Art8-2024

Member State report / Art8-2024 / 2024 / D9 / Ireland / NE Atlantic: Celtic Seas

Report type	Member State report to Commission
MSFD Article	Art8
Report due	2024-10-15
GES Descriptor	D9 Contaminants in seafood
Member State	Ireland
Region/subregion	NE Atlantic: Celtic Seas
Report date	2026-04-09 13:40:20

ACS-IE-SD-022

Simplified table

Regional assessment area
Component MRUs
GES component	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9
Feature	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood
Element	Benzo(a)pyrene	Cadmium and its compounds	Cadmium and its compounds	Cadmium and its compounds	Cadmium and its compounds	Cadmium and its compounds	Cadmium and its compounds	Cadmium and its compounds	Dioxin-like polychlorinated biphenyls (12 PCB-DLs: 77,81,105,114,118,123,126,156,157,167,169,189)	Lead and its compounds	Lead and its compounds	Lead and its compounds	Lead and its compounds	Lead and its compounds	Lead and its compounds	Lead and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Non-dioxin like PCB (sum of 6 PCB: 28, 52, 101, 138, 153 and 180)	Non-dioxin like PCB (sum of 6 PCB: 28, 52, 101, 138, 153 and 180)	Non-dioxin like PCB (sum of 6 PCB: 28, 52, 101, 138, 153 and 180)	Non-dioxin like PCB (sum of 6 PCB: 28, 52, 101, 138, 153 and 180)	Non-dioxin like PCB (sum of 6 PCB: 28, 52, 101, 138, 153 and 180)	Non-dioxin like PCB (sum of 6 PCB: 28, 52, 101, 138, 153 and 180)	Sum of PAHs (Benzo(a)pyrene, Benzo(b)fluoranthene, Benzo(k)fluoranthene, Indeno(1,2,3-cd)pyrene)	Sum of PAHs (Benzo(a)pyrene, Benzo(b)fluoranthene, Benzo(k)fluoranthene, Indeno(1,2,3-cd)pyrene)	Sum of PAHs (Benzo(a)pyrene, Benzo(b)fluoranthene, Benzo(k)fluoranthene, Indeno(1,2,3-cd)pyrene)	Sum of dioxins (WHO-PCDD/F-TEQ)	Sum of dioxins (WHO-PCDD/F-TEQ)	Sum of dioxins (WHO-PCDD/F-TEQ)	Sum of dioxins (WHO-PCDD/F-TEQ)
Element extent
Trend element	Stable	Stable		Stable		Stable			Stable	Stable	Stable			Stable			Stable		Stable	Stable				Stable	Stable			Stable				Stable	Stable	Stable		Stable
Element 2	Bivalvia			Bivalvia	Crustacea; Bivalvia	Osteichthyes	Osteichthyes, Crustacea, Bivalvia, Cephalopoda	Ostrea edulis	Osteichthyes, Crustacea, Bivalvia, Cephalopoda		Bivalvia	Bivalvia	Mytilus spp	Osteichthyes	Osteichthyes, Crustacea, Bivalvia, Cephalopoda	Ostrea edulis		Mytilus spp	Osteichthyes	Osteichthyes, Bivalvia	Osteichthyes, Bivalvia	Osteichthyes, Crustacea, Bivalvia, Cephalopoda	Ostrea edulis		Bivalvia	Bivalvia	Mytilus edulis	Osteichthyes	Osteichthyes, Crustacea, Bivalvia, Cephalopoda		Crustacea; Bivalvia	Mytilus edulis		Mytilus edulis	Mytilus edulis	Osteichthyes
Element source	Foodstuffs	Foodstuffs		Foodstuffs		Foodstuffs			Foodstuffs	Foodstuffs	Foodstuffs			Foodstuffs			Foodstuffs		Foodstuffs	Foodstuffs				Foodstuffs	Foodstuffs			Foodstuffs				Foodstuffs	Foodstuffs	Foodstuffs		Foodstuffs
Criterion	D9C1		D9C1		D9C1		D9C1	D9C1	D9C1			D9C1	D9C1		D9C1	D9C1		D9C1			D9C1	D9C1	D9C1			D9C1	D9C1		D9C1	D9C1	D9C1		D9C1		D9C1
Parameter	CONC-B-Muscle		CONC-B-Muscle		CONC-B-Muscle			CONC-B-Muscle	CONC-B-Muscle			CONC-B-Muscle	CONC-B-Muscle			CONC-B-Muscle		CONC-B-Muscle			CONC-B-Muscle		CONC-B-Muscle			CONC-B-Muscle	CONC-B-Muscle		CONC-B-Muscle		CONC-B-Muscle				CONC-B-Muscle
Threshold value upper	5.0		0.05		0.05			1.0	6.5			1.5	1.5			1.5		0.5			0.5		0.5			75.0	75.0		75.0		5.0				3.5
Threshold value lower
Threshold value operator	<=		<=		<=			<=	<=			<=	<=			<=		<=			<=		<=			<=	<=		<=		<=				<=
Threshold qualitative
Threshold value source	Regulation on contaminants in foodstuffs (EC 1881/2006)		Regulation on contaminants in foodstuffs (EC 1881/2006)		Regulation on contaminants in foodstuffs (EC 1881/2006)			Regulation on contaminants in foodstuffs (EC 1881/2006)	Regulation on contaminants in foodstuffs (EC 1881/2006)			Regulation on contaminants in foodstuffs (EC 1881/2006)	Regulation on contaminants in foodstuffs (EC 1881/2006)			Regulation on contaminants in foodstuffs (EC 1881/2006)		Regulation on contaminants in foodstuffs (EC 1881/2006)			Regulation on contaminants in foodstuffs (EC 1881/2006)		Regulation on contaminants in foodstuffs (EC 1881/2006)			Regulation on contaminants in foodstuffs (EC 1881/2006)	Regulation on contaminants in foodstuffs (EC 1881/2006)		Regulation on contaminants in foodstuffs (EC 1881/2006)		Regulation on contaminants in foodstuffs (EC 1881/2006)				Regulation on contaminants in foodstuffs (EC 1881/2006)
Value achieved upper	3.573		0.001		0.36			3.571	0.049			0.25	0.59			0.04		0.05			0.01		0.09			4.447	2.678		0.939		17.49				0.177
Value achieved lower	0.034		0.001		0.02			0.31	0.031			0.02	0.03			0.01		0.009			0.01		0.01			0.197	0.377		0.189		0.372				0.162
Value unit	microgram per kilogram of wet weight		milligram per kilogram of wet weight		milligram per kilogram of wet weight			milligram per kilogram of wet weight	pg TEQ/g ww			milligram per kilogram of wet weight	milligram per kilogram of wet weight			milligram per kilogram of wet weight		milligram per kilogram of wet weight			milligram per kilogram of wet weight		milligram per kilogram of wet weight			microgram per kilogram of wet weight	microgram per kilogram of wet weight		microgram per kilogram of wet weight		microgram per kilogram of wet weight				pg TEQ/g ww
Proportion threshold value
Proportion value achieved	100.0		100.0		100.0			89.47368421	100.0			100.0	100.0			100.0		100.0			100.0		100.0			100.0	100.0		100.0		100.0				100.0
Proportion threshold value unit	% of samples achieving threshold value		% of samples achieving threshold value		% of samples achieving threshold value			% of samples achieving threshold value	% of samples achieving threshold value			% of samples achieving threshold value	% of samples achieving threshold value			% of samples achieving threshold value		% of samples achieving threshold value			% of samples achieving threshold value		% of samples achieving threshold value			% of samples achieving threshold value	% of samples achieving threshold value		% of samples achieving threshold value		% of samples achieving threshold value				% of samples achieving threshold value
Trend parameter	Stable		Stable		Stable			Stable	Stable			Stable	Stable			Stable		Stable			Stable		Stable			Stable	Stable		Stable		Stable				Stable
Parameter achieved	Yes		Yes		Yes			Yes	Yes			Yes	Yes			Yes		Yes			Yes		Yes			Yes	Yes		Yes		Yes				Yes
Description parameter	Parameter status is met for Benzo(a)pyrene in MRU ASC-IE-SD-022 in seafood as 100% of upperbound assessments in Cockle, Crassostrea gigas, Ensis siliqua, Mytilus spp and Ostrea edulis met the 90% threshold compliance critereon		Parameter status is met for Cadmium and its compounds in MRU ASC-IE-SD-023 in seafood as 100% of upperbound assessments in Lophius piscatorius, Pollachius pollachius met the 90% threshold compliance critereon		Parameter status is met for Cadmium and its compounds in MRU ASC-IE-SD-022 in seafood as 100% of upperbound assessments in Cockle, Ensis siliqua, and Mytilus Spp met the 90% threshold compliance critereon			Parameter status is met for Cadmium and its compounds in MRU ASC-IE-SD-022 in seafood as 89.4736842105263% of upperbound assessments in Ostrea edulis met the 90% threshold compliance critereon	Parameter status is met for Dioxin-like polychlorinated biphenyls (12 PCB-DLs: 77,81,105,114,118,123,126,156,157,167,169,189) in MRU ASC-IE-SD-022 in seafood as 100% of upperbound assessments in Mytilus spp met the 90% threshold compliance critereon			Parameter status is met for Lead and its compounds in MRU ASC-IE-SD-022 in seafood as 100% of upperbound assessments in Bivalvia, Cockle and Ensis siliqua met the 90% threshold compliance critereon	Parameter status is met for Lead and its compounds in MRU ASC-IE-SD-022 in seafood as 100% of upperbound assessments in Mytilus spp met the 90% threshold compliance critereon			Parameter status is met for Lead and its compounds in MRU ASC-IE-SD-022 in seafood as 100% of upperbound assessments in Ostrea