration in the water (summer)	DIP concentration in the water (spring)	DIP concentration in the water (summer)	N-NO3 concentration in the water (spring)	N-NO3 concentration in the water (summer)	N-NO2 concentration in the water (spring)	N-NO2 concentration in the water (summer)	Chlorophyll a concentration in the water (spring)	Chlorophyll a concentration in the water (summer)	Number of potentially toxic species	Number of sequences of potentially toxic species	Noctiluca scintillans biomass	Transparency of water (spring)	Transparency of water (summer)
Threshold value upper	0.5	0.6	0.1	0.08	0.5	0.25	0.08	0.08	0.4	0.36			30.0	10.0	13.0
Threshold value lower									0.3	0.36				8.0	11.0
Threshold qualitative
Threshold value source
Threshold value source other
Value achieved upper	0.64	0.39	0.33	0.135	0.68	0.31	0.094	0.107	0.7	1.61				10.0	17.0
Value achieved lower	0.19	0.07	0.009	0.022	0.03	0.08	0.002	0.043	0.27	0.14				4.0	9.0
Value unit	micromole per litre	micromole per litre	micromole per litre	microgram per litre	micromole per litre	microgram per litre	micromole per litre	microgram per litre	microgram per litre	microgram per litre			percentage	metre	metre
Value unit other
Proportion threshold value	90.0	90.0	90.0	90.0	90.0	90.0	90.0	90.0	90.0	91.0			90.0	90.0
Proportion value achieved
Proportion threshold value unit	% area of MRU achieving threshold value	% area of MRU achieving threshold value	% area of MRU achieving threshold value	% area of MRU achieving threshold value	% area of MRU achieving threshold value	% area of MRU achieving threshold value	% area of MRU achieving threshold value	% area of MRU achieving threshold value	% area of MRU achieving threshold value				% area of MRU achieving threshold value	% area of MRU achieving threshold value
Trend	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown
Parameter achieved	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Unknown	Not assessed	Not assessed
Description parameter									This parameter was not assessed due to insufficient spatial coverage during the assessed period.	This parameter was not assessed due to insufficient spatial coverage during the assessed period.			This parameter was not assessed due to insufficient spatial coverage during the assessed period	This parameter was not assessed due to insufficient spatial coverage during the assessed period.	This parameter was not assessed due to insufficient spatial coverage during the assessed period.
Related indicator	Nutrients concentration	Nutrients concentration	Nutrients concentration	Nutrients concentration	Nutrients concentration	Nutrients concentration	Nutrients concentration	Nutrients concentration	Chlorophyll a concentration in water column	Chlorophyll a concentration in water column	Potentially toxic phytoplankton - metabarcoding	Potentially toxic phytoplankton - metabarcoding	Noctiluca scintillans biomass (%)	Transparency	Transparency
Criteria status	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Unknown	Unknown	Unknown
Description criteria
Element status	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Unknown	Unknown	Not assessed	Not assessed	Not good	Unknown	Unknown
Description element
Integration rule type parameter
Integration rule description parameter
Integration rule type criteria
Integration rule description criteria
GES extent threshold	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00
GES extent achieved
GES extent unit	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status
GES achieved	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown
Description overall status
Assessments period	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017
Related pressures
Related targets	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB

Shelf (BLK-BG-AA-Shelf)

Simplified table

GES component	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5
Feature	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication
