Art8-2024

Member State report / Art8-2024 / 2024 / D8 / Ireland / NE Atlantic: Celtic Seas

Report type	Member State report to Commission
MSFD Article	Art8
Report due	2024-10-15
GES Descriptor	D8 Contaminants
Member State	Ireland
Region/subregion	NE Atlantic: Celtic Seas
Report date	2026-04-09 13:40:20

Irish Assesment Area (ACS-IE-AA-001)

Simplified table

Regional assessment area
Component MRUs
GES component	D8
Feature	Acute pollution events
Element
Element extent
Trend element
Element 2
Element source
Criterion
Parameter
Threshold value upper
Threshold value lower
Threshold value operator
Threshold qualitative
Threshold value source
Value achieved upper
Value achieved lower
Value unit
Proportion threshold value
Proportion value achieved
Proportion threshold value unit
Trend parameter
Parameter achieved
Description parameter
Related indicator
Criteria status
Description criteria
Element status
Description element
Source assessment feature	Bonn Agreement National
Reporting method feature	Type C
Trend feature	Stable
Integration rule type parameter
Integration rule description parameter
Integration rule type criteria
Integration rule description criteria
GES extent threshold
GES extent achieved
GES extent unit
GES achieved	GES achieved by 2012
Description overall status	GES for acute pollution events has not been defined at a European level. Despite this it can be considered that Ireland has achieved GES. While some minor oil spills have been detected, no significant events have occurred in time frame of the assessment. Over the period 2016-2021 a total of 17 minor oil slicks were detected through national flight surveillance.
Assessments period	2016-2021
Related pressures	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
Related targets	IE-D8T1b-1-MRU016 IE-D8T1b-1-MRU017 IE-D8T1b-1-MRU018 IE-D8T1b-MRU016 IE-D8T1b-MRU017 IE-D8T1b-MRU018 IE-D8T3-MRU016 IE-D8T3-MRU017 IE-D8T3-MRU018
Test TV	NA
Test results	False

ACS-IE-MS-016

Simplified table

Regional assessment area	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea	OSPAR-Celtic Sea
Component MRUs
GES component	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8
Feature	Contaminants - UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Species	Acute pollution events
Element	Imposex	1,2,3-Trichlorobenzene	1,2,4-Trichlorobenzene	1,2-Dichloroethane	1,3,5-Trichlorobenzene	4-Nonylphenol	Aclonifen	Anthracene	Anthracene	Anthracene	Atrazine	BDE 85 (2,2’,3,4,4’-pentabromodiphenyl ether)	BDE-183 (2,2',3,4,4',5',6-heptabromodiphenyl ether)	BDE-183 (2,2',3,4,4',5',6-heptabromodiphenyl ether)	BDE-66 (2,3',4,4'-tetrabromodiphenyl ether)	Benz(a)anthracene	Benz(a)anthracene	Benzene	Bifenox	Cadmium and its compounds	Cadmium and its compounds	Cadmium and its compounds	Carbon tetrachloride	Chrysene	Chrysene	Cypermethrin	Di(2-ethylhexyl)phthalate (DEHP)	Dichloromethane	Dichlorvos	Dicofol	Diuron	Environmental UPBT contaminants - WFD UPBT substances	Fluoranthene	Fluoranthene	Fluoranthene	Hexachlorobenzene	Hexachlorobenzene	Isoproturon	Lead and its compounds	Lead and its compounds	Lead and its compounds	Naphthalene	Naphthalene	Nickel and its compounds	Nonylphenol	PAH	Phenanthrene	Phenanthrene	Pyrene	Pyrene	Quinoxyfen	Simazine	Terbutryn	Tetrachloroethylene	Trichloroethylene	Zinc and its compounds	Zinc and its compounds	BDE 100 (2,2’,4,4’,6-pentabromodiphenyl ether)	BDE 100 (2,2’,4,4’,6-pentabromodiphenyl ether)	BDE 153 (2,2’,4,4’,5,5’-hexabromodiphenyl ether)	BDE 153 (2,2’,4,4’,5,5’-hexabromodiphenyl ether)	BDE 154 (2,2’,4,4’,5,6’-hexabromodiphenyl ether)	BDE 154 (2,2’,4,4’,5,6’-hexabromodiphenyl ether)	BDE 28 (2,4,4-tribromodiphenyl ether)	BDE 28 (2,4,4-tribromodiphenyl ether)	BDE 47 (2,2’,4,4’-tetrabromodiphenyl ether)	BDE 47 (2,2’,4,4’-tetrabromodiphenyl ether)	BDE 99 (2,2’,4,4’,5-pentabromodiphenyl ether)	BDE 99 (2,2’,4,4’,5-pentabromodiphenyl ether)	Benzo(a)pyrene	Benzo(a)pyrene	Benzo(a)pyrene	Benzo(b)fluoranthene	Benzo(g,h,i)perylene	Benzo(g,h,i)perylene	Benzo(g,h,i)perylene	Benzo(k)fluoranthene	Hexabromocyclododecanes (HBCDD)	Indeno(1,2,3,-cd)pyrene	Indeno(1,2,3,-cd)pyrene	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	PAH	PBDE	PCB 101 (2,2’,4,5,5’-pentachlorobiphenyl)	PCB 101 (2,2’,4,5,5’-pentachlorobiphenyl)	PCB 118 (2,3’,4,4’,5-pentachlorobiphenyl)	PCB 118 (2,3’,4,4’,5-pentachlorobiphenyl)	PCB 138 (2,2’,3,4,4’,5’-hexachlorobiphenyl)	PCB 138 (2,2’,3,4,4’,5’-hexachlorobiphenyl)	PCB 153 (2,2’,4,4’,5,5’-hexachlorobiphenyl)	PCB 153 (2,2’,4,4’,5,5’-hexachlorobiphenyl)	PCB 180 (2,2’,3,4,4’,5,5’-heptachlorobiphenyl)	PCB 180 (2,2’,3,4,4’,5,5’-heptachlorobiphenyl)	PCB 28 (2,4,4’-trichlorobiphenyl)	PCB 28 (2,4,4’-trichlorobiphenyl)	PCB 52 (2,2’,5,5’-tetrachlorobiphenyl)	PCB 52 (2,2’,5,5’-tetrachlorobiphenyl)	PFOS	Polychlorinated biphenyls (7 PCB: 28,52,101,118,138,153,180)	TBT	TBT	TBT	benzo[a]anthracene; benzo[ghi]perylene; benzo[a]pyrene; chrysene; fluoranthene; indeno[1,2,3-cd]pyrene; pyrene; phenanthrene	Imposex
Element extent
Trend element	Improving																			Not assessed	Not assessed											Not assessed							Not assessed	Not assessed				Not assessed		Improving																																Not assessed			Not assessed	Not assessed		Stable	Not assessed															Not assessed	Improving	Not assessed	Not assessed	Not assessed
Element 2	Nucella lapillus									Mytilus spp				Mytilus spp			Mytilus spp					Mytilus edulis			Mytilus spp										Mytilus spp		Mytilus spp				Mytilus edulis							Mytilus spp		Mytilus spp									Mytilus spp		Mytilus spp		Mytilus spp		Mytilus spp		Mytilus spp		Mytilus spp			Mytilus edulis				Mytilus spp				Mytilus spp			Mytilus edulis				Mytilus spp		Mytilus spp		Mytilus spp		Mytilus spp		Mytilus spp		Mytilus spp		Mytilus spp							Nucella lapillus
Element source	OSPAR																			OSPAR; EQS Directive (2013/39/EU)	OSPAR; EQS Directive (2013/39/EU)											EQS Directive (2013/39/EU)							OSPAR; EQS Directive (2013/39/EU)	OSPAR; EQS Directive (2013/39/EU)				OSPAR; EQS Directive (2013/39/EU)		OSPAR; EQS Directive (2013/39/EU)																																EQS Directive (2013/39/EU)			OSPAR; EQS Directive (2013/39/EU)	OSPAR; EQS Directive (2013/39/EU)		OSPAR; EQS Directive (2013/39/EU)	OSPAR															EQS Directive (2013/39/EU)	OSPAR	EQS Directive (2013/39/EU)	EQS Directive (2013/39/EU)	EQS Directive (2013/39/EU)
Criterion		D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C2	D8C3
Parameter		Concentration in water	Concentration in water	Concentration in water	Concentration in water	Concentration in water	Concentration in water	CONC-S-63	Concentration in water	CONC-B-Other	Concentration in water	CONC-S-63	CONC-S-63	CONC-B-Other	CONC-S-63	CONC-S-63	CONC-B-Other	Concentration in water	Concentration in water	CONC-S-63	Concentration in water	CONC-B-Other	Concentration in water	CONC-S-63	CONC-B-Other	Concentration in water	Concentration in water	Concentration in water	Concentration in water	Concentration in water	Concentration in water		CONC-S-63	Concentration in water	CONC-B-Other	CONC-S-63	CONC-B-Other	Concentration in water	CONC-S-63	Concentration in water	CONC-B-Other	CONC-S-63	Concentration in water	CONC-S-63	Concentration in water		CONC-S-63	CONC-B-Other	CONC-S-63	CONC-B-Other	Concentration in water	Concentration in water	Concentration in water	Concentration in water	Concentration in water	CONC-B-Other	CONC-S-63	CONC-S-63	CONC-B-Other	CONC-S-63	CONC-B-Other	CONC-S-63	CONC-B-Other	CONC-S-63	CONC-B-Other	CONC-S-63	CONC-B-Other	CONC-S-63	CONC-B-Other	CONC-S-63	Concentration in water	CONC-B-Other	Concentration in water	CONC-S-63	Concentration in water	CONC-B-Other	Concentration in water		Concentration in water	CONC-B-Other	CONC-S-63	Concentration in water	CONC-B-Other			CONC-S-63	CONC-B-Other	CONC-S-63	CONC-B-Other	CONC-S-63	CONC-B-Other	CONC-S-63	CONC-B-Other	CONC-S-63	CONC-B-Other	CONC-S-63	CONC-B-Other	CONC-S-63	CONC-B-Other			CONC-B-Other	CONC-S-63	Concentration in water	CONC-S-63	Imposex
Threshold value upper		0.4	0.4	10.0	0.4	2.0	0.012	85.0	0.1	290.0	2.0	1.0	14000.0	0.005526802	97.5	261.0	80.0	50.0	0.004	1.2	0.45	960.0	12.0	384.0	8.1	6e-05	1.3	20.0	7e-05	3.2e-05	0.2		600.0	0.12	110.0	0.16	0.63	1.0	47.0	14.0	1300.0	160.0	130.0	36.0	2.0		240.0	1700.0	665.0	100.0	0.54	4.0	0.034	10.0	10.0	63000.0	150.0	1.0	1.7	1100.0	6.8	1100.0	6.8	110.0	204.06	110.0	74.82	1.0	1.7	430.0	0.027	600.0	0.017	103.0	0.00017	2.5	0.017		0.00017	2.4	0.15	0.07	123.0			3.0	10.28	0.6	2.12	7.9	26.9	40.0	134.7	12.0	39.87	1.7	5.69	2.7	9.18			12.0	0.8	0.0015	103.0	2.0
Threshold value lower
Threshold value operator		<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=		<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=		<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=		<=	<=	<=	<=	<=			<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=			<=	<=	<=	<=	<=
Threshold qualitative
Threshold value source		EQS Directive (2013/39/EU)	EQS Directive (2013/39/EU)	EQS Directive (2013/39/EU)	EQS Directive (2013/39/EU)	EQS Directive (2013/39/EU)	EQS Directive (2013/39/EU)	OSPAR Convention	EQS Directive (2013/39/EU)	OSPAR Convention	EQS Directive (2013/39/EU)	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	EQS Directive (2013/39/EU)	EQS Directive (2013/39/EU)	OSPAR Convention	EQS Directive (2013/39/EU)	OSPAR Convention	EQS Directive (2013/39/EU)	OSPAR Convention	OSPAR Convention	EQS Directive (2013/39/EU)	EQS Directive (2013/39/EU)	EQS Directive (2013/39/EU)	EQS Directive (2013/39/EU)	EQS Directive (2013/39/EU)	EQS Directive (2013/39/EU)		OSPAR Convention	EQS Directive (2013/39/EU)	OSPAR Convention	OSPAR Convention	OSPAR Convention	EQS Directive (2013/39/EU)	OSPAR Convention	EQS Directive (2013/39/EU)	OSPAR Convention	OSPAR Convention	EQS Directive (2013/39/EU)	OSPAR Convention	EQS Directive (2013/39/EU)		OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	EQS Directive (2013/39/EU)	EQS Directive (2013/39/EU)	EQS Directive (2013/39/EU)	EQS Directive (2013/39/EU)	EQS Directive (2013/39/EU)	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	EQS Directive (2013/39/EU)	OSPAR Convention	EQS Directive (2013/39/EU)	OSPAR Convention	EQS Directive (2013/39/EU)	OSPAR Convention	EQS Directive (2013/39/EU)		EQS Directive (2013/39/EU)	OSPAR Convention	OSPAR Convention	EQS Directive (2013/39/EU)	OSPAR Convention			OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention			OSPAR Convention	OSPAR Convention	EQS Directive (2013/39/EU)	OSPAR Convention	OSPAR Convention