edulis met the 90% threshold compliance critereon		Parameter status is met for Mercury and its compounds in MRU ASC-IE-SD-022 in seafood as 100% of upperbound assessments in Mytilus speciesmet the 90% threshold compliance critereon			Parameter status is met for Mercury and its compounds in MRU ASC-IE-SD-022 in seafood as 100% of upperbound assessments in Cockle and Ensis siliqua met the 90% threshold compliance critereon		Parameter status is met for Mercury and its compounds in MRU ASC-IE-SD-022 in seafood as 100% of upperbound assessments in Ostrea edulis met the 90% threshold compliance critereon			Parameter status is met for Non-dioxin like PCB (sum of 6 PCB: 28, 52, 101, 138, 153 and 180) in MRU ASC-IE-SD-022 in seafood as 100% of upperbound assessments in Bivalvia met the 90% threshold compliance critereon	Parameter status is met for Non-dioxin like PCB (sum of 6 PCB: 28, 52, 101, 138, 153 and 180) in MRU ASC-IE-SD-022 in seafood as 100% of upperbound assessments in Mytilus spp met the 90% threshold compliance critereon		Parameter status is met for Non-dioxin like PCB (sum of 6 PCB: 28, 52, 101, 138, 153 and 180) in MRU ASC-IE-SD-022 in seafood as 100% of upperbound assessments in Cockle Ensis siliqua and Ostrea edulis met the 90% threshold compliance critereon		Parameter status is met for Sum of PAHs (Benzo(a)pyrene, Benzo(b)fluoranthene, Benzo(k)fluoranthene, Indeno(1,2,3-cd)pyrene) in MRU ASC-IE-SD-022 in cuustacea and bivalves as > 90% of upperbound assessments in Cockle met the 90% threshold compliance critereon				Parameter status is met for Sum of dioxins (WHO-PCDD/F-TEQ) in MRU ASC-IE-SD-022 in seafood as 100% of upperbound assessments in Mytilus spp met the 90% threshold compliance critereon
Related indicator
Criteria status	Good						Good		Good						Good							Good							Good	Good			Good
Description criteria	The status of Benzo(a)pyrene in Bivalvia in MRU ACS-IE-MS-022 is Good based on greater than 90% of assessments meeting EU Reg. 1881/2006/EC. Trend status is Stable.						The status of Cadmium and its compounds in Osteichthyes, Crustacea, Bivalvia, Cephalopoda in MRU ACS-IE-MS-022 is Good based on greater than 90% of assessments meeting EU Reg. 1881/2006/EC. Trend status is Stable.		The status of Dioxin-like polychlorinated biphenyls (12 PCB-DLs: 77,81,105,114,118,123,126,156,157,167,169,189) in Osteichthyes, Crustacea, Bivalvia, Cephalopoda in MRU ACS-IE-MS-022 is Good based on greater than 90% of assessments meeting EU Reg. 1881/2006/EC. Trend status is Stable.						The status of Lead and its compounds in Osteichthyes, Crustacea, Bivalvia, Cephalopoda in MRU ACS-IE-MS-022 is Good based on greater than 90% of assessments meeting EU Reg. 1881/2006/EC. Trend status is Stable.							The status of Mercury and its compounds in Osteichthyes, Crustacea, Bivalvia, Cephalopoda in MRU ACS-IE-MS-022 is Good based on greater than 90% of assessments meeting EU Reg. 1881/2006/EC. Trend status is Stable.							The status of Non-dioxin like PCB (sum of 6 PCB: 28, 52, 101, 138, 153 and 180) in Osteichthyes, Crustacea, Bivalvia, Cephalopoda in MRU ACS-IE-MS-022 is Good based on greater than 90% of assessments meeting EU Reg. 1881/2006/EC. Trend status is Stable.	The status of Sum of PAHs (Benzo(a)pyrene, Benzo(b)fluoranthene, Benzo(k)fluoranthene, Indeno(1,2,3-cd)pyrene) in Bivalvia in MRU ACS-IE-MS-022 is Good based on greater than 90% of assessments meeting EU Reg. 1881/2006/EC. Trend status is Stable.			The status of Sum of dioxins (WHO-PCDD/F-TEQ) in Osteichthyes, Crustacea, Bivalvia, Cephalopoda in MRU ACS-IE-MS-022 is Good based on greater than 90% of assessments meeting EU Reg. 1881/2006/EC. Trend status is Stable.
Element status	Good	Good		Good		Good			Good	Good	Good			Good			Good		Good	Good				Good	Good			Good				Good	Good	Good		Good
Description element	The status of Benzo(a)pyrene is Good based on greater than 90% of assessments meeting PAH specific thresholds as per EU Reg. 1881/2006/EC. Element trend is Stable	The status of Cadmium and its compounds is Good based on greater than 90% of assessments meeting species specific thresholds for cephalopods and crustacea as per EU Reg. 1881/2006/EC. Element trend is Stable		The status of Cadmium and its compounds is Good based on greater than 90% of assessments meeting species specific thresholds as per EU Reg. 1881/2006/EC. Element trend is Stable		The status of Cadmium and its compounds is Good based on greater than 90% of assessments meeting species specific thresholds as per EU Reg. 1881/2006/EC. Element trend is Stable			The status of Dioxin-like polychlorinated biphenyls (12 PCB-DLs: 77,81,105,114,118,123,126,156,157,167,169,189) is Good based on greater than 90% of assessments meeting species specific thresholds for cephalopods and crustacea as per EU Reg. 1881/2006/EC. Element trend is Stable	The status of Lead and its compounds is Good based on greater than 90% of assessments meeting species specific thresholds for cephalopods and crustacea as per EU Reg. 1881/2006/EC. Element trend is Stable	The status of Lead and its compounds is Good based on greater than 90% of assessments meeting species specific thresholds as per EU Reg. 1881/2006/EC. Element trend is Stable			The status of Lead and its compounds in MRU ACS-IE-MS-022 is Good based on greater than 90% of assessments meeting species specific thresholds as per EU Reg. 1881/2006/EC. Element trend is Stable			The status of Mercury and its compounds is Good based on greater than 90% of assessments meeting species specific thresholds for cephalopods and crustacea as per EU Reg. 1881/2006/EC. Element trend is Stable		The status of Mercury and its compounds is Good based on greater than 90% of assessments meeting species specific thresholds as per EU Reg. 1881/2006/EC. Element trend is Stable	The status of Mercury and its compounds is Good based on greater than 90% of assessments meeting species specific thresholds as per EU Reg. 1881/2006/EC. Element trend is Stable				The status of Non-dioxin like PCB (sum of 6 PCB: 28, 52, 101, 138, 153 and 180) is Good based on greater than 90% of assessments meeting species specific thresholds for cephalopods and crustacea as per EU Reg. 1881/2006/EC. Element trend is Stable	The status of Non-dioxin like PCB (sum of 6 PCB: 28, 52, 101, 138, 153 and 180) is Good based on greater than 90% of assessments meeting species specific thresholds as per EU Reg. 1881/2006/EC. Element trend is Stable			The status of Non-dioxin like PCB (sum of 6 PCB: 28, 52, 101, 138, 153 and 180) is Good based on greater than 90% of assessments meeting species specific thresholds as per EU Reg. 1881/2006/EC. Element trend is Stable				The status of Sum of PAHs (Benzo(a)pyrene, Benzo(b)fluoranthene, Benzo(k)fluoranthene, Indeno(1,2,3-cd)pyrene) is Good based on greater than 90% of assessments meeting PAH specific thresholds as per EU Reg. 1881/2006/EC. Element trend is Stable	The status of Sum of dioxins (WHO-PCDD/F-TEQ) is Good based on greater than 90% of assessments meeting species specific thresholds for cephalopods and crustacea as per EU Reg. 1881/2006/EC. Element trend is Stable	The status of Sum of dioxins (WHO-PCDD/F-TEQ) is Good based on greater than 90% of assessments meeting species specific thresholds as per EU Reg. 1881/2006/EC. Element trend is Stable		The status of Sum of dioxins (WHO-PCDD/F-TEQ) is Good based on greater than 90% of assessments meeting species specific thresholds as per EU Reg. 1881/2006/EC. Element trend is Stable
Source assessment feature	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD
Reporting method feature	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D
Trend feature	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable
Integration rule type 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	Other	Other	Other	Other
Integration rule description parameter	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.