Element	Dissolved ammonium nitrogen	Dissolved ammonium nitrogen	Dissolved inorganic phosphorus	Dissolved inorganic phosphorus	Dissolved nitrate nitrogen	Dissolved nitrate nitrogen	Dissolved nitrite nitrogen	Dissolved nitrite nitrogen	Chlorophyll-a	Chlorophyll-a	Molecular taxonomy of potentially toxic species	Molecular taxonomy of potentially toxic species	Noctiluca scintillans	Transparency	Transparency	Benthic habitats - macrobenthic communities
Element code	DissolvedAmoniumNitrogen	DissolvedAmoniumNitrogen	DissolvedInorganicPhosphorus	DissolvedInorganicPhosphorus	DissolvedNitrateNitrogen	DissolvedNitrateNitrogen	DissolvedNitriteNitrogen	DissolvedNitriteNitrogen	EEA_3164-01-0	EEA_3164-01-0	Combined_K	Combined_K	109921	QE3-1-1	QE3-1-1
Element code source	Undefined	Undefined	Undefined	Undefined	Undefined	Undefined	Undefined	Undefined	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Undefined	Undefined	Species (D1) http://www.marinespecies.org/	Eutrophication (D5)(EQRs) http://dd.eionet.europa.eu/vocabulary/wise/ObservedPropertyBiologyEQR/view	Eutrophication (D5)(EQRs) http://dd.eionet.europa.eu/vocabulary/wise/ObservedPropertyBiologyEQR/view
Element 2
Element 2 code
Element 2 code source
Element source	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National
Criterion	D5C1	D5C1	D5C1	D5C1	D5C1	D5C1	D5C1	D5C1	D5C2	D5C2	D5C3	D5C3	D5C3	D5C4	D5C4	D5C8
Parameter	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other
Parameter other	N-NH4 concentration in the water (spring)	N-NH4 concentration in the water (summer)	DIP concentration in the water (spring)	DIP concentration in the water (summer)	N-NO3 concentration in the water (spring)	N-NO3 concentration in the water (summer)	N-NO2 concentration in the water (spring)	N-NO2 concentration in the water (summer)	Chlorophyll a concentration in the water (spring)	Chlorophyll a concentration in the water (summer)	Number of potentially toxic species	Number of sequences of potentially toxic species	Noctiluca scintillans biomass	Transparency of water (spring)	Transparency of water (summer)	EQR M-AMBI(n)
Threshold value upper	0.5	0.6	0.1	0.08	0.5	0.25	0.08	0.08	1.4	1.2			30.0	6.5	7.7	0.68
Threshold value lower									1.4	1.2				5.8	6.5
Threshold qualitative
Threshold value source																Water Framework Directive (2000/60/EC)
Threshold value source other
Value achieved upper	1.63	0.55	0.335	0.17	6.03	2.42	0.273	0.122	2.13	4.6				10.0	19.0	1.0
Value achieved lower	0.08	0.02	0.046	0.018	0.03	0.13	0.003	0.025	0.26	0.23				3.5	4.5	0.46
Value unit	micromole per litre	micromole per litre	micromole per litre	microgram per litre	micromole per litre	microgram per litre	micromole per litre	microgram per litre	microgram per litre	microgram per litre			percentage	metre	metre
Value unit other
Proportion threshold value	90.0	90.0	90.0	90.0	90.0	90.0	90.0	90.0	90.0	90.0			90.0	90.0	90.0
Proportion value achieved	62.0	96.0	21.0	63.0	47.0	71.0	59.0	63.0	97.0				5.0	71.0		90.4
Proportion threshold value unit	% area of MRU achieving threshold value	% area of MRU achieving threshold value	% area of MRU achieving threshold value	% area of MRU achieving threshold value	% area of MRU achieving threshold value	% area of MRU achieving threshold value	% area of MRU achieving threshold value	% area of MRU achieving threshold value	% area of MRU achieving threshold value	% area of MRU achieving threshold value			% area of MRU achieving threshold value	% area of MRU achieving threshold value	% area of MRU achieving threshold value	% area of MRU achieving threshold value
Trend	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown
Parameter achieved	No	Yes	No	No	No	No	No	No	Yes	Not assessed	Not assessed	Not assessed	No	No	Not assessed	Yes
Description parameter										This parameter was not assessed due to insufficient spatial coverage during the assessed period					This parameter was not assessed due to insufficient spatial coverage during the assessed period	Although specific proportion threshold is not set for D5C8, the proportion 90.4 % of the seabed over which the EQR threshold value set has been achieved is sufficient to reach the overall GES proportion threshold of 90 %, if the other parameters were achieved too.