Value achieved upper		0.005	0.005	0.03	0.005	0.15	0.01	9.301075269	0.002	1.390315326	0.005	0.855614973	0.134408602	69.73491719	0.134408602	15.32258065	2.957227807	0.03	0.002	0.271463415	0.05	548.4454829	0.05	21.10215054	4.932449624	0.0005	0.02	0.03	0.0001	0.0001	0.01		30.77956989	0.002	7.277201327	0.055432373	0.257176837	0.01	41.59756098	0.2499	1078.416002	26.88172043	0.002	33.5915719	0.005		46.37096774	19.23802293	27.28494624	8.611319363	0.02	0.005	0.01	0.05	0.05	77199.95771	127.1585366	0.044345898	0.204825038	0.134408602	0.084747061	0.134408602	2.359818547	0.134408602	0.123644664	0.134408602	0.693471157	0.134408602	0.43132379	20.43010753	0.001	0.727067253	0.002	32.52688172	0.001	6.153988994	0.002		0.001	1.893100219	0.08947561	0.00151	60.21853762			0.044345898	0.58961779	0.044345898	0.613784986	0.044345898	1.200333294	0.055432373	2.098288916	0.044345898	0.403246812	0.044345898	0.123644664	0.044345898	0.282704034				2.771618625	9e-05	39.65053763	0.214375
Value achieved lower
Value unit		microgram per litre	microgram per litre	microgram per litre	microgram per litre	microgram per litre	microgram per litre	microgram per kilogram of dry weight	microgram per litre	microgram per kilogram of dry weight	microgram per litre	microgram per kilogram of dry weight	microgram per kilogram of dry weight	ug/kg lw	microgram per kilogram of dry weight	microgram per kilogram of dry weight	microgram per kilogram of dry weight	microgram per litre	microgram per litre	mg/kg dw	microgram per litre	microgram per kilogram of dry weight	microgram per litre	microgram per kilogram of dry weight	microgram per kilogram of dry weight	microgram per litre	microgram per litre	microgram per litre	microgram per litre	microgram per litre	microgram per litre		microgram per kilogram of dry weight	microgram per litre	microgram per kilogram of wet weight	microgram per kilogram of dry weight	microgram per kilogram of wet weight	microgram per litre	mg/kg dw	microgram per litre	microgram per kilogram of dry weight	microgram per kilogram of dry weight	microgram per litre	mg/kg dw	microgram per litre		microgram per kilogram of dry weight	microgram per kilogram of dry weight	microgram per kilogram of dry weight	microgram per kilogram of dry weight	microgram per litre	microgram per litre	microgram per litre	microgram per litre	microgram per litre	microgram per kilogram of dry weight	mg/kg dw	microgram per kilogram of dry weight	ug/kg lw	microgram per kilogram of dry weight	ug/kg lw	microgram per kilogram of dry weight	ug/kg lw	microgram per kilogram of dry weight	ug/kg lw	microgram per kilogram of dry weight	ug/kg lw	microgram per kilogram of dry weight	ug/kg lw	microgram per kilogram of dry weight	microgram per litre	microgram per kilogram of wet weight	microgram per litre	microgram per kilogram of dry weight	microgram per litre	microgram per litre	microgram per litre		microgram per litre	microgram per kilogram of dry weight	mg/kg dw	microgram per litre	microgram per kilogram of wet weight			microgram per kilogram of dry weight	ug/kg lw	microgram per kilogram of dry weight	ug/kg lw	microgram per kilogram of dry weight	ug/kg lw	microgram per kilogram of dry weight	ug/kg lw	microgram per kilogram of dry weight	ug/kg lw	microgram per kilogram of dry weight	ug/kg lw	microgram per kilogram of dry weight	ug/kg lw			microgram per kilogram of dry weight	microgram per kilogram of dry weight	microgram per litre	microgram per kilogram of dry weight	index VDSI
Proportion threshold value
Proportion value achieved
Proportion threshold value unit
Trend parameter		Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Stable	Not relevant	Not relevant	Not relevant	Stable	Not relevant	Not relevant	Stable	Not relevant	Not relevant	Not relevant	Not relevant	Stable	Not relevant	Not relevant	Stable	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant		Not relevant	Not relevant	Stable	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Stable	Not relevant	Not relevant	Not relevant	Not relevant		Not relevant	Stable	Not relevant	Stable	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Stable	Not relevant	Not relevant	Stable	Not relevant	Stable	Not relevant	Stable	Not relevant	Stable	Not relevant	Stable	Not relevant	Stable	Not relevant	Not relevant	Stable	Stable	Not relevant	Stable	Stable	Stable		Stable	Stable	Not relevant	Not relevant	Stable			Not relevant	Stable	Not relevant	Stable	Not relevant	Stable	Not relevant	Stable	Not relevant	Stable	Not relevant	Stable	Not relevant	Stable			Stable	Not relevant	Stable	Not relevant	Stable
Parameter achieved		Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	No	Not assessed	Not assessed	Not assessed	Yes	Not assessed	Not assessed	Yes	Not assessed	Not assessed	Not assessed	Not assessed	Yes	Not assessed	Not assessed	Yes	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed		Not assessed	Not assessed	Yes	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Yes	Not assessed	Not assessed	Not assessed	Not assessed		Not assessed	Yes	Not assessed	Yes	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Yes	Not assessed	Not assessed	Yes	Not assessed	Yes	Not assessed	Yes	Not assessed	Yes	Not assessed	Yes	Not assessed	Yes	Not assessed	Not assessed	Yes	Yes	Not assessed	Yes	Yes	Yes		Yes	Yes	Not assessed	Not assessed	No			Not assessed	Yes	Not assessed	No	Not assessed	Yes	Not assessed	Yes	Not assessed	Yes	Not assessed	No	Not assessed	Yes			Yes	Not assessed	Yes	Not assessed	Yes
Description parameter		Parameter status is Not assessed for 1,2,3-Trichlorobenzene in ACS-IE-MS-016as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is Not assessed for 1,2,4-Trichlorobenzene in ACS-IE-MS-016as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is Not assessed for 1,2-Dichloroethane in ACS-IE-MS-016as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is Not assessed for 1,3,5-Trichlorobenzene in ACS-IE-MS-016as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is Not assessed for 4-Nonylphenol in ACS-IE-MS-016as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is Not assessed for Aclonifen in ACS-IE-MS-016as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is Not assessed for Anthracene in ACS-IE-MS-016as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is Not assessed for Anthracene in ACS-IE-MS-016as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status was not achieved for Anthracene in ACS-IE-MS-016. The number of assessments meet the minimum of 4 sites/assessments but the element fails to meet threshold criteria of 90% compliance.	Parameter status is Not assessed for Atrazine in ACS-IE-MS-016as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is Not assessed for BDE 85 (2,2�,3,4,4�-pentabromodiphenyl ether) in ACS-IE-MS-016as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is Not assessed for BDE-183 (2,2',3,4,4',5',6-heptabromodiphenyl ether) in ACS-IE-MS-016as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is achieved for BDE-183 (2,2',3,4,4',5',6-heptabromodiphenyl ether) in ACS-IE-MS-016as assessments completed meet the minimum of 4 sites/assessments and also meet threshold criteria of 90% compliance.	Parameter status is Not assessed for BDE-66 (2,3',4,4'-tetrabromodiphenyl ether) in ACS-IE-MS-016as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is Not assessed for Benz(a)anthracene in ACS-IE-MS-016as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is achieved for Benz(a)anthracene in ACS-IE-MS-016as assessments completed meet the minimum of 4 sites/assessments and also meet threshold criteria of 90% compliance.	Parameter status is Not assessed for Benzene in ACS-IE-MS-016as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is Not assessed for Bifenox in ACS-IE-MS-016as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is Not assessed for Cadmium and its compounds in ACS-IE-MS-016as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is Not assessed for Cadmium and its compounds in ACS-IE-MS-016as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is achieved for Cadmium and its compounds in ACS-IE-MS-016as assessments completed meet the minimum of 4 sites/assessments and also meet threshold criteria of 90% compliance.	Parameter status is Not assessed for carbon tetrachloride in ACS-IE-MS-016as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is Not assessed for Chrysene in ACS-IE-MS-016as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is achieved for Chrysene in ACS-IE-MS-016as assessments completed meet the minimum of 4 sites/assessments and also meet threshold criteria of 90% compliance.	Parameter status is Not assessed for Cypermethrin in ACS-IE-MS-016as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is Not assessed for Di(2-ethylhexyl)phthalate (DEHP) in ACS-IE-MS-016as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is Not assessed for Dichloromethane in ACS-IE-MS-016as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is Not assessed for Dichlorvos in ACS-IE-MS-016as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is Not assessed for Dicofol in ACS-IE-MS-016as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is Not assessed for Diuron in ACS-IE-MS-016as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.		Parameter status is Not assessed for Fluoranthene in ACS-IE-MS-016as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is Not assessed for Fluoranthene in ACS-IE-MS-016as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is achieved for Fluoranthene in ACS-IE-MS-016as assessments completed meet the minimum of 4 sites/assessments and also meet threshold criteria of 90% compliance.	Parameter status is Not assessed for Hexachlorobenzene in ACS-IE-MS-016as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is Not assessed for Hexachlorobenzene in ACS-IE-MS-016as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is Not assessed for Isoproturon in ACS-IE-MS-016as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is Not assessed for Lead and its compounds in ACS-IE-MS-016as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is Not assessed for Lead and its compounds in ACS-IE-MS-016as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is achieved for Lead and its compounds in ACS-IE-MS-016as assessments completed meet the minimum of 4 sites/assessments and also meet threshold criteria of 90% compliance.	Parameter status is Not assessed for Naphthalene in ACS-IE-MS-016as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is Not assessed for Naphthalene in ACS-IE-MS-016as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is Not assessed for Nickel and its compounds in ACS-IE-MS-016as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is Not assessed for Nonylphenol in ACS-IE-MS-016as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.		Parameter status is Not assessed for Phenanthrene in ACS-IE-MS-016as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is achieved for Phenanthrene in ACS-IE-MS-016as assessments completed meet the minimum of 4 sites/assessments and also meet threshold criteria of 90% compliance.	