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	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	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80
GES extent unit	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status
GES achieved	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012
Description overall status	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.
Assessments period	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021
Related pressures	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
Related targets	IE-D9T1-MRU022	IE-D9T1-MRU022	IE-D9T1-MRU022	IE-D9T1-MRU022	IE-D9T1-MRU022	IE-D9T1-MRU022	IE-D9T1-MRU022	IE-D9T1-MRU022	IE-D9T1-MRU022	IE-D9T1-MRU022	IE-D9T1-MRU022	IE-D9T1-MRU022	IE-D9T1-MRU022	IE-D9T1-MRU022	IE-D9T1-MRU022	IE-D9T1-MRU022	IE-D9T1-MRU022	IE-D9T1-MRU022	IE-D9T1-MRU022	IE-D9T1-MRU022	IE-D9T1-MRU022	IE-D9T1-MRU022	IE-D9T1-MRU022	IE-D9T1-MRU022	IE-D9T1-MRU022	IE-D9T1-MRU022	IE-D9T1-MRU022	IE-D9T1-MRU022	IE-D9T1-MRU022	IE-D9T1-MRU022	IE-D9T1-MRU022	IE-D9T1-MRU022	IE-D9T1-MRU022	IE-D9T1-MRU022	IE-D9T1-MRU022	IE-D9T1-MRU022
Test TV	Yes	NA	Yes	NA	No	NA	NA	No	Yes	NA	NA	Yes	Yes	NA	NA	Yes	NA	Yes	NA	NA	Yes	NA	Yes	NA	NA	Yes	Yes	NA	Yes	NA	No	NA	NA	NA	Yes	NA
Test results	Correct	False	Correct	False	False	False	False	False	Correct	False	False	Correct	Correct	False	False	Correct	False	Correct	False	False	Correct	False	Correct	False	False	Correct	Correct	False	Correct	False	False	False	False	False	Correct	False

ACS-IE-SD-023

Simplified table

Regional assessment area
Component MRUs
GES component	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9	D9
Feature	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood	Contaminants - in seafood
Element	Benzo(a)pyrene	Cadmium and its compounds	Cadmium and its compounds	Cadmium and its compounds	Cadmium and its compounds	Cadmium and its compounds	Cadmium and its compounds	Cadmium and its compounds	Cadmium and its compounds	Cadmium and its compounds	Cadmium and its compounds	Cadmium and its compounds	Cadmium and its compounds	Cadmium and its compounds	Cadmium and its compounds	Cadmium and its compounds	Cadmium and its compounds	Cadmium and its compounds	Cadmium and its compounds	Cadmium and its compounds	Cadmium and its compounds	Dioxin-like polychlorinated biphenyls (12 PCB-DLs: 77,81,105,114,118,123,126,156,157,167,169,189)	Dioxin-like polychlorinated biphenyls (12 PCB-DLs: 77,81,105,114,118,123,126,156,157,167,169,189)	Lead and its compounds	Lead and its compounds	Lead and its compounds	Lead and its compounds	Lead and its compounds	Lead and its compounds	Lead and its compounds	Lead and its compounds	Lead and its compounds	Lead and its compounds	Lead and its compounds	Lead and its compounds	Lead and its compounds	Lead and its compounds	Lead and its compounds	Lead and its compounds	Lead and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Non-dioxin like PCB (sum of 6 PCB: 28, 52, 101, 138, 153 and 180)	Non-dioxin like PCB (sum of 6 PCB: 28, 52, 101, 138, 153 and 180)	Non-dioxin like PCB (sum of 6 PCB: 28, 52, 101, 138, 153 and 180)	Non-dioxin like PCB (sum of 6 PCB: 28, 52, 101, 138, 153 and 180)	Non-dioxin like PCB (sum of 6 PCB: 28, 52, 101, 138, 153 and 180)	Non-dioxin like PCB (sum of 6 PCB: 28, 52, 101, 138, 153 and 180)	Non-dioxin like PCB (sum of 6 PCB: 28, 52, 101, 138, 153 and 180)	Non-dioxin like PCB (sum of 6 PCB: 28, 52, 101, 138, 153 and 180)	Non-dioxin like PCB (sum of 6 PCB: 28, 52, 101, 138, 153 and 180)	Non-dioxin like PCB (sum of 6 PCB: 28, 52, 101, 138, 153 and 180)	Non-dioxin like PCB (sum of 6 PCB: 28, 52, 101, 138, 153 and 180)	Non-dioxin like PCB (sum of 6 PCB: 28, 52, 101, 138, 153 and 180)	Non-dioxin like PCB (sum of 6 PCB: 28, 52, 101, 138, 153 and 180)	Perfluorooctane sulfonic acid (PFOS) and its derivatives	Perfluorooctane sulfonic acid (PFOS) and its derivatives	Sum of dioxins (WHO-PCDD/F-TEQ)	Sum of dioxins (WHO-PCDD/F-TEQ)	Sum of dioxins (WHO-PCDD/F-TEQ)	Sum of dioxins (WHO-PCDD/F-TEQ)	Sum of dioxins (WHO-PCDD/F-TEQ)	Sum of dioxins (WHO-PCDD/F-TEQ)	Sum of dioxins (WHO-PCDD/F-TEQ)	Sum of dioxins (WHO-PCDD/F-TEQ)	Sum of dioxins (WHO-PCDD/F-TEQ)	Sum of dioxins (WHO-PCDD/F-TEQ)	Sum of dioxins (WHO-PCDD/F-TEQ)	Sum of dioxins (WHO-PCDD/F-TEQ)	Sum of dioxins (WHO-PCDD/F-TEQ)
Element extent
Trend element		Stable	Stable									Stable											Stable	Stable	Stable								Stable								Stable												Stable		Stable									Stable	Stable							Stable					Not assessed		Stable							Stable	Stable
Element 2	Bivalvia		Bivalvia	Clupea harengus	Dicentrarchus labrax	Gadus morhua	Melanogrammus aeglefinus	Merlangius merlangus	Merluccius merluccius	Mullus barbatus	Nephrops norvegicus	Osteichthyes	Osteichthyes	Osteichthyes	Osteichthyes, Crustacea, Bivalvia, Cephalopoda	Pleuronectes platessa	Raja clavata	Scomber scombrus	Scyliorhinus canicula	Solea solea	Thunnus spp.	Clupea harengus	Osteichthyes, Crustacea, Bivalvia, Cephalopoda		Bivalvia	Clupea harengus	Gadus morhua	Melanogrammus aeglefinus	Merlangius merlangus	Merluccius merluccius	Mullus barbatus	Nephrops norvegicus	Osteichthyes	Osteichthyes	Osteichthyes, Crustacea, Bivalvia, Cephalopoda	Pleuronectes platessa	Raja clavata	Scomber scombrus	Scyliorhinus canicula	Solea solea		Clupea harengus	Dicentrarchus labrax	Gadus morhua	Lepidorhombus whiffiagonis	Loligo vulgaris	Lophius piscatorius	Melanogrammus aeglefinus	Merlangius merlangus	Merluccius merluccius	Micromesistius poutassou	Mullus barbatus	Mytilus edulis	Nephrops norvegicus	Osteichthyes	Osteichthyes	Osteichthyes, Crustacea, Bivalvia, Cephalopoda	Pleuronectes platessa	Raja clavata	Scomber scombrus	Solea solea	Trachurus trachurus	Zeus faber		Bivalvia	Clupea harengus	Gadus morhua	Melanogrammus aeglefinus	Merlangius merlangus	Merluccius merluccius	Nephrops norvegicus	Osteichthyes	Osteichthyes	Osteichthyes, Crustacea, Bivalvia, Cephalopoda	Pleuronectes platessa	Scomber scombrus		Clupea harengus		Clupea harengus	Dicentrarchus labrax	Gadus morhua	Melanogrammus aeglefinus	Merlangius merlangus	Merluccius merluccius	Mytilus edulis	Osteichthyes	Osteichthyes	Pleuronectes platessa	Scomber scombrus	Solea solea
Element source		Foodstuffs	Foodstuffs									Foodstuffs											Foodstuffs	Foodstuffs	Foodstuffs								Foodstuffs								Foodstuffs												Foodstuffs		Foodstuffs									Foodstuffs	Foodstuffs							Foodstuffs					EU		Foodstuffs							Foodstuffs	Foodstuffs
Criterion	D9C1			D9C1	D9C1	D9C1	D9C1	D9C1	D9C1	D9C1	D9C1		D9C1	D9C1	D9C1	D9C1	D9C1	D9C1	D9C1	D9C1	D9C1	D9C1	D9C1			D9C1	D9C1	D9C1	D9C1	D9C1	D9C1	D9C1		D9C1	D9C1	D9C1	D9C1	D9C1	D9C1	D9C1		D9C1	D9C1	D9C1	D9C1	D9C1	D9C1	D9C1	D9C1	D9C1	D9C1	D9C1		D9C1		D9C1	D9C1	D9C1	D9C1	D9C1	D9C1	D9C1	D9C1			D9C1	D9C1	D9C1	D9C1	D9C1	D9C1		D9C1	D9C1	D9C1	D9C1	D9C1	D9C1	D9C1	D9C1	D9C1	D9C1	D9C1	D9C1	D9C1			D9C1	D9C1	D9C1	D9C1
Parameter	CONC-B-Muscle			CONC-B-Muscle	CONC-B-Muscle	CONC-B-Muscle	CONC-B-Muscle	CONC-B-Muscle	CONC-B-Muscle	CONC-B-Muscle	CONC-B-Muscle		CONC-B-Muscle	CONC-B-Muscle		CONC-B-Muscle	CONC-B-Muscle	CONC-B-Muscle	CONC-B-Muscle	CONC-B-Muscle	CONC-B-Muscle	CONC-B-Muscle	CONC-B-Muscle			CONC-B-Muscle	CONC-B-Muscle	CONC-B-Muscle	CONC-B-Muscle	CONC-B-Muscle	CONC-B-Muscle	CONC-B-Muscle		CONC-B-Muscle		CONC-B-Muscle	CONC-B-Muscle	CONC-B-Muscle	CONC-B-Muscle	CONC-B-Muscle		CONC-B-Muscle	CONC-B-Muscle	CONC-B-Muscle	CONC-B-Muscle	CONC-B-Muscle	CONC-B-Muscle	CONC-B-Muscle	CONC-B-Muscle	CONC-B-Muscle	CONC-B-Muscle	CONC-B-Muscle		CONC-B-Muscle		CONC-B-Muscle		CONC-B-Muscle	CONC-B-Muscle	CONC-B-Muscle	CONC-B-Muscle	CONC-B-Muscle	CONC-B-Muscle			CONC-B-Muscle	CONC-B-Muscle	CONC-B-Muscle	CONC-B-Muscle	CONC-B-Muscle	CONC-B-Muscle		CONC-B-Muscle		CONC-B-Muscle	CONC-B-Muscle	CONC-B-Muscle	CONC-B-Muscle		CONC-B-Muscle	CONC-B-Muscle	CONC-B-Muscle	CONC-B-Muscle	CONC-B-Muscle	CONC-B-Muscle			CONC-B-Muscle	CONC-B-Muscle	CONC-B-Muscle	CONC-B-Muscle