Related indicator	Nutrients concentration	Nutrients concentration	Nutrients concentration	Nutrients concentration	Nutrients concentration	Nutrients concentration	Nutrients concentration	Nutrients concentration	Chlorophyll a concentration in water column	Chlorophyll a concentration in water column	Potentially toxic phytoplankton - metabarcoding	Potentially toxic phytoplankton - metabarcoding	Noctiluca scintillans biomass (%)	Transparency	Transparency	M-AMBI(n)
Criteria status	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Unknown	Unknown	Not assessed	Not assessed	Unknown	Unknown	Unknown	Good
Description criteria
Element status	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Unknown	Unknown	Not assessed	Not assessed	Not good	Unknown	Unknown	Good
Description element
Integration rule type parameter
Integration rule description parameter
Integration rule type criteria	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO
Integration rule description criteria
GES extent threshold	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00
GES extent achieved
GES extent unit	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status
GES achieved	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown
Description overall status
Assessments period	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017
Related pressures
Related targets	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB

Sivriburun-Kaliakra (BLK-BG-AA-SivriburunKaliakra)

Simplified table

GES component	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5	D5
Feature	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication	Eutrophication
Element	Dissolved ammonium nitrogen	Dissolved ammonium nitrogen	Dissolved inorganic phosphorus	Dissolved inorganic phosphorus	Dissolved nitrate nitrogen	Dissolved nitrate nitrogen	Dissolved nitrite nitrogen	Dissolved nitrite nitrogen	Chlorophyll-a	Chlorophyll-a	Molecular taxonomy of potentially toxic species	Molecular taxonomy of potentially toxic species	Noctiluca scintillans	Transparency	Transparency	Oxygen saturation	Oxygen saturation	Benthic habitats - opportunistic macroalgae	Benthic habitats - opportunistic macroalgae	Benthic habitats - opportunistic macroalgae	Benthic habitats - macrophyte communities	Benthic habitats - macrophyte communities	Benthic habitats - macrophyte communities	Benthic habitats - macrophyte communities	Benthic habitats - macrophyte communities	Benthic habitats - macrophyte communities	Benthic habitats - macrophyte communities	Benthic habitats - macrobenthic communities
Element code	DissolvedAmoniumNitrogen	DissolvedAmoniumNitrogen	DissolvedInorganicPhosphorus	DissolvedInorganicPhosphorus	DissolvedNitrateNitrogen	DissolvedNitrateNitrogen	DissolvedNitriteNitrogen	DissolvedNitriteNitrogen	EEA_3164-01-0	EEA_3164-01-0	Combined_K	Combined_K	109921	QE3-1-1	QE3-1-1	EEA_3131-01-9	EEA_3131-01-9	QE1-2-1	QE1-2-1	QE1-2-1	QE1-2-2	QE1-2-2	QE1-2-2	QE1-2-2	QE1-2-2	QE1-2-2	QE1-2-2
Element code source	Undefined	Undefined	Undefined	Undefined	Undefined	Undefined	Undefined	Undefined	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Undefined	Undefined	Species (D1) http://www.marinespecies.org/	Eutrophication (D5)(EQRs) http://dd.eionet.europa.eu/vocabulary/wise/ObservedPropertyBiologyEQR/view	Eutrophication (D5)(EQRs) http://dd.eionet.europa.eu/vocabulary/wise/ObservedPropertyBiologyEQR/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5)(EQRs) http://dd.eionet.europa.eu/vocabulary/wise/ObservedPropertyBiologyEQR/view	Eutrophication (D5)(EQRs) http://dd.eionet.europa.eu/vocabulary/wise/ObservedPropertyBiologyEQR/view	Eutrophication (D5)(EQRs) http://dd.eionet.europa.eu/vocabulary/wise/ObservedPropertyBiologyEQR/view	Eutrophication (D5)(EQRs) http://dd.eionet.europa.eu/vocabulary/wise/ObservedPropertyBiologyEQR/view	Eutrophication (D5)(EQRs) http://dd.eionet.europa.eu/vocabulary/wise/ObservedPropertyBiologyEQR/view	Eutrophication (D5)(EQRs) http://dd.eionet.europa.eu/vocabulary/wise/ObservedPropertyBiologyEQR/view	Eutrophication (D5)(EQRs) http://dd.eionet.europa.eu/vocabulary/wise/ObservedPropertyBiologyEQR/view	Eutrophication (D5)(EQRs) http://dd.eionet.europa.eu/vocabulary/wise/ObservedPropertyBiologyEQR/view	Eutrophication (D5)(EQRs) http://dd.eionet.europa.eu/vocabulary/wise/ObservedPropertyBiologyEQR/view	Eutrophication (D5)(EQRs) http://dd.eionet.europa.eu/vocabulary/wise/ObservedPropertyBiologyEQR/view
Element 2
Element 2 code
Element 2 code source
Element source	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National
Criterion	D5C1	D5C1	D5C1	D5C1	D5C1	D5C1	D5C1	D5C1	D5C2	D5C2	D5C3	D5C3	D5C3	D5C4	D5C4	D5C5	D5C5	D5C6	D5C6	D5C6	D5C7	D5C7	D5C7	D5C7	D5C7	D5C7	D5C7	D5C8
Parameter	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other