Parameter status is Not assessed for Pyrene in ACS-IE-MS-016as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is achieved for Pyrene in ACS-IE-MS-016as assessments completed meet the minimum of 4 sites/assessments and also meet threshold criteria of 90% compliance.	Parameter status is Not assessed for Quinoxyfen in ACS-IE-MS-016as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is Not assessed for Simazine in ACS-IE-MS-016as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is Not assessed for Terbutryn in ACS-IE-MS-016as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is Not assessed for Tetrachloroethylene in ACS-IE-MS-016as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is Not assessed for Trichloroethylene in ACS-IE-MS-016as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is achieved for Zinc and its compounds in ACS-IE-MS-016as assessments completed meet the minimum of 4 sites/assessments and also meet threshold criteria of 90% compliance.	Parameter status is Not assessed for Zinc and its compounds in ACS-IE-MS-016as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is Not assessed for BDE 100 (2,2�,4,4�,6-pentabromodiphenyl ether) in ACS-IE-MS-016as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is achieved for BDE 100 (2,2�,4,4�,6-pentabromodiphenyl ether) in ACS-IE-MS-016as assessments completed meet the minimum of 4 sites/assessments and also meet threshold criteria of 90% compliance.	Parameter status is Not assessed for BDE 153 (2,2�,4,4�,5,5�-hexabromodiphenyl ether) in ACS-IE-MS-016as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is achieved for BDE 153 (2,2�,4,4�,5,5�-hexabromodiphenyl ether) in ACS-IE-MS-016as assessments completed meet the minimum of 4 sites/assessments and also meet threshold criteria of 90% compliance.	Parameter status is Not assessed for BDE 154 (2,2�,4,4�,5,6�-hexabromodiphenyl ether) in ACS-IE-MS-016as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is achieved for BDE 154 (2,2�,4,4�,5,6�-hexabromodiphenyl ether) in ACS-IE-MS-016as assessments completed meet the minimum of 4 sites/assessments and also meet threshold criteria of 90% compliance.	Parameter status is Not assessed for BDE 28 (2,4,4-tribromodiphenyl ether) in ACS-IE-MS-016as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is achieved for BDE 28 (2,4,4-tribromodiphenyl ether) in ACS-IE-MS-016as assessments completed meet the minimum of 4 sites/assessments and also meet threshold criteria of 90% compliance.	Parameter status is Not assessed for BDE 47 (2,2�,4,4�-tetrabromodiphenyl ether) in ACS-IE-MS-016as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is achieved for BDE 47 (2,2�,4,4�-tetrabromodiphenyl ether) in ACS-IE-MS-016as assessments completed meet the minimum of 4 sites/assessments and also meet threshold criteria of 90% compliance.	Parameter status is Not assessed for BDE 99 (2,2�,4,4�,5-pentabromodiphenyl ether) in ACS-IE-MS-016as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is achieved for BDE 99 (2,2�,4,4�,5-pentabromodiphenyl ether) in ACS-IE-MS-016as assessments completed meet the minimum of 4 sites/assessments and also meet threshold criteria of 90% compliance.	Parameter status is Not assessed for Benz(a)pyrene in ACS-IE-MS-016as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is Not assessed for Benz(a)pyrene in ACS-IE-MS-016as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is achieved for Benz(a)pyrene in ACS-IE-MS-016as assessments completed meet the minimum of 4 sites/assessments and also meet threshold criteria of 90% compliance.	Assessments completed in ACS-IE-MS-016 for Benzo(b)fluoranthene in this matrix meet the assemment threshold criteria of 90% compliance	Parameter status is Not assessed for Benzo(g,h,i)perylene in ACS-IE-MS-016as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Assessments completed in ACS-IE-MS-016 for Benzo(g,h,i)perylene in this matrix meet the assemment threshold criteria of 90% compliance	Parameter status is achieved for Benzo(g,h,i)perylene in ACS-IE-MS-016as assessments completed meet the minimum of 4 sites/assessments and also meet threshold criteria of 90% compliance.	Assessments completed in ACS-IE-MS-016 for Benzo(k)fluoranthene in this matrix meet the assemment threshold criteria of 90% compliance		Assessments completed in ACS-IE-MS-016 for indeno[1,2,3-cd]pyrene; in this matrix meet the assemment threshold criteria of 90% compliance	Parameter status is achieved for indeno[1,2,3-cd]pyrene; in ACS-IE-MS-016as assessments completed meet the minimum of 4 sites/assessments and also meet threshold criteria of 90% compliance.	Parameter status is Not assessed for Mercury in ACS-IE-MS-016as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is Not assessed for Mercury in ACS-IE-MS-016as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status was not achieved for Mercury in ACS-IE-MS-016. The number of assessments meet the minimum of 4 sites/assessments but the element fails to meet threshold criteria of 90% compliance.			Parameter status is Not assessed for PCB 101 (2,2�,4,5,5�-pentachlorobiphenyl) in ACS-IE-MS-016as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is achieved for PCB 101 (2,2�,4,5,5�-pentachlorobiphenyl) in ACS-IE-MS-016as assessments completed meet the minimum of 4 sites/assessments and also meet threshold criteria of 90% compliance.	Parameter status is Not assessed for PCB 118 (2,3�,4,4�,5-pentachlorobiphenyl) in ACS-IE-MS-016as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status was not achieved for PCB 118 (2,3�,4,4�,5-pentachlorobiphenyl) in ACS-IE-MS-016. The number of assessments meet the minimum of 4 sites/assessments but the element fails to meet threshold criteria of 90% compliance.	Parameter status is Not assessed for PCB 138 (2,2�,3,4,4�,5�-hexachlorobiphenyl) in ACS-IE-MS-016as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is achieved for PCB 138 (2,2�,3,4,4�,5�-hexachlorobiphenyl) in ACS-IE-MS-016as assessments completed meet the minimum of 4 sites/assessments and also meet threshold criteria of 90% compliance.	Parameter status is Not assessed for PCB 153 (2,2�,4,4�,5,5�-hexachlorobiphenyl) in ACS-IE-MS-016as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is achieved for PCB 153 (2,2�,4,4�,5,5�-hexachlorobiphenyl) in ACS-IE-MS-016as assessments completed meet the minimum of 4 sites/assessments and also meet threshold criteria of 90% compliance.	Parameter status is Not assessed for PCB 180 (2,2�,3,4,4�,5,5�-heptachlorobiphenyl) in ACS-IE-MS-016as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is achieved for PCB 180 (2,2�,3,4,4�,5,5�-heptachlorobiphenyl) in ACS-IE-MS-016as assessments completed meet the minimum of 4 sites/assessments and also meet threshold criteria of 90% compliance.	Parameter status is Not assessed for PCB 28 (2,4,4�-trichlorobiphenyl) in ACS-IE-MS-016as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status was not achieved for PCB 28 (2,4,4�-trichlorobiphenyl) in ACS-IE-MS-016. The number of assessments meet the minimum of 4 sites/assessments but the element fails to meet threshold criteria of 90% compliance.	Parameter status is Not assessed for PCB 52 (2,2�,5,5�-tetrachlorobiphenyl) in ACS-IE-MS-016as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is achieved for PCB 52 (2,2�,5,5�-tetrachlorobiphenyl) in ACS-IE-MS-016as assessments completed meet the minimum of 4 sites/assessments and also meet threshold criteria of 90% compliance.			Assessments completed in ACS-IE-MS-016 for TBT in this matrix meet the assemment threshold criteria of 90% compliance	Parameter status is Not assessed for TBT in ACS-IE-MS-016as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Assessments completed in ACS-IE-MS-016 for TBT in this matrix meet the assemment threshold criteria of 90% compliance	Parameter status is Not assessed for indeno[1,2,3-cd]pyrene; in ACS-IE-MS-016as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is achieved for Imposex in ACS-IE-MS-016as assessments completed meet the minimum of 4 sites/assessments and also meet threshold criteria of 90% compliance.
Related indicator
Criteria status																				Good	Good											Unknown							Good	Good				Unknown		Good																																Unknown			Not good	Not good		Good	Good															Unknown	Good	Unknown	Unknown	Unknown		Good	Good, based on low risk
Description criteria																				The status of Cadmium and its compounds is Good in the Celtic Sea based on 100% of assessments meeting the 90% criteria. Trend status is Stable.	The status of Cadmium and its compounds is Good in the Celtic Sea based on 100% of assessments meeting the 90% criteria. Trend status is Stable.											The status of WFD PS is Unknown in the Celtic Sea.Trend status is Unknown.							The status of Lead and its compounds is Good in the Celtic Sea based on 100% of assessments meeting the 90% criteria. Trend status is Stable.	The status of Lead and its compounds is Good in the Celtic Sea based on 100% of assessments meeting the 90% criteria. Trend status is Stable.				The status of Nickel and its compounds is Unknown in the Celtic Sea.Trend status is Unknown.		The status of PAHs is Good in the Celtic Sea based on 95.8% of assessments meeting the 90% criteria. Trend status is Not assessed.																																The status of HBCDD is Unknown in the Celtic Sea based on Unknown% of assessments meeting the 90% criteria. Trend status is Unknown.			The status of Mercury and its compounds is Not good in the Celtic Sea based on 77.8% of assessments meeting the 90% criteria. Trend status is Not assessed.	The status of Mercury and its compounds is Not good in the Celtic Sea based on 77.8% of assessments meeting the 90% criteria. Trend status is Not assessed.		The status of PAHs is Good in the Celtic Sea based on 100% of assessments meeting the 90% criteria. Trend status is Not assessed.	The status of PBDEs is Good in the Celtic Sea based on 100% of assessments meeting the 90% criteria. Trend status is Not assessed.															The status of PFOS is Unknown in the Celtic Sea based on Unknown% of assessments meeting the 90% criteria. Trend status is Unknown.	The status of PCBs is Good in the Celtic Sea based on 95.2% of assessments meeting the 90% criteria. Trend status is Not assessed.	The status of TBT is Unknown in the Celtic Sea based on Unknown% of assessments meeting the 90% criteria. Trend status is Unknown.	The status of TBT is Unknown in the Celtic Sea based on Unknown% of assessments meeting the 90% criteria. Trend status is Unknown.	The status of TBT is Unknown in the Celtic Sea based on Unknown% of assessments meeting the 90% criteria. Trend status is Unknown.		The status of Imposex is Good in the Celtic Sea based on 100% of assessments meeting the 90% criteria. Trend status is Improving.