Threshold value upper	5.0			0.05	0.05	0.05	0.05	0.05	0.05	0.05	0.5		0.05	0.05		0.05	0.05	0.1	0.05	0.05	0.1	6.5	6.5			0.3	0.3	0.3	0.3	0.3	0.3	0.5		0.3		0.3	0.3	0.3	0.3	0.3		0.5	0.5	1.0	1.0	0.5	0.5	0.5	0.5	0.5	0.5	0.5		0.5		0.5		0.5	1.0	0.5	0.5	0.5	0.5			75.0	75.0	75.0	75.0	75.0	75.0		75.0		75.0	75.0	9.1	9.1		3.5	3.5	3.5	3.5	3.5	3.5			3.5	3.5	3.5	3.5
Threshold value lower
Threshold value operator	<=			<=	<=	<=	<=	<=	<=	<=	<=		<=	<=		<=	<=	<=	<=	<=	<=	<=	<=			<=	<=	<=	<=	<=	<=	<=		<=		<=	<=	<=	<=	<=		<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=		<=		<=		<=	<=	<=	<=	<=	<=			<=	<=	<=	<=	<=	<=		<=		<=	<=	<=	<=		<=	<=	<=	<=	<=	<=			<=	<=	<=	<=
Threshold qualitative
Threshold value source	Regulation on contaminants in foodstuffs (EC 1881/2006)			Regulation on contaminants in foodstuffs (EC 1881/2006)	Regulation on contaminants in foodstuffs (EC 1881/2006)	Regulation on contaminants in foodstuffs (EC 1881/2006)	Regulation on contaminants in foodstuffs (EC 1881/2006)	Regulation on contaminants in foodstuffs (EC 1881/2006)	Regulation on contaminants in foodstuffs (EC 1881/2006)	Regulation on contaminants in foodstuffs (EC 1881/2006)	Regulation on contaminants in foodstuffs (EC 1881/2006)		Regulation on contaminants in foodstuffs (EC 1881/2006)	Regulation on contaminants in foodstuffs (EC 1881/2006)		Regulation on contaminants in foodstuffs (EC 1881/2006)	Regulation on contaminants in foodstuffs (EC 1881/2006)	Regulation on contaminants in foodstuffs (EC 1881/2006)	Regulation on contaminants in foodstuffs (EC 1881/2006)	Regulation on contaminants in foodstuffs (EC 1881/2006)	Regulation on contaminants in foodstuffs (EC 1881/2006)	Regulation on contaminants in foodstuffs (EC 1881/2006)	Regulation on contaminants in foodstuffs (EC 1881/2006)			Regulation on contaminants in foodstuffs (EC 1881/2006)	Regulation on contaminants in foodstuffs (EC 1881/2006)	Regulation on contaminants in foodstuffs (EC 1881/2006)	Regulation on contaminants in foodstuffs (EC 1881/2006)	Regulation on contaminants in foodstuffs (EC 1881/2006)	Regulation on contaminants in foodstuffs (EC 1881/2006)	Regulation on contaminants in foodstuffs (EC 1881/2006)		Regulation on contaminants in foodstuffs (EC 1881/2006)		Regulation on contaminants in foodstuffs (EC 1881/2006)	Regulation on contaminants in foodstuffs (EC 1881/2006)	Regulation on contaminants in foodstuffs (EC 1881/2006)	Regulation on contaminants in foodstuffs (EC 1881/2006)	Regulation on contaminants in foodstuffs (EC 1881/2006)		Regulation on contaminants in foodstuffs (EC 1881/2006)	Regulation on contaminants in foodstuffs (EC 1881/2006)	Regulation on contaminants in foodstuffs (EC 1881/2006)	Regulation on contaminants in foodstuffs (EC 1881/2006)	Regulation on contaminants in foodstuffs (EC 1881/2006)	Regulation on contaminants in foodstuffs (EC 1881/2006)	Regulation on contaminants in foodstuffs (EC 1881/2006)	Regulation on contaminants in foodstuffs (EC 1881/2006)	Regulation on contaminants in foodstuffs (EC 1881/2006)	Regulation on contaminants in foodstuffs (EC 1881/2006)	Regulation on contaminants in foodstuffs (EC 1881/2006)		Regulation on contaminants in foodstuffs (EC 1881/2006)		Regulation on contaminants in foodstuffs (EC 1881/2006)		Regulation on contaminants in foodstuffs (EC 1881/2006)	Regulation on contaminants in foodstuffs (EC 1881/2006)	Regulation on contaminants in foodstuffs (EC 1881/2006)	Regulation on contaminants in foodstuffs (EC 1881/2006)	Regulation on contaminants in foodstuffs (EC 1881/2006)	Regulation on contaminants in foodstuffs (EC 1881/2006)			Regulation on contaminants in foodstuffs (EC 1881/2006)	Regulation on contaminants in foodstuffs (EC 1881/2006)	Regulation on contaminants in foodstuffs (EC 1881/2006)	Regulation on contaminants in foodstuffs (EC 1881/2006)	Regulation on contaminants in foodstuffs (EC 1881/2006)	Regulation on contaminants in foodstuffs (EC 1881/2006)		Regulation on contaminants in foodstuffs (EC 1881/2006)		Regulation on contaminants in foodstuffs (EC 1881/2006)	Regulation on contaminants in foodstuffs (EC 1881/2006)	EU	EU		Regulation on contaminants in foodstuffs (EC 1881/2006)	Regulation on contaminants in foodstuffs (EC 1881/2006)	Regulation on contaminants in foodstuffs (EC 1881/2006)	Regulation on contaminants in foodstuffs (EC 1881/2006)	Regulation on contaminants in foodstuffs (EC 1881/2006)	Regulation on contaminants in foodstuffs (EC 1881/2006)			Regulation on contaminants in foodstuffs (EC 1881/2006)	Regulation on contaminants in foodstuffs (EC 1881/2006)	Regulation on contaminants in foodstuffs (EC 1881/2006)	Regulation on contaminants in foodstuffs (EC 1881/2006)
Value achieved upper	17.49			0.004	0.002	0.001	0.001	0.001	0.001	0.001	0.13		0.14	0.14		0.001	0.001	0.06	0.005	0.001	0.01	0.266	0.227			0.01	0.02	0.02	0.02	0.01	0.02	0.03		0.03		0.04	0.007	0.09	0.005	0.02		0.06	0.04	0.22	0.19	0.04	0.189	0.216	0.18	0.33	0.047	0.12		0.15		0.074		0.12	0.12	0.06	0.19	0.146	0.111			13.91	0.541	0.31	0.484	0.528	2.193		0.31		0.369	4.434	0.3	0.1		0.281	0.173	0.158	0.158	0.158	0.158			0.16	0.171	0.158	0.158
Value achieved lower	2.963			0.001	0.002	0.001	0.001	0.001	0.001	0.001	0.02		0.001	0.001		0.001	0.001	0.002	0.005	0.001	0.004	0.266	0.009			0.007	0.007	0.007	0.007	0.004	0.02	0.02		0.004		0.004	0.007	0.007	0.005	0.007		0.027	0.04	0.04	0.04	0.023	0.081	0.09	0.091	0.08	0.047	0.12		0.07		0.074		0.04	0.12	0.01	0.049	0.05	0.06			0.31	0.315	0.31	0.336	0.528	0.54		0.31		0.369	2.676				0.281	0.173	0.158	0.158	0.158	0.158			0.16	0.158	0.158	0.158
Value unit	microgram per kilogram of wet weight			milligram per kilogram of wet weight	milligram per kilogram of wet weight	milligram per kilogram of wet weight	milligram per kilogram of wet weight	milligram per kilogram of wet weight	milligram per kilogram of wet weight	milligram per kilogram of wet weight	milligram per kilogram of wet weight		milligram per kilogram of wet weight	milligram per kilogram of wet weight		milligram per kilogram of wet weight	milligram per kilogram of wet weight	milligram per kilogram of wet weight	milligram per kilogram of wet weight	milligram per kilogram of wet weight	milligram per kilogram of wet weight	pg TEQ/g ww	pg TEQ/g ww			milligram per kilogram of wet weight	milligram per kilogram of wet weight	milligram per kilogram of wet weight	milligram per kilogram of wet weight	milligram per kilogram of wet weight	milligram per kilogram of wet weight	milligram per kilogram of wet weight		milligram per kilogram of wet weight		milligram per kilogram of wet weight	milligram per kilogram of wet weight	milligram per kilogram of wet weight	milligram per kilogram of wet weight	milligram per kilogram of wet weight		milligram per kilogram of wet weight	milligram per kilogram of wet weight	milligram per kilogram of wet weight	milligram per kilogram of wet weight	milligram per kilogram of wet weight	milligram per kilogram of wet weight	milligram per kilogram of wet weight	milligram per kilogram of wet weight	milligram per kilogram of wet weight	milligram per kilogram of wet weight	milligram per kilogram of wet weight		milligram per kilogram of wet weight		milligram per kilogram of wet weight		milligram per kilogram of wet weight	milligram per kilogram of wet weight	milligram per kilogram of wet weight	milligram per kilogram of wet weight	milligram per kilogram of wet weight	milligram per kilogram of wet weight			microgram per kilogram of wet weight	microgram per kilogram of wet weight	microgram per kilogram of wet weight	microgram per kilogram of wet weight	microgram per kilogram of wet weight	microgram per kilogram of wet weight		microgram per kilogram of wet weight		microgram per kilogram of wet weight	microgram per kilogram of wet weight	microgram per kilogram of wet weight	microgram per kilogram of wet weight		pg TEQ/g ww	pg TEQ/g ww	pg TEQ/g ww	pg TEQ/g ww	pg TEQ/g ww	pg TEQ/g ww			pg TEQ/g ww	pg TEQ/g ww	pg TEQ/g ww	pg TEQ/g ww