Parameter other	N-NH4 concentration in the water (spring)	N-NH4 concentration in the water (summer)	DIP concentration in the water (spring)	DIP concentration in the water (summer)	N-NO3 concentration in the water (spring)	N-NO3 concentration in the water (summer)	N-NO2 concentration in the water (spring)	N-NO2 concentration in the water (summer)	Chlorophyll a concentration in the water (spring)	Chlorophyll a concentration in the water (summer)	Number of potentially toxic species	Number of sequences of potentially toxic species	Noctiluca scintillans biomass	Transparency of water (spring)	Transparency of water (summer)	Oxygen saturation in the surface water (spring)	Oxygen saturation in the surface water (summer)	Proportion of sensitive and tolerant macroalgae species biomass	Proportion of tolerant macroalgae species biomass	Total projected cover of macroalgae tolerant species (lower infralittoral)	Maximal depth distribution of Ericaria bosphorica (Cystoseira crinitaf.bosphorica	Maximal depth distribution of Gongolaria barbata (Cystoseira barbata	Maximal depth distribution of Phyllophora crispa and other sciophylic sensitive macroalgae (lower infralitoral)	Proportion of sensitive macroalgae species biomass	Proportion of sensitive and tolerant macroalgae species biomass	Proportion of sensitive and tolerant macroalgae species cover (Ecological index- EQR-cover)	Total projected cover of macroalgae sensitive species of Phyllophora crispa and other sciophylic sensitive macroalgae (lower infralittoral)	EQR M-AMBI(n)
Threshold value upper	0.9	0.7	0.15	0.15	1.0	0.3	0.3	0.12	3.4	1.5			30.0	4.7	5.2	116.0	110.0	1.0	0.4					1.0	1.0	1.0		0.68
Threshold value lower									3.4					4.7	5.2	105.0	95.0	0.644						0.6	0.644	0.664
Threshold qualitative
Threshold value source																		National		National	National	National	National	National	National	National	National	Water Framework Directive (2000/60/EC)
Threshold value source other
Value achieved upper	1.41	0.56	0.178	0.196	5.71	0.52	0.281	0.103	4.45	7.39				6.0	12.0	115.0	108.0											1.0
Value achieved lower	0.48	0.23	0.109	0.058	0.76	0.05	0.187	0.047	0.62	0.26				3.0	3.5	100.0	104.0											0.34
Value unit	micromole per litre	micromole per litre	micromole per litre	microgram per litre	micromole per litre	microgram per litre	micromole per litre	microgram per litre	microgram per litre	microgram per litre			percentage	metre	metre	percentage	percentage	ratio	ratio	percentage	metre	metre	metre	ratio	ratio	ratio	percentage	Other
Value unit other																												EQR
Proportion threshold value	90.0	90.0	90.0	90.0	90.0	90.0	90.0	90.0	90.0	90.0			90.0	90.0	90.0	90.0	90.0
Proportion value achieved	87.2	100.0	86.0	90.0	15.0	49.0	100.0	100.0	100.0	84.0				19.0	100.0	96.0	100.0	100.0	100.0					100.0	100.0	75.0		65.8
Proportion threshold value unit	% area of MRU achieving threshold value	% area of MRU achieving threshold value	% area of MRU achieving threshold value	% area of MRU achieving threshold value	% area of MRU achieving threshold value	% area of MRU achieving threshold value	% area of MRU achieving threshold value	% area of MRU achieving threshold value	% area of MRU achieving threshold value	% area of MRU achieving threshold value			% area of MRU achieving threshold value	% area of MRU achieving threshold value	% area of MRU achieving threshold value	% area of MRU achieving threshold value	% area of MRU achieving threshold value	% of stations achieving threshold value	% of stations achieving threshold value	% of stations achieving threshold value	% of stations achieving threshold value	% of stations achieving threshold value	% of stations achieving threshold value	% of stations achieving threshold value	% of stations achieving threshold value	% of stations achieving threshold value	% of stations achieving threshold value	% area of MRU achieving threshold value
Trend	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown
Parameter achieved	No	Yes	No	Yes	No	No	Yes	Yes	Yes	No	Not assessed	Not assessed	No	No	Yes	Yes	Yes	Yes	Yes	Not assessed	Not assessed	Not assessed	Not assessed	Yes	Yes	Yes	Not assessed	No
Description parameter																				This indicator was not assessed, due to insufficient data.	This parameter was not assessed due to unsufficient data.	This parameter was not assessed due to insufficient data.	This parameter was not assessed due to unsufficient data.	The proportion of the MRU assessment is based only on the results for some of the stations (polygons) monitored during the assessment period (not all stations (polygons) from the monitoring program have been assessed). .	The proportion of the MRU assessment is based only on the results for some of the stations (polygons) monitored during the assessment period (not all stations (polygons) from the monitoring program have been assessed). .		This parameter was not assessed due to unsufficient data.	Although specific proportion threshold is not set for D5C8, the proportion 65.8 % of the seabed over which the EQR threshold value set has been achieved is insufficient to reach the overall GES proportion threshold of 90 %.