Element status	Not relevant																			Not relevant	Not relevant											Not relevant							Not relevant	Not relevant				Not relevant		Not relevant																																Not relevant			Not relevant	Not relevant		Not relevant	Not relevant															Not relevant	Not relevant	Not relevant	Not relevant	Not relevant
Description element	A total of 100% of assessments for Imposex in the Celtic Sea was obtained relative to a 90% threshold.The trend is Improving																			The number of assessments of Cadmium and its compounds in the Celtic Sea is insufficient to complete assessment relative to a 90% threshold.	The number of assessments of Cadmium and its compounds in the Celtic Sea is insufficient to complete assessment relative to a 90% threshold.											The number of assessments of Environmental UPBT contaminants - WFD UPBT substances in the Celtic Sea is insufficient to complete assessment relative to a 90% threshold.							The number of assessments of Lead and its compounds in the Celtic Sea is insufficient to complete assessment relative to a 90% threshold.	The number of assessments of Lead and its compounds in the Celtic Sea is insufficient to complete assessment relative to a 90% threshold.				The number of assessments of Nickel and its compounds in the Celtic Sea is insufficient to complete assessment relative to a 90% threshold.		A total of 95.8% of assessments for PAH in the Celtic Sea was obtained relative to a 90% threshold.The trend is Improving																																The number of assessments of HBCDD in the Celtic Sea is insufficient to complete assessment relative to a 90% threshold.			77.8% of assessments of Mercury and its compounds in the Celtic Sea met with the 90% threshold value. Trends were Not assessed	77.8% of assessments of Mercury and its compounds in the Celtic Sea met with the 90% threshold value. Trends were Not assessed		100% of assessments of PAH in the Celtic Sea met with the 90% threshold value. Trends were Stable	100% of assessments of PBDE in the Celtic Sea met with the 90% threshold value. Trends were Not assessed															The number of assessments of PFOS in the Celtic Sea is insufficient to complete assessment relative to a 90% threshold.	A total of 95.2% of assessments for Polychlorinated biphenyls (7 PCB: 28,52,101,118,138,153,180) in the Celtic Sea was obtained relative to a 90% threshold.The trend is Improving	The number of assessments of TBT in the Celtic Sea is insufficient to complete assessment relative to a 90% threshold.	The number of assessments of TBT in the Celtic Sea is insufficient to complete assessment relative to a 90% threshold.	The number of assessments of TBT in the Celtic Sea is insufficient to complete assessment relative to a 90% threshold.
Source assessment feature	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD
Reporting method feature	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C
Trend feature	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed
Integration rule type parameter	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE
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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.
Integration rule type criteria
Integration rule description criteria
GES extent threshold
GES extent achieved	77.80	95.80	95.80	95.80	95.80	95.80	95.80	95.80	95.80	95.80	95.80	95.80	95.80	95.80	95.80	95.80	95.80	95.80	95.80	95.80	95.80	95.80	95.80	95.80	95.80	95.80	95.80	95.80	95.80	95.80	95.80	95.80	95.80	95.80	95.80	95.80	95.80	95.80	95.80	95.80	95.80	95.80	95.80	95.80	95.80	95.80	95.80	95.80	95.80	95.80	95.80	95.80	95.80	95.80	95.80	95.80	95.80	77.80	77.80	77.80	77.80	77.80	77.80	77.80	77.80	77.80	77.80	77.80	77.80	77.80	77.80	77.80	77.80	77.80	77.80	77.80	77.80	77.80	77.80	77.80	77.80	77.80	77.80	77.80	77.80	77.80	77.80	77.80	77.80	77.80	77.80	77.80	77.80	77.80	77.80	77.80	77.80	77.80	77.80	77.80	77.80	77.80	77.80	77.80	77.80
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	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	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed
Description overall status	UPBT concentrations in water, sediments and biota in the Celtic seas are mostly in GES. Legacy issues persist for Mercury in this area where discreet failures for shellfish were present.	Non-UPBT concentrations in water and sediments in the Celtic seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Celtic seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Celtic seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Celtic seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Celtic seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Celtic seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Celtic seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Celtic seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Celtic seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Celtic seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Celtic seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Celtic seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Celtic seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Celtic seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Celtic seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Celtic seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Celtic seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Celtic seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Celtic seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Celtic seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Celtic seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Celtic seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Celtic seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Celtic seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Celtic seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Celtic seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Celtic seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Celtic seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Celtic seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Celtic seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Celtic seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Celtic seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Celtic seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Celtic seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Celtic seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Celtic seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Celtic seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Celtic seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Celtic seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Celtic seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Celtic seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Celtic seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Celtic seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Celtic seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Celtic seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Celtic seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Celtic seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Celtic seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Celtic seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Celtic seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Celtic seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Celtic seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Celtic seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Celtic seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Celtic seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Celtic seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	UPBT concentrations in water, sediments and biota in the Celtic seas are mostly in GES. Legacy issues persist for Mercury in this area where discreet failures for shellfish were present.	UPBT concentrations in water, sediments and biota in the Celtic seas are mostly in GES. Legacy issues persist for Mercury in this area where discreet failures for shellfish were present.	UPBT concentrations in water, sediments and biota in the Celtic seas are mostly in GES. Legacy issues persist for Mercury in this area where discreet failures for shellfish were present.	UPBT concentrations in water, sediments and biota in the Celtic seas are mostly in GES. Legacy issues persist for Mercury in this area where discreet failures for shellfish were present.	UPBT concentrations in water, sediments and biota in the Celtic seas are mostly in GES. Legacy issues persist for Mercury in this area where discreet failures for shellfish were present.	UPBT concentrations in water, sediments and biota in the Celtic seas are mostly in GES. Legacy issues persist for Mercury in this area where discreet failures for shellfish were present.	UPBT concentrations in water, sediments and biota in the Celtic seas are mostly in GES. Legacy issues persist for Mercury in this area where discreet failures for shellfish were present.	UPBT concentrations in water, sediments and biota in the Celtic seas are mostly in GES. Legacy issues persist for Mercury in this area where discreet failures for shellfish were present.	UPBT concentrations in water, sediments and biota in the Celtic seas are mostly in GES. Legacy issues persist for Mercury in this area where discreet failures for shellfish were present.	UPBT concentrations in water, sediments and biota in the Celtic seas are mostly in GES. Legacy issues persist for Mercury in this area where discreet failures for shellfish were present.	UPBT concentrations in water, sediments and biota in the Celtic seas are mostly in GES. Legacy issues persist for Mercury in this area where discreet failures for shellfish were present.	UPBT concentrations in water, sediments and biota in the Celtic seas are mostly in GES. Legacy issues persist for Mercury in this area where discreet failures for shellfish were present.	UPBT concentrations in water, sediments and biota in the Celtic seas are mostly in GES. Legacy issues persist for Mercury in this area where discreet failures for shellfish were present.	UPBT concentrations in water, sediments and biota in the Celtic seas are mostly in GES. Legacy issues persist for Mercury in this area where discreet failures for shellfish were present.	UPBT concentrations in water, sediments and biota in the Celtic seas are mostly in GES. Legacy issues persist for Mercury in this area where discreet failures for shellfish were present.	UPBT concentrations in water, sediments and biota in the Celtic seas are mostly in GES. Legacy issues persist for Mercury in this area where discreet failures for shellfish were present.	UPBT concentrations in water, sediments and biota in the Celtic seas are mostly in GES. Legacy issues persist for Mercury in this area where discreet failures for shellfish were present.	UPBT concentrations in water, sediments and biota in the Celtic seas are mostly in GES. Legacy issues persist for Mercury in this area where discreet failures for shellfish were present.	UPBT concentrations in water, sediments and biota in the Celtic seas are mostly in GES. Legacy issues persist for Mercury in this area where discreet failures for shellfish were present.	UPBT concentrations in water, sediments and biota in the Celtic seas are mostly in GES. Legacy issues persist for Mercury in this area where discreet failures for shellfish were present.	UPBT concentrations in water, sediments and biota in the Celtic seas are mostly in GES. Legacy issues persist for Mercury in this area where discreet failures for shellfish were present.	UPBT concentrations in water, sediments and biota in the Celtic seas are mostly in GES. Legacy issues persist for Mercury in this area where discreet failures for shellfish were present.	UPBT concentrations in water, sediments and biota in the Celtic seas are mostly in GES. Legacy issues persist for Mercury in this area where discreet failures for shellfish were present.	UPBT concentrations in water, sediments and biota in the Celtic seas are mostly in GES. Legacy issues persist for Mercury in this area where discreet failures for shellfish were present.	UPBT concentrations in water, sediments and biota in the Celtic seas are mostly in GES. Legacy issues persist for Mercury in this area where discreet failures for shellfish were present.	UPBT concentrations in water, sediments and biota in the Celtic seas are mostly in GES. Legacy issues persist for Mercury in this area where discreet failures for shellfish were present.	UPBT concentrations in water, sediments and biota in the Celtic seas are mostly in GES. Legacy issues persist for Mercury in this area where discreet failures for shellfish were present.	UPBT concentrations in water, sediments and biota in the Celtic seas are mostly in GES. Legacy issues persist for Mercury in this area where discreet failures for shellfish were present.	UPBT concentrations in water, sediments and biota in the Celtic seas are mostly in GES. Legacy issues persist for Mercury in this area where discreet failures for shellfish were present.	UPBT concentrations in water, sediments and biota in the Celtic seas are mostly in GES. Legacy issues persist for Mercury in this area where discreet failures for shellfish were present.	UPBT concentrations in water, sediments and biota in the Celtic seas are mostly in GES. Legacy issues persist for Mercury in this area where discreet failures for shellfish were present.	UPBT concentrations in water, sediments and biota in the Celtic seas are mostly in GES. Legacy issues persist for Mercury in this area where discreet failures for shellfish were present.	UPBT concentrations in water, sediments and biota in the Celtic seas are mostly in GES. Legacy issues persist for Mercury in this area where discreet failures for shellfish were present.	UPBT concentrations in water, sediments and biota in the Celtic seas are mostly in GES. Legacy issues persist for Mercury in this area where discreet failures for shellfish were present.	UPBT concentrations in water, sediments and biota in the Celtic seas are mostly in GES. Legacy issues persist for Mercury in this area where discreet failures for shellfish were present.	UPBT concentrations in water, sediments and biota in the Celtic seas are mostly in GES. Legacy issues persist for Mercury in this area where discreet failures for shellfish were present.	UPBT concentrations in water, sediments and biota in the Celtic seas are mostly in GES. Legacy issues persist for Mercury in this area where discreet failures for shellfish were present.	UPBT concentrations in water, sediments and biota in the Celtic seas are mostly in GES. Legacy issues persist for Mercury in this area where discreet failures for shellfish were present.	UPBT concentrations in water, sediments and biota in the Celtic seas are mostly in GES. Legacy issues persist for Mercury in this area where discreet failures for shellfish were present.	UPBT concentrations in water, sediments and biota in the Celtic seas are mostly in GES. Legacy issues persist for Mercury in this area where discreet failures for shellfish were present.	UPBT concentrations in water, sediments and biota in the Celtic seas are mostly in GES. Legacy issues persist for Mercury in this area where discreet failures for shellfish were present.	UPBT concentrations in water, sediments and biota in the Celtic seas are mostly in GES. Legacy issues persist for Mercury in this area where discreet failures for shellfish were present.	UPBT concentrations in water, sediments and biota in the Celtic seas are mostly in GES. Legacy issues persist for Mercury in this area where discreet failures for shellfish were present.	UPBT concentrations in water, sediments and biota in the Celtic seas are mostly in GES. Legacy issues persist for Mercury in this area where discreet failures for shellfish were present.	UPBT concentrations in water, sediments and biota in the Celtic seas are mostly in GES. Legacy issues persist for Mercury in this area where discreet failures for shellfish were present.	UPBT concentrations in water, sediments and biota in the Celtic seas are mostly in GES. Legacy issues persist for Mercury in this area where discreet failures for shellfish were present.	UPBT concentrations in water, sediments and biota in the Celtic seas are mostly in GES. Legacy issues persist for Mercury in this area where discreet failures for shellfish were present.	UPBT concentrations in water, sediments and biota in the Celtic seas are mostly in GES. Legacy issues persist for Mercury in this area where discreet failures for shellfish were present.