Proportion threshold value
Proportion value achieved	90.0			100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0		50.0	100.0		100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0			100.0	100.0	100.0	100.0	100.0	100.0	100.0		100.0		100.0	100.0	100.0	100.0	100.0		100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0		100.0		100.0		100.0	100.0	100.0	100.0	100.0	100.0			100.0	100.0	100.0	100.0	100.0	100.0		100.0		100.0	100.0	100.0	100.0		100.0	100.0	100.0	100.0	100.0	100.0			100.0	100.0	100.0	100.0
Proportion threshold value unit	% of samples achieving threshold value			% of samples achieving threshold value	% of samples achieving threshold value	% of samples achieving threshold value	% of samples achieving threshold value	% of samples achieving threshold value	% of samples achieving threshold value	% of samples achieving threshold value	% of samples achieving threshold value		% of samples achieving threshold value	% of samples achieving threshold value		% of samples achieving threshold value	% of samples achieving threshold value	% of samples achieving threshold value	% of samples achieving threshold value	% of samples achieving threshold value	% of samples achieving threshold value	% of samples achieving threshold value	% of samples achieving threshold value			% of samples achieving threshold value	% of samples achieving threshold value	% of samples achieving threshold value	% of samples achieving threshold value	% of samples achieving threshold value	% of samples achieving threshold value	% of samples achieving threshold value		% of samples achieving threshold value		% of samples achieving threshold value	% of samples achieving threshold value	% of samples achieving threshold value	% of samples achieving threshold value	% of samples achieving threshold value		% of samples achieving threshold value	% of samples achieving threshold value	% of samples achieving threshold value	% of samples achieving threshold value	% of samples achieving threshold value	% of samples achieving threshold value	% of samples achieving threshold value	% of samples achieving threshold value	% of samples achieving threshold value	% of samples achieving threshold value	% of samples achieving threshold value		% of samples achieving threshold value		% of samples achieving threshold value		% of samples achieving threshold value	% of samples achieving threshold value	% of samples achieving threshold value	% of samples achieving threshold value	% of samples achieving threshold value	% of samples achieving threshold value			% of samples achieving threshold value	% of samples achieving threshold value	% of samples achieving threshold value	% of samples achieving threshold value	% of samples achieving threshold value	% of samples achieving threshold value		% of samples achieving threshold value		% of samples achieving threshold value	% of samples achieving threshold value	% of samples achieving threshold value	% of samples achieving threshold value		% of samples achieving threshold value	% of samples achieving threshold value	% of samples achieving threshold value	% of samples achieving threshold value	% of samples achieving threshold value	% of samples achieving threshold value			% of samples achieving threshold value	% of samples achieving threshold value	% of samples achieving threshold value	% of samples achieving threshold value
Trend parameter	Stable			Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable		Stable	Stable		Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable			Stable	Stable	Stable	Stable	Stable	Stable	Stable		Stable		Stable	Stable	Stable	Stable	Stable		Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable		Stable		Stable		Stable	Stable	Stable	Stable	Stable	Stable			Stable	Stable	Stable	Stable	Stable	Stable		Stable		Stable	Stable	Not assessed	Not assessed		Stable	Stable	Stable	Stable	Stable	Stable			Stable	Stable	Stable	Stable
Parameter achieved	Yes			Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes		No	Yes		Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes			Yes	Yes	Yes	Yes	Yes	Yes	Yes		Yes		Yes	Yes	Yes	Yes	Yes		Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes		Yes		Yes		Yes	Yes	Yes	Yes	Yes	Yes			Yes	Yes	Yes	Yes	Yes	Yes		Yes		Yes	Yes	Yes	Yes		Yes	Yes	Yes	Yes	Yes	Yes			Yes	Yes	Yes	Yes
Description parameter	Parameter status is met for Benzo(a)pyrene in MRU ASC-IE-SD-023 in seafood as >90% of upperbound assessments in Bivalves met the 90% threshold compliance critereon			Parameter status is met for Cadmium and its compounds in MRU ASC-IE-SD-023 in seafood as 100% of upperbound assessments in Clupea harengus met the 90% threshold compliance critereon	Parameter status is met for Cadmium and its compounds in MRU ASC-IE-SD-023 in seafood as 100% of upperbound assessments in Dicentrarchus labrax met the 90% threshold compliance critereon	Parameter status is met for Cadmium and its compounds in MRU ASC-IE-SD-023 in seafood as 100% of upperbound assessments in Gadus morhua met the 90% threshold compliance critereon	Parameter status is met for Cadmium and its compounds in MRU ASC-IE-SD-023 in seafood as 100% of upperbound assessments in Melanogrammus aeglefinus met the 90% threshold compliance critereon	Parameter status is met for Cadmium and its compounds in MRU ASC-IE-SD-023 in seafood as 100% of upperbound assessments in Merlangius merlangus met the 90% threshold compliance critereon	Parameter status is met for Cadmium and its compounds in MRU ASC-IE-SD-023 in seafood as 100% of upperbound assessments in Merluccius merluccius met the 90% threshold compliance critereon	Parameter status is met for Cadmium and its compounds in MRU ASC-IE-SD-023 in seafood as 100% of upperbound assessments in Mullus barbatus met the 90% threshold compliance critereon	Parameter status is met for Cadmium and its compounds in MRU ASC-IE-SD-023 in seafood as 100% of upperbound assessments in Nephrops norvegicus met the 90% threshold compliance critereon		Parameter status is met for Cadmium and its compounds in MRU ASC-IE-SD-023 in seafood as 50% of upperbound assessments in Boarfish (Capros aper), fail to meet the 90% species specific threshold compliance critereon	Parameter status is met for Cadmium and its compounds in MRU ASC-IE-SD-023 in seafood as 50% of upperbound assessments in Boarfish (Capros aper), Eutrigla gurnardus , Glyptocephalus cynoglossus, Lepidorhombus whiffiagonis, Limaa limaa , Littorina littorea, Loligo vulgaris, Lophius budegassa , Micromesistius poutassou ,Microstomus kitt , Molva molva , Pollachius virens, Psetta maxima, Raja montagui , Scophthalmus rhombus, Squalus acanthias , Trachurus trachurus , Trisopterus luscus and Zeus faber met the 