Related indicator	Nutrients concentration	Nutrients concentration	Nutrients concentration	Nutrients concentration	Nutrients concentration	Nutrients concentration	Nutrients concentration	Nutrients concentration	Chlorophyll a concentration in water column	Chlorophyll a concentration in water column	Potentially toxic phytoplankton - metabarcoding	Potentially toxic phytoplankton - metabarcoding	Noctiluca scintillans biomass (%)	Transparency	Transparency	Oxygen Saturation	Oxygen Saturation	BLK-BG-D5C6-EI_biom (Ecological index-EQR biomass)	Proportin of tolerant macroalgae species biomass	Total projected cover of macroalgae tolerant species -lower infralitoral	BLK_BG_D5C7- Max_depth_distr_E..bosph.	BLK_BG_D5C7- Max_depth_distr_.G_barb.	BLK_BG_D5C7- Max_depth_distr_sens_sp_low_inf	BLK_BG_D5C7- Prop_sens-sp_biom	BLK_BG_D5C7-EI _biom (Ecological index - biomass)	BLK_BG_D5C7- EI_cov	BLK_BG_D5C7- Cov_sens_sp_low_inf	M-AMBI(n)
Criteria status	Not good	Not good	Not good	Not good	Not good	Not good	Good	Good	Not good	Not good	Not assessed	Not assessed	Unknown	Not good	Not good	Good	Good	Good	Good	Good	Good	Good	Good	Good	Good	Good	Good	Unknown
Description criteria
Element status	Not good	Not good	Not good	Not good	Not good	Not good	Good	Good	Not good	Not good	Not assessed	Not assessed	Not good	Not good	Not good	Good	Good	Good	Good	Good	Good	Good	Good	Good	Good	Good	Good	Not good
Description element
Integration rule type parameter
Integration rule description parameter
Integration rule type criteria	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO
Integration rule description criteria	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.	TRIX and EQR M-AMBI(n) ecological indexes were used to integrate eutrophication indicators in the coastal MRUs. TRIX taking into consideration causes -nutrients (DIP and DIN) and effects (chlorophyll a and oxygen saturation) (Vollenweider et al. (1998)) and M-AMBI(n) (Sigovini et al., 2013) was used for assessing adverse effects on benthic macroinvertebrates.
GES extent threshold	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00	90.00
GES extent achieved	20.00	20.00	20.00	20.00	20.00	20.00	20.00	20.00	20.00	20.00	20.00	20.00	20.00	20.00	20.00	20.00	20.00	20.00	20.00	20.00	20.00	20.00	20.00	20.00	20.00	20.00	20.00	20.00
GES extent unit	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status	Proportion of area in good status
GES achieved	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported
Description overall status
Assessments period	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017	2012-2017
Related pressures
Related targets	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS	T_ BLK-BG-D5C4-SecchiDepth T_BLK-BG-D5C1_Nutrients T_BLK-BG-D5C2-CHL T_BLK-BG-D5C3_NsB% T_BLK-BG-D5C3_PHPh-MB T_BLK-BG-D5C5_OS