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	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	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-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016	IE-D8T1a-1-MRU016 IE-D8T1a-MRU016 IE-D8T1b-1-MRU016 IE-D8T1b-MRU016 IE-D8T2-MRU016
Test TV	NA	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	No	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	No	Yes	Yes	No	No	Yes	NA	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	NA	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	No	No	Yes	NA	No	Yes	Yes	Yes	Yes	NA	NA	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	NA	NA	NA	No	Yes	Yes	Yes	NA
Test results	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	Correct	False	False	False	False	Correct	False	False	Correct	False	False	False	False	False	False	False	False	False	Correct	False	False	False	False	False	Correct	False	False	False	False	False	False	Correct	False	Correct	False	False	False	False	False	False	False	False	Correct	False	Correct	False	Correct	False	Correct	False	Correct	False	Correct	False	False	Correct	Correct	False	False	False	Correct	False	False	Correct	False	False	False	False	False	False	Correct	False	False	False	Correct	False	Correct	False	Correct	False	False	False	Correct	False	False	False	False	Correct	False	Correct	False

ACS-IE-MS-017

Simplified table

Regional assessment area	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea	OSPAR-Irish Sea
Component MRUs
GES component	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8
Feature	Contaminants - UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Species	Acute pollution events
Element	Imposex	1,2,3-Trichlorobenzene	1,2,4-Trichlorobenzene	1,2-Dichloroethane	1,3,5-Trichlorobenzene	4-Nonylphenol	Aclonifen	Anthracene	Anthracene	Anthracene	Atrazine	BDE 85 (2,2’,3,4,4’-pentabromodiphenyl ether)	BDE-183 (2,2',3,4,4',5',6-heptabromodiphenyl ether)	BDE-66 (2,3',4,4'-tetrabromodiphenyl ether)	Benz(a)anthracene	Benz(a)anthracene	Benzene	Bifenox	Cadmium and its compounds	Cadmium and its compounds	Cadmium and its compounds	Carbon tetrachloride	Chrysene	Chrysene	Cypermethrin	Di(2-ethylhexyl)phthalate (DEHP)	Dichloromethane	Dichlorvos	Dicofol	Diuron	Environmental UPBT contaminants - WFD UPBT substances	Fluoranthene	Fluoranthene	Fluoranthene	Hexachlorobenzene	Hexachlorobenzene	Isoproturon	Lead and its compounds	Lead and its compounds	Lead and its compounds	Naphthalene	Naphthalene	Nickel and its compounds	Nickel and its compounds	Nonylphenol	PAH	Phenanthrene	Phenanthrene	Pyrene	Pyrene	Quinoxyfen	Simazine	Terbutryn	Tetrachloroethylene	Trichloroethylene	Zinc and its compounds	Zinc and its compounds	BDE 100 (2,2’,4,4’,6-pentabromodiphenyl ether)	BDE 100 (2,2’,4,4’,6-pentabromodiphenyl ether)	BDE 153 (2,2’,4,4’,5,5’-hexabromodiphenyl ether)	BDE 153 (2,2’,4,4’,5,5’-hexabromodiphenyl ether)	BDE 154 (2,2’,4,4’,5,6’-hexabromodiphenyl ether)	BDE 154 (2,2’,4,4’,5,6’-hexabromodiphenyl ether)	BDE 28 (2,4,4-tribromodiphenyl ether)	BDE 28 (2,4,4-tribromodiphenyl ether)	BDE 47 (2,2’,4,4’-tetrabromodiphenyl ether)	BDE 47 (2,2’,4,4’-tetrabromodiphenyl ether)	BDE 99 (2,2’,4,4’,5-pentabromodiphenyl ether)	BDE 99 (2,2’,4,4’,5-pentabromodiphenyl ether)	Benzo(a)pyrene	Benzo(a)pyrene	Benzo(a)pyrene	Benzo(b)fluoranthene	Benzo(g,h,i)perylene	Benzo(g,h,i)perylene	Benzo(g,h,i)perylene	Benzo(k)fluoranthene	Hexabromocyclododecanes (HBCDD)	Indeno(1,2,3,-cd)pyrene	Indeno(1,2,3,-cd)pyrene	Indeno(1,2,3,-cd)pyrene	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	PAH	PBDE	PCB 101 (2,2’,4,5,5’-pentachlorobiphenyl)	PCB 101 (2,2’,4,5,5’-pentachlorobiphenyl)	PCB 118 (2,3’,4,4’,5-pentachlorobiphenyl)	PCB 118 (2,3’,4,4’,5-pentachlorobiphenyl)	PCB 138 (2,2’,3,4,4’,5’-hexachlorobiphenyl)	PCB 138 (2,2’,3,4,4’,5’-hexachlorobiphenyl)	PCB 153 (2,2’,4,4’,5,5’-hexachlorobiphenyl)	PCB 153 (2,2’,4,4’,5,5’-hexachlorobiphenyl)	PCB 180 (2,2’,3,4,4’,5,5’-heptachlorobiphenyl)	PCB 180 (2,2’,3,4,4’,5,5’-heptachlorobiphenyl)	PCB 28 (2,4,4’-trichlorobiphenyl)	PCB 28 (2,4,4’-trichlorobiphenyl)	PCB 52 (2,2’,5,5’-tetrachlorobiphenyl)	PCB 52 (2,2’,5,5’-tetrachlorobiphenyl)	PFOS	Polychlorinated biphenyls (7 PCB: 28,52,101,118,138,153,180)	TBT	TBT	Imposex
Element extent
Trend element	Improving																		Improving	Improving											Not assessed							Not assessed	Not assessed				Not assessed	Not assessed		Not assessed																																Not assessed				Not assessed	Not assessed		Not assessed	Not assessed															Not assessed	Not assessed	Not assessed	Not assessed
Element 2	Nucella lapillus									Mytilus spp						Mytilus spp					Mytilus edulis			Mytilus spp										Mytilus spp		Mytilus spp				Mytilus edulis								Mytilus spp		Mytilus spp									Mytilus spp		Mytilus spp		Mytilus spp		Mytilus spp		Mytilus spp		Mytilus spp			Mytilus edulis				Mytilus spp					Mytilus spp			Mytilus edulis				Mytilus spp		Mytilus spp		Mytilus spp		Mytilus spp		Mytilus spp		Mytilus spp		Mytilus spp					Nucella lapillus
Element source	OSPAR																		OSPAR; EQS Directive (2013/39/EU)	OSPAR; EQS Directive (2013/39/EU)											EQS Directive (2013/39/EU)							OSPAR; EQS Directive (2013/39/EU)	OSPAR; EQS Directive (2013/39/EU)				OSPAR; EQS Directive (2013/39/EU)	OSPAR; EQS Directive (2013/39/EU)		OSPAR; EQS Directive (2013/39/EU)																																EQS Directive (2013/39/EU)				OSPAR; EQS Directive (2013/39/EU)	OSPAR; EQS Directive (2013/39/EU)		OSPAR; EQS Directive (2013/39/EU)	OSPAR															EQS Directive (2013/39/EU)	OSPAR	EQS Directive (2013/39/EU)	EQS Directive (2013/39/EU)
Criterion		D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C2	D8C3
Parameter		Concentration in water	Concentration in water	Concentration in water	Concentration in water	Concentration in water	Concentration in water	CONC-S-63	Concentration in water	CONC-B-Other	Concentration in water	CONC-S-63	CONC-S-63	CONC-S-63	CONC-S-63	CONC-B-Other	Concentration in water	Concentration in water	CONC-S-63	Concentration in water	CONC-B-Other	Concentration in water	CONC-S-63	CONC-B-Other	Concentration in water	Concentration in water	Concentration in water	Concentration in water	Concentration in water	Concentration in water		CONC-S-63	Concentration in water	CONC-B-Other	CONC-S-63	CONC-B-Other	Concentration in water	CONC-S-63	Concentration in water	CONC-B-Other	CONC-S-63	Concentration in water	CONC-S-63	Concentration in water	Concentration in water		CONC-S-63	CONC-B-Other	CONC-S-63	CONC-B-Other	Concentration in water	Concentration in water	Concentration in water	Concentration in water	Concentration in water	CONC-B-Other	CONC-S-63	CONC-S-63	CONC-B-Other	CONC-S-63	CONC-B-Other	CONC-S-63	CONC-B-Other	CONC-S-63	CONC-B-Other	CONC-S-63	CONC-B-Other	CONC-S-63	CONC-B-Other	CONC-S-63	Concentration in water	CONC-B-Other	Concentration in water	CONC-S-63	Concentration in water	CONC-B-Other	Concentration in water	Concentration in water	CONC-S-63	Concentration in water	CONC-B-Other	CONC-S-63	Concentration in water	CONC-B-Other			CONC-S-63	CONC-B-Other	CONC-S-63	CONC-B-Other	CONC-S-63	CONC-B-Other	CONC-S-63	CONC-B-Other	CONC-S-63	CONC-B-Other	CONC-S-63	CONC-B-Other	CONC-S-63	CONC-B-Other	Concentration in water		CONC-S-63	Concentration in water	Imposex
Threshold value upper		0.4	0.4	10.0	0.4	2.0	0.12	85.0	0.1	290.0	2.0	1.0	14000.0	97.5	261.0	80.0	50.0	0.004	1.2	0.45	960.0	12.0	384.0	8.1	6e-05	1.3	20.0	7e-05	3.2e-05	0.2		600.0	0.12	110.0	0.16	0.63	1.0	47.0	14.0	1300.0	160.0	130.0	36.0	34.0	2.0		240.0	1700.0	665.0	100.0	0.54	4.0	0.034	10.0	10.0	63000.0	150.0	1.0	1.7	1100.0	6.8	1100.0	6.8	110.0	204.06	110.0	74.82	1.0	1.7	430.0	0.027	600.0	0.017	103.0	0.00017	2.5	0.017	0.05	103.0	0.00017	2.4	0.15	0.07	123.0			3.0	10.28	0.6	2.12	7.9	26.9	40.0	134.7	12.0	39.87	1.7	5.69	2.7	9.18	7.2		0.8	0.0015	2.0
Threshold value lower
Threshold value operator		<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=		<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=		<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=			<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=		<=	<=	<=
Threshold qualitative
Threshold value source		EQS Directive (2013/39/EU)	EQS Directive (2013/39/EU)	EQS Directive (2013/39/EU)	EQS Directive (2013/39/EU)	EQS Directive (2013/39/EU)	EQS Directive (2013/39/EU)	OSPAR Convention	EQS Directive (2013/39/EU)	OSPAR Convention	EQS Directive (2013/39/EU)	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	EQS Directive (2013/39/EU)	EQS Directive (2013/39/EU)	OSPAR Convention	EQS Directive (2013/39/EU)	OSPAR Convention	EQS Directive (2013/39/EU)	OSPAR Convention	OSPAR Convention	EQS Directive (2013/39/EU)	EQS Directive (2013/39/EU)	EQS Directive (2013/39/EU)	EQS Directive (2013/39/EU)	EQS Directive (2013/39/EU)	EQS Directive (2013/39/EU)		OSPAR Convention	EQS Directive (2013/39/EU)	OSPAR Convention	OSPAR Convention	OSPAR Convention	EQS Directive (2013/39/EU)	OSPAR Convention	EQS Directive (2013/39/EU)	OSPAR Convention	OSPAR Convention	EQS Directive (2013/39/EU)	OSPAR Convention	EQS Directive (2013/39/EU)	EQS Directive (2013/39/EU)		OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	EQS Directive (2013/39/EU)	EQS Directive (2013/39/EU)	EQS Directive (2013/39/EU)	EQS Directive (2013/39/EU)	EQS Directive (2013/39/EU)	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	EQS Directive (2013/39/EU)	OSPAR Convention	EQS Directive (2013/39/EU)	OSPAR Convention	EQS Directive (2013/39/EU)	OSPAR Convention	EQS Directive (2013/39/EU)	EQS Directive (2013/39/EU)	OSPAR Convention	EQS Directive (2013/39/EU)	OSPAR Convention	OSPAR Convention	EQS Directive (2013/39/EU)	OSPAR Convention			OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	EQS Directive (2013/39/EU)		OSPAR Convention	EQS Directive (2013/39/EU)	OSPAR Convention
Value achieved upper		0.005	0.005	0.03	0.005	0.17	0.01	8.272727273	0.002	11.421654	0.005	0.151515152	0.151515152		14.78787879	37.58421167	0.03	0.002	0.335853659	0.05	545.2734128	0.05	19.6969697	20.25841182	0.0005	0.02	0.03	0.0001	0.0001	0.01		26.96969697	0.002	57.72206904	0.151515152	0.33012309	0.01	36.36585366	0.18495	2408.636845	22.57575758	0.002	30.42682927	0.305	0.005		39.09090909	51.05350746	21.21212121	46.91099598	0.02	0.005	0.01	0.05	0.05	79981.22846	115.7560976	0.151515152	0.545202859	0.151515152	0.306139214	0.151515152	0.174116281	0.151515152	0.219056956	0.151515152	1.208872307	0.151515152	0.6407956	15.75757576	0.001	9.294143428	0.002	23.48484848	0.001	29.84268169	0.002	0.0001	27.12121212	0.001	14.4444627	0.151515152	0.001273371	101.3013159			0.121212121	2.523463988	0.121212121	2.509686167	0.159090909	4.202448683	0.204545455	6.988757273	0.121212121	0.782062592	0.148484848	0.219056956	0.121212121	0.776848498	0.000235		2.666666667	0.000105	0.207894737
Value achieved lower