90% species specific threshold compliance critereon		Parameter status is met for Cadmium and its compounds in MRU ASC-IE-SD-023 in seafood as 100% of upperbound assessments in Pleuronectes platessa met the 90% threshold compliance critereon	Parameter status is met for Cadmium and its compounds in MRU ASC-IE-SD-023 in seafood as 100% of upperbound assessments in Raja clavata met the 90% threshold compliance critereon	Parameter status is met for Cadmium and its compounds in MRU ASC-IE-SD-023 in seafood as 100% of upperbound assessments in Scomber scombrus met the 90% threshold compliance critereon	Parameter status is met for Cadmium and its compounds in MRU ASC-IE-SD-023 in seafood as 100% of upperbound assessments in Scyliorhinus canicula met the 90% threshold compliance critereon	Parameter status is met for Cadmium and its compounds in MRU ASC-IE-SD-023 in seafood as 100% of upperbound assessments in Solea solea met the 90% threshold compliance critereon	Parameter status is met for Cadmium and its compounds in MRU ASC-IE-SD-023 in seafood as 100% of upperbound assessments in Thunnus alalunga met the 90% threshold compliance critereon	Parameter status is met for Dioxin-like polychlorinated biphenyls (12 PCB-DLs: 77,81,105,114,118,123,126,156,157,167,169,189) in MRU ASC-IE-SD-023 in seafood as 100% of upperbound assessments in Clupea harengus met the 90% threshold compliance critereon	Parameter status is met for Dioxin-like polychlorinated biphenyls (12 PCB-DLs: 77,81,105,114,118,123,126,156,157,167,169,189) in MRU ASC-IE-SD-023 in seafood as 100% of upperbound assessments in Dicentrarchus labrax, Gadus morhua, Loligo vulgaris, Lophius budegassa, Lophius budegassa,Melanogrammus aeglefinus, Merluccius merluccius, Molva molva,Pleuronectes platessa, Pollachius pollachius, Scomber scombrus, Solea solea met the 90% threshold compliance critereon for species specific threholds.			Parameter status is met for Lead and its compounds in MRU ASC-IE-SD-023 in seafood as 100% of upperbound assessments in Clupea harengus met the 90% threshold compliance critereon	Parameter status is met for Lead and its compounds in MRU ASC-IE-SD-023 in seafood as 100% of upperbound assessments in Gadus morhua met the 90% threshold compliance critereon	Parameter status is met for Lead and its compounds in MRU ASC-IE-SD-023 in seafood as 100% of upperbound assessments in Melanogrammus aeglefinus met the 90% threshold compliance critereon	Parameter status is met for Lead and its compounds in MRU ASC-IE-SD-023 in seafood as 100% of upperbound assessments in Merlangius merlangus met the 90% threshold compliance critereon	Parameter status is met for Lead and its compounds in MRU ASC-IE-SD-023 in seafood as 100% of upperbound assessments in Merluccius merluccius met the 90% threshold compliance critereon	Parameter status is met for Lead and its compounds in MRU ASC-IE-SD-023 in seafood as 100% of upperbound assessments in Mullus barbatus met the 90% threshold compliance critereon	Parameter status is met for Lead and its compounds in MRU ASC-IE-SD-023 in seafood as 100% of upperbound assessments in Nephrops norvegicus met the 90% threshold compliance critereon		Parameter status is met for Lead and its compounds in MRU ASC-IE-SD-023 in seafood as 100% of upperbound assessments in Boarfish (Capros aper), Cockle, Dicentrarchus labrax, Eutrigla gurnardus , Glyptocephalus cynoglossus , Lepidorhombus whiffiagonis, Limaa limaa , Littorina littorea , Loligo vulgaris, Lophius budegassa, Lophius piscatorius , Micromesistius poutassou , Microstomus kitt , Molva molva , Pollachius pollachius , Pollachius virens , Psetta maxima, Scophthalmus rhombus, Squalus acanthias, Thunnus alalunga, Trachurus trachurus , Trisopterus luscus and Zeus faber met the 90% threshold compliance critereon		Parameter status is met for Lead and its compounds in MRU ASC-IE-SD-023 in seafood as 100% of upperbound assessments in Pleuronectes platessa met the 90% threshold compliance critereon	Parameter status is met for Lead and its compounds in MRU ASC-IE-SD-023 in seafood as 100% of upperbound assessments in Raja clavata met the 90% threshold compliance critereon	Parameter status is met for Lead and its compounds in MRU ASC-IE-SD-023 in seafood as 100% of upperbound assessments in Scomber scombrus met the 90% threshold compliance critereon	Parameter status is met for Lead and its compounds in MRU ASC-IE-SD-023 in seafood as 100% of upperbound assessments in Scyliorhinus canicula met the 90% threshold compliance critereon	Parameter status is met for Lead and its compounds in MRU ASC-IE-SD-023 in seafood as 100% of upperbound assessments in Solea solea met the 90% threshold compliance critereon		Parameter status is met for Mercury and its compounds in MRU ASC-IE-SD-023 in seafood as 100% of upperbound assessments in Clupea harengus met the 90% threshold compliance critereon	Parameter status is met for Mercury and its compounds in MRU ASC-IE-SD-023 in seafood as 100% of upperbound assessments in Dicentrarchus labrax met the 90% threshold compliance critereon	Parameter status is met for Mercury and its compounds in MRU ASC-IE-SD-023 in seafood as 100% of upperbound assessments in Gadus morhua met the 90% threshold compliance critereon	Parameter status is met for Mercury and its compounds in MRU ASC-IE-SD-023 in seafood as 100% of upperbound assessments in Lepidorhombus whiffiagonis met the 90% threshold compliance critereon	Parameter status is met for Mercury and its compounds in MRU ASC-IE-SD-023 in seafood as 100% of upperbound assessments in Loligo vulgaris met the 90% threshold compliance critereon	Parameter status is met for Mercury and its compounds in MRU ASC-IE-SD-023 in seafood as 100% of upperbound assessments in Lophius piscatorius met the 90% threshold compliance critereon	Parameter status is met for Mercury and its compounds in MRU ASC-IE-SD-023 in seafood as 100% of upperbound assessments in Melanogrammus aeglefinus met the 90% threshold compliance critereon	Parameter status is met for Mercury and its compounds in MRU ASC-IE-SD-023 in seafood as 100% of upperbound assessments in Merlangius merlangus met the 90% threshold compliance critereon	Parameter status is met for Mercury and its compounds in MRU ASC-IE-SD-023 in seafood as 100% of upperbound assessments in Merluccius merluccius met the 90% threshold compliance critereon	Parameter status is met for Mercury and its compounds in MRU ASC-IE-SD-023 in seafood as 100% of upperbound assessments in Micromesistius poutassou met the 90% threshold compliance critereon	Parameter status is met for Mercury and its compounds in MRU ASC-IE-SD-023 in seafood as 100% of upperbound assessments in Mullus barbatus met the 90% threshold compliance critereon		Parameter status is met for Mercury and its compounds in MRU ASC-IE-SD-023 in seafood as 100% of upperbound assessments in Nephrops norvegicus met the 90% threshold compliance critereon		Parameter status is met for Mercury and its compounds in MRU ASC-IE-SD-023 in seafood as 100% of upperbound assessments in Boarfish, Eutrigla gurnardus, Limaa limaa , Lophius budegassa , Microstomus kitt , Molva molva , Pecten maximus, Phycis Phycis , Pollachius pollachius, Psetta maxima, Scophthalmus rhombus , Squalus acanthias, Thunnus alalunga, Trisopterus luscus met the 90% threshold compliance critereon for species specific thresholds.		Parameter status is met for Mercury and its compounds in MRU ASC-IE-SD-023 in seafood as 100% of upperbound assessments in Pleuronectes platessa met the 90% threshold compliance critereon	Parameter status is met for Mercury and its compounds in MRU ASC-IE-SD-023 in seafood as 100% of upperbound assessments in Raja clavata met the 90% threshold compliance critereon	Parameter status is met for Mercury and its compounds in MRU ASC-IE-SD-023 in seafood as 100% of upperbound assessments in Scomber scombrus met the 90% threshold compliance critereon	Parameter status is met for Mercury and its compounds in MRU ASC-IE-SD-023 in seafood as 100% of upperbound assessments in Solea solea met the 90% threshold compliance critereon	Parameter status is met for Mercury and its compounds in MRU ASC-IE-SD-023 in seafood as 100% of upperbound assessments in Trachurus trachurus met the 90% threshold compliance critereon	Parameter status is met for Mercury and its compounds in MRU ASC-IE-SD-023 in seafood as 100% of upperbound assessments in Zeus faber met the 90% threshold compliance critereon			Parameter status is met for Non-dioxin like PCB (sum of 6 PCB: 28, 52, 101, 138, 153 and 180) in MRU ASC-IE-SD-023 in seafood as 100% of upperbound assessments in Clupea harengus met the 90% threshold compliance critereon	Parameter status is met for Non-dioxin like PCB (sum of 6 PCB: 28, 52, 101, 138, 153 and 180) in MRU ASC-IE-SD-023 in seafood as 100% of upperbound assessments in Gadus morhua met the 90% threshold compliance critereon	Parameter status is met for Non-dioxin like PCB (sum of 6 PCB: 28, 52, 101, 138, 153 and 180) in MRU ASC-IE-SD-023 in seafood as 100% of upperbound assessments in Melanogrammus aeglefinus met the 90% threshold compliance critereon	Parameter status is met for Non-dioxin like PCB (sum of 6 PCB: 28, 52, 101, 138, 153 and 180) in MRU ASC-IE-SD-023 in seafood as 100% of upperbound assessments in Merlangius merlangus met the 90% threshold compliance critereon	Parameter status is met for Non-dioxin like PCB (sum of 6 PCB: 28, 52, 101, 138, 153 and 180) in MRU ASC-IE-SD-023 in seafood as 100% of upperbound assessments in Merluccius merluccius met the 90% threshold compliance critereon	Parameter status is met for Non-dioxin like PCB (sum of 6 PCB: 28, 52, 101, 138, 153 and 180) in MRU ASC-IE-SD-023 in seafood as 100% of upperbound assessments in Nephrops norvegicus met the 90% threshold compliance critereon		Parameter status is met for Non-dioxin like PCB (sum of 6 PCB: 28, 52, 101, 138, 153 and 180) in MRU ASC-IE-SD-023 in seafood as 100% of upperbound assessments in Lophius piscatorius, Microstomus kitt and Thunnus alalunga met the 90% threshold compliance critereon.		Parameter status is met for Non-dioxin like PCB (sum of 6 PCB: 28, 52, 101, 138, 153 and 180) in MRU ASC-IE-SD-023 in seafood as 100% of upperbound assessments in Pleuronectes platessa met the 90% threshold compliance critereon	Parameter status is met for Non-dioxin like PCB (sum of 6 PCB: 28, 52, 101, 138, 153 and 180) in MRU ASC-IE-SD-023 in seafood as 100% of upperbound assessments in Scomber scombrus met the 90% threshold compliance critereon	Parameter status is met for Perfluorooctane sulfonic acid (PFOS) and its derivatives in MRU ASC-IE-SD-023 in seafood as 100% of upperbound assessments in Gadus morhua, Merlangius merlangus, Melanogrammus aeglefinus , Merluccius merluccius, Lophius piscatorius, Pollachius pollachius, Lepidorhombus whiffiagonis and Thunnus alalunga met the 90% threshold compliance critereon	Parameter status is met for Perfluorooctane sulfonic acid (PFOS) and its derivatives in MRU ASC-IE-SD-023 in seafood as 100% of upperbound assessments in Clupea harengus met the 90% threshold compliance critereon		Parameter status is met for Sum of dioxins (WHO-PCDD/F-TEQ) in MRU ASC-IE-SD-023 in seafood as 100% of upperbound assessments in Clupea harengus met the 90% threshold compliance critereon	Parameter status is met for Sum of dioxins (WHO-PCDD/F-TEQ) in MRU ASC-IE-SD-023 in seafood as 100% of upperbound assessments in Dicentrarchus labrax met the 90% threshold compliance critereon	Parameter status is met for Sum of dioxins (WHO-PCDD/F-TEQ) in MRU ASC-IE-SD-023 in seafood as 100% of upperbound assessments in Gadus morhua met the 90% threshold compliance critereon	Parameter status is met for Sum of dioxins (WHO-PCDD/F-TEQ) in MRU ASC-IE-SD-023 in seafood as 100% of upperbound assessments in Melanogrammus aeglefinus met the 90% threshold compliance critereon	Parameter status is met for Sum of dioxins (WHO-PCDD/F-TEQ) in MRU ASC-IE-SD-023 in seafood as 100% of upperbound assessments in Merlangius merlangus met the 90% threshold compliance critereon	Parameter status is met for Sum of dioxins (WHO-PCDD/F-TEQ) in MRU ASC-IE-SD-023 in seafood as 100% of upperbound assessments in Merluccius merluccius met the 90% threshold compliance critereon			Parameter status is met for Sum of dioxins (WHO-PCDD/F-TEQ) in MRU ASC-IE-SD-023 in seafood as 100% of upperbound assessments in Loligo vulgaris, Lophius budegassa, Lophius piscatorius, Molva molva,Pollachius pollachius met the 90% threshold compliance critereon	Parameter status is met for Sum of dioxins (WHO-PCDD/F-TEQ) in MRU ASC-IE-SD-023 in seafood as 100% of upperbound assessments in Pleuronectes platessa met the 90% threshold compliance critereon	Parameter status is met for Sum of dioxins (WHO-PCDD/F-TEQ) in MRU ASC-IE-SD-023 in seafood as 100% of upperbound assessments in Scomber scombrus met the 90% threshold compliance critereon	Parameter status is met for Sum of dioxins (WHO-PCDD/F-TEQ) in MRU ASC-IE-SD-023 in seafood as 100% of upperbound assessments in Solea solea met the 90% threshold compliance critereon
Related indicator
Criteria status															Good								Good												Good																						Good																	Good			Good		Good
Description criteria															The status of Cadmium and its compounds in Osteichthyes, Crustacea, Bivalvia, Cephalopoda in MRU ACS-IE-MS-023 is Good based on greater than 90% of assessments meeting EU Reg. 1881/2006/EC. Trend status is Stable.								The status of Dioxin-like polychlorinated biphenyls (12 PCB-DLs: 77,81,105,114,118,123,126,156,157,167,169,189) in Osteichthyes, Crustacea, Bivalvia, Cephalopoda in MRU ACS-IE-MS-023 is Good based on greater than 90% of assessments meeting EU Reg. 1881/2006/EC. Trend status is Stable.												The status of Lead and its compounds in Osteichthyes, Crustacea, Bivalvia, Cephalopoda in MRU ACS-IE-MS-023 is Good based on greater than 90% of assessments meeting EU Reg. 1881/2006/EC. Trend status is Stable.																						The status of Mercury and its compounds in Osteichthyes, Crustacea, Bivalvia, Cephalopoda in MRU ACS-IE-MS-023 is Good based on greater than 90% of assessments meeting EU Reg. 1881/2006/EC. Trend status is Stable.																	The status of Non-dioxin like PCB (sum of 6 PCB: 28, 52, 101, 138, 153 and 180) in Osteichthyes, Crustacea, Bivalvia, Cephalopoda in MRU ACS-IE-MS-023 is Good based on greater than 90% of assessments meeting EU Reg. 1881/2006/EC. Trend status is Stable.			The status of Perfluorooctane sulfonic acid (PFOS) and its derivatives in Osteichthyes in MRU ACS-IE-MS-023 is Good based on greater than 90% of assessments meeting EU thresholds. Trend status is Unknown.		The status of Sum of dioxins (WHO-PCDD/F-TEQ) in Osteichthyes, Crustacea, Bivalvia, Cephalopoda in MRU ACS-IE-MS-023 is Good based on greater than 90% of assessments meeting EU Reg. 1881/2006/EC. Trend status is Stable.