Value unit		microgram per litre	microgram per litre	microgram per litre	microgram per litre	microgram per litre	microgram per litre	microgram per kilogram of dry weight	microgram per litre	microgram per kilogram of dry weight	microgram per litre	microgram per kilogram of dry weight	microgram per kilogram of dry weight	microgram per kilogram of dry weight	microgram per kilogram of dry weight	microgram per kilogram of dry weight	microgram per litre	microgram per litre	mg/kg dw	microgram per litre	microgram per kilogram of dry weight	microgram per litre	microgram per kilogram of dry weight	microgram per kilogram of dry weight	microgram per litre	microgram per litre	microgram per litre	microgram per litre	microgram per litre	microgram per litre		microgram per kilogram of dry weight	microgram per litre	microgram per kilogram of wet weight	microgram per kilogram of dry weight	microgram per kilogram of wet weight	microgram per litre	mg/kg dw	microgram per litre	microgram per kilogram of dry weight	microgram per kilogram of dry weight	microgram per litre	mg/kg dw	microgram per litre	microgram per litre		microgram per kilogram of dry weight	microgram per kilogram of dry weight	microgram per kilogram of dry weight	microgram per kilogram of dry weight	microgram per litre	microgram per litre	microgram per litre	microgram per litre	microgram per litre	microgram per kilogram of dry weight	mg/kg dw	microgram per kilogram of dry weight	ug/kg lw	microgram per kilogram of dry weight	ug/kg lw	microgram per kilogram of dry weight	ug/kg lw	microgram per kilogram of dry weight	ug/kg lw	microgram per kilogram of dry weight	ug/kg lw	microgram per kilogram of dry weight	ug/kg lw	microgram per kilogram of dry weight	microgram per litre	microgram per kilogram of wet weight	microgram per litre	microgram per kilogram of dry weight	microgram per litre	microgram per litre	microgram per litre	microgram per litre	microgram per kilogram of dry weight	microgram per litre	microgram per kilogram of dry weight	mg/kg dw	microgram per litre	microgram per kilogram of wet weight			microgram per kilogram of dry weight	ug/kg lw	microgram per kilogram of dry weight	ug/kg lw	microgram per kilogram of dry weight	ug/kg lw	microgram per kilogram of dry weight	ug/kg lw	microgram per kilogram of dry weight	ug/kg lw	microgram per kilogram of dry weight	ug/kg lw	microgram per kilogram of dry weight	ug/kg lw	microgram per litre		microgram per kilogram of dry weight	microgram per litre	index VDSI
Proportion threshold value
Proportion value achieved
Proportion threshold value unit
Trend parameter		Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Stable	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Stable	Not relevant	Not relevant	Not relevant	Not relevant	Stable	Not relevant	Not relevant	Stable	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant		Not relevant	Stable	Stable	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Stable	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant		Not relevant	Stable	Not relevant	Stable	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Stable	Not relevant	Not relevant	Stable	Not relevant	Stable	Not relevant	Stable	Not relevant	Stable	Not relevant	Stable	Not relevant	Stable	Not relevant	Not relevant	Stable	Not relevant	Not relevant	Stable	Stable	Stable	Not relevant	Not relevant	Stable	Stable	Not relevant	Not relevant	Stable			Not relevant	Stable	Stable	Stable	Not relevant	Stable	Not relevant	Stable	Not relevant	Stable	Not relevant	Stable	Not relevant	Stable	Not relevant		Not relevant	Not relevant	Stable
Parameter achieved		Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Yes	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Yes	Not assessed	Not assessed	Not assessed	Not assessed	Yes	Not assessed	Not assessed	Yes	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed		Not assessed	Yes	Yes	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Yes	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed		Not assessed	Yes	Not assessed	Yes	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Yes	Not assessed	Not assessed	No	Not assessed	Yes	Not assessed	Yes	Not assessed	No	Not assessed	Yes	Not assessed	Yes	Not assessed	Not assessed	Yes	Not assessed	Not assessed	Yes	Yes	Yes	Not assessed	Not assessed	Yes	Yes	Not assessed	Not assessed	No			Not assessed	Yes	Yes	No	Not assessed	Yes	Not assessed	Yes	Not assessed	Yes	Not assessed	Yes	Not assessed	No	Not assessed		Not assessed	Not assessed	Yes
Description parameter		Parameter status is Not assessed for 1,2,3-Trichlorobenzene in ACS-IE-MS-017as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is Not assessed for 1,2,4-Trichlorobenzene in ACS-IE-MS-017as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is Not assessed for 1,2-Dichloroethane in ACS-IE-MS-017as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is Not assessed for 1,3,5-Trichlorobenzene in ACS-IE-MS-017as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is Not assessed for 4-Nonylphenol in ACS-IE-MS-017as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is Not assessed for Aclonifen in ACS-IE-MS-017as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is Not assessed for Anthracene in ACS-IE-MS-017as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is Not assessed for Anthracene in ACS-IE-MS-017as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is achieved for Anthracene in ACS-IE-MS-017as assessments completed meet the minimum of 4 sites/assessments and also meet threshold criteria of 90% compliance.	Parameter status is Not assessed for Atrazine in ACS-IE-MS-017as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is Not assessed for BDE 85 (2,2�,3,4,4�-pentabromodiphenyl ether) in ACS-IE-MS-017as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is Not assessed for BDE-183 (2,2',3,4,4',5',6-heptabromodiphenyl ether) in ACS-IE-MS-017as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is Not assessed for BDE-66 (2,3',4,4'-tetrabromodiphenyl ether) in ACS-IE-MS-017as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is Not assessed for Benz(a)anthracene in ACS-IE-MS-017as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is achieved for Benz(a)anthracene in ACS-IE-MS-017as assessments completed meet the minimum of 4 sites/assessments and also meet threshold criteria of 90% compliance.	Parameter status is Not assessed for Benzene in ACS-IE-MS-017as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is Not assessed for Bifenox in ACS-IE-MS-017as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is Not assessed for Cadmium and its compounds in ACS-IE-MS-017as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is Not assessed for Cadmium and its compounds in ACS-IE-MS-017as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is achieved for Cadmium and its compounds in ACS-IE-MS-017as assessments completed meet the minimum of 4 sites/assessments and also meet threshold criteria of 90% compliance.	Parameter status is Not assessed for carbon tetrachloride in ACS-IE-MS-017as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is Not assessed for Chrysene in ACS-IE-MS-017as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is achieved for Chrysene in ACS-IE-MS-017as assessments completed meet the minimum of 4 sites/assessments and also meet threshold criteria of 90% compliance.	Parameter status is Not assessed for Cypermethrin in ACS-IE-MS-017as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is Not assessed for Di(2-ethylhexyl)phthalate (DEHP) in ACS-IE-MS-017as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is Not assessed for Dichloromethane in ACS-IE-MS-017as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is Not assessed for Dichlorvos in ACS-IE-MS-017as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is Not assessed for Dicofol in ACS-IE-MS-017as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is Not assessed for Diuron in ACS-IE-MS-017as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.		Parameter status is Not assessed for Fluoranthene in ACS-IE-MS-017as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Assessments completed in ACS-IE-MS-017 for Fluoranthene in this matrix meet the assemment threshold criteria of 90% compliance	Parameter status is achieved for Fluoranthene in ACS-IE-MS-017as assessments completed meet the minimum of 4 sites/assessments and also meet threshold criteria of 90% compliance.	Parameter status is Not assessed for Hexachlorobenzene in ACS-IE-MS-017as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is Not assessed for Hexachlorobenzene in ACS-IE-MS-017as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is Not assessed for Isoproturon in ACS-IE-MS-017as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is Not assessed for Lead and its compounds in ACS-IE-MS-017as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is Not assessed for Lead and its compounds in ACS-IE-MS-017as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is achieved for Lead and its compounds in ACS-IE-MS-017as assessments completed meet the minimum of 4 sites/assessments and also meet threshold criteria of 90% compliance.	Parameter status is Not assessed for Naphthalene in ACS-IE-MS-017as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is Not assessed for Naphthalene in ACS-IE-MS-017as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is Not assessed for Nickel and its compounds in ACS-IE-MS-017as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is Not assessed for Nickel and its compounds in ACS-IE-MS-017as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is Not assessed for Nonylphenol in ACS-IE-MS-017as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.		Parameter status is Not assessed for Phenanthrene in ACS-IE-MS-017as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is achieved for Phenanthrene in ACS-IE-MS-017as assessments completed meet the minimum of 4 sites/assessments and also meet threshold criteria of 90% compliance.	Parameter status is Not assessed for Pyrene in ACS-IE-MS-017as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is achieved for Pyrene in ACS-IE-MS-017as assessments completed meet the minimum of 4 sites/assessments and also meet threshold criteria of 90% compliance.	Parameter status is Not assessed for Quinoxyfen in ACS-IE-MS-017as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is Not assessed for Simazine in ACS-IE-MS-017as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is Not assessed for Terbutryn in ACS-IE-MS-017as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is Not assessed for Tetrachloroethylene in ACS-IE-MS-017as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is Not assessed for Trichloroethylene in ACS-IE-MS-017as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is achieved for Zinc and its compounds in ACS-IE-MS-017as assessments completed meet the minimum of 4 sites/assessments and also meet threshold criteria of 90% compliance.	Parameter status is Not assessed for Zinc and its compounds in ACS-IE-MS-017as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is Not assessed for BDE 100 (2,2�,4,4�,6-pentabromodiphenyl ether) in ACS-IE-MS-017as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status was not achieved for BDE 100 (2,2�,4,4�,6-pentabromodiphenyl ether) in ACS-IE-MS-017. The number of assessments meet the minimum of 4 sites/assessments but the element fails to meet threshold criteria of 90% compliance.	Parameter status is Not assessed for BDE 153 (2,2�,4,4�,5,5�-hexabromodiphenyl ether) in ACS-IE-MS-017as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is achieved for BDE 153 (2,2�,4,4�,5,5�-hexabromodiphenyl ether) in ACS-IE-MS-017as assessments completed meet the minimum of 4 sites/assessments and also meet threshold criteria of 90% compliance.	