Element status		Good	Good									Good											Good	Good	Good								Good								Good												Good		Good									Good	Good							Good					Good		Good							Good	Good
Description element		The status of Cadmium and its compounds is Good based on greater than 90% of assessments meeting species specific thresholds for cephalopods and crustacea as per EU Reg. 1881/2006/EC. Element trend is Stable	The status of Cadmium and its compounds is Good based on greater than 90% of assessments meeting species specific thresholds as per EU Reg. 1881/2006/EC. Element trend is Stable									The status of Cadmium and its compounds is Good based on greater than 90% of assessments meeting species specific thresholds as per EU Reg. 1881/2006/EC. Element trend is Stable											The status of Dioxin-like polychlorinated biphenyls (12 PCB-DLs: 77,81,105,114,118,123,126,156,157,167,169,189) is Good based on greater than 90% of assessments meeting species specific thresholds for cephalopods and crustacea as per EU Reg. 1881/2006/EC. Element trend is Stable	The status of Lead and its compounds is Good based on greater than 90% of assessments meeting species specific thresholds for cephalopods and crustacea as per EU Reg. 1881/2006/EC. Element trend is Stable	The status of Lead and its compounds is Good based on greater than 90% of assessments meeting species specific thresholds as per EU Reg. 1881/2006/EC. Element trend is Stable								The status of Lead and its compounds is Good based on greater than 90% of assessments meeting species specific thresholds as per EU Reg. 1881/2006/EC. Element trend is Stable								The status of Mercury and its compounds is Good based on greater than 90% of assessments meeting species specific thresholds for cephalopods and crustacea as per EU Reg. 1881/2006/EC. Element trend is Stable												The status of Mercury and its compounds is Good based on greater than 90% of assessments meeting species specific thresholds as per EU Reg. 1881/2006/EC. Element trend is Stable		The status of Mercury and its compounds is Good based on greater than 90% of assessments meeting species specific thresholds as per EU Reg. 1881/2006/EC. Element trend is Stable									The status of Non-dioxin like PCB (sum of 6 PCB: 28, 52, 101, 138, 153 and 180) is Good based on greater than 90% of assessments meeting species specific thresholds for cephalopods and crustacea as per EU Reg. 1881/2006/EC. Element trend is Stable	The status of Non-dioxin like PCB (sum of 6 PCB: 28, 52, 101, 138, 153 and 180) is Good based on greater than 90% of assessments meeting species specific thresholds as per EU Reg. 1881/2006/EC. Element trend is Stable							The status of Non-dioxin like PCB (sum of 6 PCB: 28, 52, 101, 138, 153 and 180) is Good based on greater than 90% of assessments meeting species specific thresholds as per EU Reg. 1881/2006/EC. Element trend is Stable					The status of Perfluorooctane sulfonic acid (PFOS) and its derivatives in Osteichthyes is Good based on greater than 90% of assessments meeting PAH specific thresholds as per EU Reg. 1881/2006/EC. Element trend is Not assessed		The status of Sum of dioxins (WHO-PCDD/F-TEQ) is Good based on greater than 90% of assessments meeting species specific thresholds for cephalopods and crustacea as per EU Reg. 1881/2006/EC. Element trend is Stable							The status of Sum of dioxins (WHO-PCDD/F-TEQ) is Good based on greater than 90% of assessments meeting species specific thresholds as per EU Reg. 1881/2006/EC. Element trend is Stable	The status of Sum of dioxins (WHO-PCDD/F-TEQ) is Good based on greater than 90% of assessments meeting species specific thresholds as per EU Reg. 1881/2006/EC. Element trend is Stable
Source assessment feature	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD	National WaterFD
Reporting method feature	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D	Type D
Trend feature	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable
Integration rule type 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	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	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
Integration rule description parameter	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.	At each sampling station substance concentrations in each matrix (water, biota and sediment) are compared against thresholds. If one matrix fails then the station fails for that specific substances (OOAO). A total of 90% or more stations must pass with no increasing trend in contaminants in shellfish for an MRU to be in GES for a substance. Integration rules for combining substance results have not been agreed at EU level and so feature results for each MRU are qualitative at this time.
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	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	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	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	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80	99.80
GES extent unit	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status
GES achieved	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012	GES achieved by 2012
Description overall status	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.	The level of contaminants as measured in edible tissue to seafood caught or harvested in the wild in Irish waters (excluding fin-fish from aquaculture) are below the relevant regulatory limits in Commission Regulation 2023/915.
Assessments period	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021
Related pressures	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
Related targets	IE-D9T1-MRU023	IE-D9T1-MRU023	IE-D9T1-MRU023	IE-D9T1-MRU023	IE-D9T1-MRU023	IE-D9T1-MRU023	IE-D9T1-MRU023	IE-D9T1-MRU023	IE-D9T1-MRU023	IE-D9T1-MRU023	IE-D9T1-MRU023	IE-D9T1-MRU023	IE-D9T1-MRU023	IE-D9T1-MRU023	IE-D9T1-MRU023	IE-D9T1-MRU023	IE-D9T1-MRU023	IE-D9T1-MRU023	IE-D9T1-MRU023	IE-D9T1-MRU023	IE-D9T1-MRU023	IE-D9T1-MRU023	IE-D9T1-MRU023	IE-D9T1-MRU023	IE-D9T1-MRU023	IE-D9T1-MRU023	IE-D9T1-MRU023	IE-D9T1-MRU023	IE-D9T1-MRU023	IE-D9T1-MRU023	IE-D9T1-MRU023	IE-D9T1-MRU023	IE-D9T1-MRU023	IE-D9T1-MRU023	IE-D9T1-MRU023	IE-D9T1-MRU023	IE-D9T1-MRU023	IE-D9T1-MRU023	IE-D9T1-MRU023	IE-D9T1-MRU023	IE-D9T1-MRU023	IE-D9T1-MRU023	IE-D9T1-MRU023	IE-D9T1-MRU023	IE-D9T1-MRU023	IE-D9T1-MRU023	IE-D9T1-MRU023	IE-D9T1-MRU023	IE-D9T1-MRU023	IE-D9T1-MRU023	IE-D9T1-MRU023	IE-D9T1-MRU023	IE-D9T1-MRU023	IE-D9T1-MRU023	IE-D9T1-MRU023	IE-D9T1-MRU023	IE-D9T1-MRU023	IE-D9T1-MRU023	IE-D9T1-MRU023	IE-D9T1-MRU023	IE-D9T1-MRU023	IE-D9T1-MRU023	IE-D9T1-MRU023	IE-D9T1-MRU023	IE-D9T1-MRU023	IE-D9T1-MRU023	IE-D9T1-MRU023	IE-D9T1-MRU023	IE-D9T1-MRU023	IE-D9T1-MRU023	IE-D9T1-MRU023	IE-D9T1-MRU023	IE-D9T1-MRU023	IE-D9T1-MRU023	IE-D9T1-MRU023	IE-D9T1-MRU023	IE-D9T1-MRU023	IE-D9T1-MRU023	IE-D9T1-MRU023	IE-D9T1-MRU023	IE-D9T1-MRU023	IE-D9T1-MRU023	IE-D9T1-MRU023	IE-D9T1-MRU023	IE-D9T1-MRU023	IE-D9T1-MRU023	IE-D9T1-MRU023	IE-D9T1-MRU023	IE-D9T1-MRU023	IE-D9T1-MRU023	IE-D9T1-MRU023
Test TV	No	NA	NA	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	NA	No	No	NA	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	NA	NA	Yes	Yes	Yes	Yes	Yes	Yes	Yes	NA	Yes	NA	Yes	Yes	Yes	Yes	Yes	NA	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	NA	Yes	NA	Yes	NA	Yes	Yes	Yes	Yes	Yes	Yes	NA	NA	Yes	Yes	Yes	Yes	Yes	Yes	NA	Yes	NA	Yes	Yes	Yes	Yes	NA	Yes	Yes	Yes	Yes	Yes	Yes	NA	NA	Yes	Yes	Yes	Yes
Test results	False	False	False	Correct	Correct	Correct	Correct	Correct	Correct	Correct	Correct	False	Correct	False	False	Correct	Correct	Correct	Correct	Correct	Correct	Correct	Correct	False	False	Correct	Correct	Correct	Correct	Correct	Correct	Correct	False	Correct	False	Correct	Correct	Correct	Correct	Correct	False	Correct	Correct	Correct	Correct	Correct	Correct	Correct	Correct	Correct	Correct	Correct	False	Correct	False	Correct	False	Correct	Correct	Correct	Correct	Correct	Correct	False	False	Correct	Correct	Correct	Correct	Correct	Correct	False	Correct	False	Correct	Correct	Correct	Correct	False	Correct	Correct	Correct	Correct	Correct	Correct	False	False	Correct	Correct	Correct	Correct