Parameter status is Not assessed for BDE 154 (2,2�,4,4�,5,6�-hexabromodiphenyl ether) in ACS-IE-MS-017as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is achieved for BDE 154 (2,2�,4,4�,5,6�-hexabromodiphenyl ether) in ACS-IE-MS-017as assessments completed meet the minimum of 4 sites/assessments and also meet threshold criteria of 90% compliance.	Parameter status is Not assessed for BDE 28 (2,4,4-tribromodiphenyl ether) in ACS-IE-MS-017as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status was not achieved for BDE 28 (2,4,4-tribromodiphenyl ether) in ACS-IE-MS-017. The number of assessments meet the minimum of 4 sites/assessments but the element fails to meet threshold criteria of 90% compliance.	Parameter status is Not assessed for BDE 47 (2,2�,4,4�-tetrabromodiphenyl ether) in ACS-IE-MS-017as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is achieved for BDE 47 (2,2�,4,4�-tetrabromodiphenyl ether) in ACS-IE-MS-017as assessments completed meet the minimum of 4 sites/assessments and also meet threshold criteria of 90% compliance.	Parameter status is Not assessed for BDE 99 (2,2�,4,4�,5-pentabromodiphenyl ether) in ACS-IE-MS-017as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is achieved for BDE 99 (2,2�,4,4�,5-pentabromodiphenyl ether) in ACS-IE-MS-017as assessments completed meet the minimum of 4 sites/assessments and also meet threshold criteria of 90% compliance.	Parameter status is Not assessed for Benz(a)pyrene in ACS-IE-MS-017as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is Not assessed for Benz(a)pyrene in ACS-IE-MS-017as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is achieved for Benz(a)pyrene in ACS-IE-MS-017as assessments completed meet the minimum of 4 sites/assessments and also meet threshold criteria of 90% compliance.	Parameter status is Not assessed for Benzo(b)fluoranthene in ACS-IE-MS-017as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is Not assessed for Benzo(g,h,i)perylene in ACS-IE-MS-017as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Assessments completed in ACS-IE-MS-017 for Benzo(g,h,i)perylene in this matrix meet the assemment threshold criteria of 90% compliance	Parameter status is achieved for Benzo(g,h,i)perylene in ACS-IE-MS-017as assessments completed meet the minimum of 4 sites/assessments and also meet threshold criteria of 90% compliance.	Assessments completed in ACS-IE-MS-017 for Benzo(k)fluoranthene in this matrix meet the assemment threshold criteria of 90% compliance	Parameter status is Not assessed for Hexabromocyclododecanes (HBCDD) in ACS-IE-MS-017as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is Not assessed for indeno[1,2,3-cd]pyrene; in ACS-IE-MS-017as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Assessments completed in ACS-IE-MS-017 for indeno[1,2,3-cd]pyrene; in this matrix meet the assemment threshold criteria of 90% compliance	Parameter status is achieved for indeno[1,2,3-cd]pyrene; in ACS-IE-MS-017as assessments completed meet the minimum of 4 sites/assessments and also meet threshold criteria of 90% compliance.	Parameter status is Not assessed for Mercury in ACS-IE-MS-017as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is Not assessed for Mercury in ACS-IE-MS-017as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status was not achieved for Mercury in ACS-IE-MS-017. The number of assessments meet the minimum of 4 sites/assessments but the element fails to meet threshold criteria of 90% compliance.			Parameter status is Not assessed for PCB 101 (2,2�,4,5,5�-pentachlorobiphenyl) in ACS-IE-MS-017as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is achieved for PCB 101 (2,2�,4,5,5�-pentachlorobiphenyl) in ACS-IE-MS-017as assessments completed meet the minimum of 4 sites/assessments and also meet threshold criteria of 90% compliance.	Assessments completed in ACS-IE-MS-017 for PCB 118 (2,3�,4,4�,5-pentachlorobiphenyl) in this matrix meet the assemment threshold criteria of 90% compliance	Parameter status was not achieved for PCB 118 (2,3�,4,4�,5-pentachlorobiphenyl) in ACS-IE-MS-017. The number of assessments meet the minimum of 4 sites/assessments but the element fails to meet threshold criteria of 90% compliance.	Parameter status is Not assessed for PCB 138 (2,2�,3,4,4�,5�-hexachlorobiphenyl) in ACS-IE-MS-017as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is achieved for PCB 138 (2,2�,3,4,4�,5�-hexachlorobiphenyl) in ACS-IE-MS-017as assessments completed meet the minimum of 4 sites/assessments and also meet threshold criteria of 90% compliance.	Parameter status is Not assessed for PCB 153 (2,2�,4,4�,5,5�-hexachlorobiphenyl) in ACS-IE-MS-017as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is achieved for PCB 153 (2,2�,4,4�,5,5�-hexachlorobiphenyl) in ACS-IE-MS-017as assessments completed meet the minimum of 4 sites/assessments and also meet threshold criteria of 90% compliance.	Parameter status is Not assessed for PCB 180 (2,2�,3,4,4�,5,5�-heptachlorobiphenyl) in ACS-IE-MS-017as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is achieved for PCB 180 (2,2�,3,4,4�,5,5�-heptachlorobiphenyl) in ACS-IE-MS-017as assessments completed meet the minimum of 4 sites/assessments and also meet threshold criteria of 90% compliance.	Parameter status is Not assessed for PCB 28 (2,4,4�-trichlorobiphenyl) in ACS-IE-MS-017as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is achieved for PCB 28 (2,4,4�-trichlorobiphenyl) in ACS-IE-MS-017as assessments completed meet the minimum of 4 sites/assessments and also meet threshold criteria of 90% compliance.	Parameter status is Not assessed for PCB 52 (2,2�,5,5�-tetrachlorobiphenyl) in ACS-IE-MS-017as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status was not achieved for PCB 52 (2,2�,5,5�-tetrachlorobiphenyl) in ACS-IE-MS-017. The number of assessments meet the minimum of 4 sites/assessments but the element fails to meet threshold criteria of 90% compliance.	Parameter status is Not assessed for PFOS in ACS-IE-MS-017as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.		Parameter status is Not assessed for TBT in ACS-IE-MS-017as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is Not assessed for TBT in ACS-IE-MS-017as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is achieved for Imposex in ACS-IE-MS-017as assessments completed meet the minimum of 4 sites/assessments and also meet threshold criteria of 90% compliance.
Related indicator
Criteria status																			Unknown	Unknown											Unknown							Unknown	Unknown				Unknown	Unknown		Good																																Unknown				Not good	Not good		Good	Good															Unknown	Good	Unknown	Unknown	Good	Good, based on low risk
Description criteria																			The status of Cadmium and its compounds is Unknown in the Irish Sea.Trend status is Improving.	The status of Cadmium and its compounds is Unknown in the Irish Sea.Trend status is Improving.											The status of WFD PS is Unknown in the Irish Sea.Trend status is Unknown.							The status of Lead and its compounds is Unknown in the Irish Sea.Trend status is Improving.	The status of Lead and its compounds is Unknown in the Irish Sea.Trend status is Improving.				The status of Nickel and its compounds is Unknown in the Irish Sea.Trend status is Unknown.	The status of Nickel and its compounds is Unknown in the Irish Sea.Trend status is Unknown.		The status of PAHs is Good in the Irish Sea based on 95% of assessments meeting the 90% criteria. Trend status is Improving.																																The status of HBCDD is Unknown in the Irish Sea.Trend status is Unknown.				The status of Mercury and its compounds is Not good in the Irish Sea based on 87.5% of assessments meeting the 90% criteria. Trend status is Not assessed.	The status of Mercury and its compounds is Not good in the Irish Sea based on 87.5% of assessments meeting the 90% criteria. Trend status is Not assessed.		The status of PAHs is Good in the Irish Sea based on 100% of assessments meeting the 90% criteria. Trend status is Improving.	The status of PBDEs is Good in the Irish Sea based on 95% of assessments meeting the 90% criteria. Trend status is Not assessed.															The status of PFOS is Unknown in the Irish Sea.Trend status is Unknown.	The status of PCBs is Good in the Irish Sea based on 92.7% of assessments meeting the 90% criteria. Trend status is Improving.	The status of TBT is Unknown in the Irish Sea based on % of assessments meeting the 90% criteria. Trend status is Unknown.	The status of TBT is Unknown in the Irish Sea based on % of assessments meeting the 90% criteria. Trend status is Unknown.	The status of Imposex is Good in the Irish Sea based on 100% of assessments meeting the 90% criteria. Trend status is Improving.
Element status	Not relevant																		Not relevant	Not relevant											Not relevant							Not relevant	Not relevant				Not relevant	Not relevant		Not relevant																																Not relevant				Not relevant	Not relevant		Not relevant	Not relevant															Not relevant	Not relevant	Not relevant	Not relevant
Description element	A total of 100% of assessments for Imposex in the Irish Sea was obtained relative to a 90% threshold.The trend is Improving																		A total of 100% of assessments for Cadmium and its compounds in the Irish Sea was obtained relative to a 90% threshold.The trend is Improving	A total of 100% of assessments for Cadmium and its compounds in the Irish Sea was obtained relative to a 90% threshold.The trend is Improving											The number of assessments of Environmental UPBT contaminants - WFD UPBT substances in the Irish Sea is insufficient to complete assessment relative to a 90% threshold.							The number of assessments of Lead and its compounds in the Irish Sea is insufficient to complete assessment relative to a 90% threshold.	The number of assessments of Lead and its compounds in the Irish Sea is insufficient to complete assessment relative to a 90% threshold.				The number of assessments of Nickel and its compounds in the Irish Sea is insufficient to complete assessment relative to a 90% threshold.	The number of assessments of Nickel and its compounds in the Irish Sea is insufficient to complete assessment relative to a 90% threshold.		95% of assessments of PAH in the Irish Sea met with the 90% threshold value. Trends were Not assessed																																The number of assessments of HBCDD in the Irish Sea is insufficient to complete assessment relative to a 90% threshold.				87.5% of assessments of Mercury and its compounds in the Irish Sea met with the 90% threshold value. Trends were Not assessed	87.5% of assessments of Mercury and its compounds in the Irish Sea met with the 90% threshold value. Trends were Not assessed		100% of assessments of PAH in the Irish Sea met with the 90% threshold value. Trends were Not assessed	95% of assessments of PBDE in the Irish Sea met with the 90% threshold value. Trends were Not assessed															The number of assessments of PFOS in the Irish Sea is insufficient to complete assessment relative to a 90% threshold.	92.7% of assessments of Polychlorinated biphenyls (7 PCB: 28,52,101,118,138,153,180) in the Irish Sea met with the 90% threshold value. Trends were Not assessed	The number of assessments of TBT in the Irish Sea is insufficient to complete assessment relative to a 90% threshold.	The number of assessments of TBT in the Irish Sea is insufficient to complete assessment relative to a 90% threshold.
Source assessment feature	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD
Reporting method feature	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C
Trend feature	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed
Integration rule type parameter	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE
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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.
Integration rule type criteria
Integration rule description criteria
GES extent threshold
GES extent achieved	87.50	95.00	95.00	95.00	95.00	95.00	95.00	95.00	95.00	95.00	95.00	95.00	95.00	95.00	95.00	95.00	95.00	95.00	95.00	95.00	95.00	95.00	95.00	95.00	95.00	95.00	95.00	95.00	95.00	95.00	95.00	95.00	95.00	95.00	95.00	95.00	95.00	95.00	95.00	95.00	95.00	95.00	95.00	95.00	95.00	95.00	95.00	95.00	95.00	95.00	95.00	95.00	95.00	95.00	95.00	95.00	95.00	87.50	87.50	87.50	87.50	87.50	87.50	87.50	87.50	87.50	87.50	87.50	87.50	87.50	87.50	87.50	87.50	87.50	87.50	87.50	87.50	87.50	87.50	87.50	87.50	87.50	87.50	87.50	87.50	87.50	87.50	87.50	87.50	87.50	87.50	87.50	87.50	87.50	87.50	87.50	87.50	87.50	87.50	87.50	87.50	87.50	87.50	87.50
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
GES achieved	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed
Description overall status	UPBT concentrations in water, sediments and biota in the Irish seas are mostly in GES. Legacy issues persist for Mercury in this area where discreet failures for shellfish were present. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish seas are in GES. GES extent thresholds have not been defined at a regional or EU level.	UPBT concentrations in water, sediments and biota in the Irish seas are mostly in GES. Legacy issues persist for Mercury in this area where discreet failures for shellfish were present. GES extent thresholds have not been defined at a regional or EU level.	UPBT concentrations in water, sediments and biota in the Irish seas are mostly in GES. Legacy issues persist for Mercury in this area where discreet failures for shellfish were present. GES extent thresholds have not been defined at a regional or EU level.	UPBT concentrations in water, sediments and biota in the Irish seas are mostly in GES. Legacy issues persist for Mercury in this area where discreet failures for shellfish were present. GES extent thresholds have not been defined at a regional or EU level.	UPBT concentrations in water, sediments and biota in the Irish seas are mostly in GES. Legacy issues persist for Mercury in this area where discreet failures for shellfish were present. GES extent thresholds have not been defined at a regional or EU level.	UPBT concentrations in water, sediments and biota in the Irish seas are mostly in GES. Legacy issues persist for Mercury in this area where discreet failures for shellfish were present. GES extent thresholds have not been defined at a regional or EU level.	UPBT concentrations in water, sediments and biota in the Irish seas are mostly in GES. Legacy issues persist for Mercury in this area where discreet failures for shellfish were present. GES extent thresholds have not been defined at a regional or EU level.	UPBT concentrations in water, sediments and biota in the Irish seas are mostly in GES. Legacy issues persist for Mercury in this area where discreet failures for shellfish were present. GES extent thresholds have not been defined at a regional or EU level.	UPBT concentrations in water, sediments and biota in the Irish seas are mostly in GES. Legacy issues persist for Mercury in this area where discreet failures for shellfish were present. GES extent thresholds have not been defined at a regional or EU level.	UPBT concentrations in water, sediments and biota in the Irish seas are mostly in GES. Legacy issues persist for Mercury in this area where discreet failures for shellfish were present. GES extent thresholds have not been defined at a regional or EU level.	UPBT concentrations in water, sediments and biota in the Irish seas are mostly in GES. Legacy issues persist for Mercury in this area where discreet failures for shellfish were present. GES extent thresholds have not been defined at a regional or EU level.	UPBT concentrations in water, sediments and biota in the Irish seas are mostly in GES. Legacy issues persist for Mercury in this area where discreet failures for shellfish were present. GES extent thresholds have not been defined at a regional or EU level.	UPBT concentrations in water, sediments and biota in the Irish seas are mostly in GES. Legacy issues persist for Mercury in this area where discreet failures for shellfish were present. GES extent thresholds have not been defined at a regional or EU level.	UPBT concentrations in water, sediments and biota in the Irish seas are mostly in GES. Legacy issues persist for Mercury in this area where discreet failures for shellfish were present. GES extent thresholds have not been defined at a regional or EU level.	UPBT concentrations in water, sediments and biota in the Irish seas are mostly in GES. Legacy issues persist for Mercury in this area where discreet failures for shellfish were present. GES extent thresholds have not been defined at a regional or EU level.	UPBT concentrations in water, sediments and biota in the Irish seas are mostly in GES. Legacy issues persist for Mercury in this area where discreet failures for shellfish were present. GES extent thresholds have not been defined at a regional or EU level.	UPBT concentrations in water, sediments and biota in the Irish seas are mostly in GES. Legacy issues persist for Mercury in this area where discreet failures for shellfish were present. GES extent thresholds have not been defined at a regional or EU level.	UPBT concentrations in water, sediments and biota in the Irish seas are mostly in GES. Legacy issues persist for Mercury in this area where discreet failures for shellfish were present. GES extent thresholds have not been defined at a regional or EU level.	UPBT concentrations in water, sediments and biota in the Irish seas are mostly in GES. Legacy issues persist for Mercury in this area where discreet failures for shellfish were present. GES extent thresholds have not been defined at a regional or EU level.	UPBT concentrations in water, sediments and biota in the Irish seas are mostly in GES. Legacy issues persist for Mercury in this area where discreet failures for shellfish were present. GES extent thresholds have not been defined at a regional or EU level.	UPBT concentrations in water, sediments and biota in the Irish seas are mostly in GES. Legacy issues persist for Mercury in this area where discreet failures for shellfish were present. GES extent thresholds have not been defined at a regional or EU level.	UPBT concentrations in water, sediments and biota in the Irish seas are mostly in GES. Legacy issues persist for Mercury in this area where discreet failures for shellfish were present. GES extent thresholds have not been defined at a regional or EU level.	UPBT concentrations in water, sediments and biota in the Irish seas are mostly in GES. Legacy issues persist for Mercury in this area where discreet failures for shellfish were present. GES extent thresholds have not been defined at a regional or EU level.	UPBT concentrations in water, sediments and biota in the Irish seas are mostly in GES. Legacy issues persist for Mercury in this area where discreet failures for shellfish were present. GES extent thresholds have not been defined at a regional or EU level.	UPBT concentrations in water, sediments and biota in the Irish seas are mostly in GES. Legacy issues persist for Mercury in this area where discreet failures for shellfish were present. GES extent thresholds have not been defined at a regional or EU level.	UPBT concentrations in water, sediments and biota in the Irish seas are mostly in GES. Legacy issues persist for Mercury in this area where discreet failures for shellfish were present. GES extent thresholds have not been defined at a regional or EU level.	UPBT concentrations in water, sediments and biota in the Irish seas are mostly in GES. Legacy issues persist for Mercury in this area where discreet failures for shellfish were present. GES extent thresholds have not been defined at a regional or EU level.	UPBT concentrations in water, sediments and biota in the Irish seas are mostly in GES. Legacy issues persist for Mercury in this area where discreet failures for shellfish were present. GES extent thresholds have not been defined at a regional or EU level.	UPBT concentrations in water, sediments and biota in the Irish seas are mostly in GES. Legacy issues persist for Mercury in this area where discreet failures for shellfish were present. GES extent thresholds have not been defined at a regional or EU level.	UPBT concentrations in water, sediments and biota in the Irish seas are mostly in GES. Legacy issues persist for Mercury in this area where discreet failures for shellfish were present. GES extent thresholds have not been defined at a regional or EU level.	UPBT concentrations in water, sediments and biota in the Irish seas are mostly in GES. Legacy issues persist for Mercury in this area where discreet failures for shellfish were present. GES extent thresholds have not been defined at a regional or EU level.	UPBT concentrations in water, sediments and biota in the Irish seas are mostly in GES. Legacy issues persist for Mercury in this area where discreet failures for shellfish were present. GES extent thresholds have not been defined at a regional or EU level.	UPBT concentrations in water, sediments and biota in the Irish seas are mostly in GES. Legacy issues persist for Mercury in this area where discreet failures for shellfish were present. GES extent thresholds have not been defined at a regional or EU level.	UPBT concentrations in water, sediments and biota in the Irish seas are mostly in GES. Legacy issues persist for Mercury in this area where discreet failures for shellfish were present. GES extent thresholds have not been defined at a regional or EU level.	UPBT concentrations in water, sediments and biota in the Irish seas are mostly in GES. Legacy issues persist for Mercury in this area where discreet failures for shellfish were present. GES extent thresholds have not been defined at a regional or EU level.	UPBT concentrations in water, sediments and biota in the Irish seas are mostly in GES. Legacy issues persist for Mercury in this area where discreet failures for shellfish were present. GES extent thresholds have not been defined at a regional or EU level.	UPBT concentrations in water, sediments and biota in the Irish seas are mostly in GES. Legacy issues persist for Mercury in this area where discreet failures for shellfish were present. GES extent thresholds have not been defined at a regional or EU level.	UPBT concentrations in water, sediments and biota in the Irish seas are mostly in GES. Legacy issues persist for Mercury in this area where discreet failures for shellfish were present. GES extent thresholds have not been defined at a regional or EU level.	UPBT concentrations in water, sediments and biota in the Irish seas are mostly in GES. Legacy issues persist for Mercury in this area where discreet failures for shellfish were present. GES extent thresholds have not been defined at a regional or EU level.	UPBT concentrations in water, sediments and biota in the Irish seas are mostly in GES. Legacy issues persist for Mercury in this area where discreet failures for shellfish were present. GES extent thresholds have not been defined at a regional or EU level.	UPBT concentrations in water, sediments and biota in the Irish seas are mostly in GES. Legacy issues persist for Mercury in this area where discreet failures for shellfish were present. GES extent thresholds have not been defined at a regional or EU level.	UPBT concentrations in water, sediments and biota in the Irish seas are mostly in GES. Legacy issues persist for Mercury in this area where discreet failures for shellfish were present. GES extent thresholds have not been defined at a regional or EU level.	UPBT concentrations in water, sediments and biota in the Irish seas are mostly in GES. Legacy issues persist for Mercury in this area where discreet failures for shellfish were present. GES extent thresholds have not been defined at a regional or EU level.	UPBT concentrations in water, sediments and biota in the Irish seas are mostly in GES. Legacy issues persist for Mercury in this area where discreet failures for shellfish were present. GES extent thresholds have not been defined at a regional or EU level.	UPBT concentrations in water, sediments and biota in the Irish seas are mostly in GES. Legacy issues persist for Mercury in this area where discreet failures for shellfish were present. GES extent thresholds have not been defined at a regional or EU level.	UPBT concentrations in water, sediments and biota in the Irish seas are mostly in GES. Legacy issues persist for Mercury in this area where discreet failures for shellfish were present. GES extent thresholds have not been defined at a regional or EU level.	UPBT concentrations in water, sediments and biota in the Irish seas are mostly in GES. Legacy issues persist for Mercury in this area where discreet failures for shellfish were present. GES extent thresholds have not been defined at a regional or EU level.	UPBT concentrations in water, sediments and biota in the Irish seas are mostly in GES. Legacy issues persist for Mercury in this area where discreet failures for shellfish were present. GES extent thresholds have not been defined at a regional or EU level.
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	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	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-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017	IE-D8T1a-1-MRU017 IE-D8T1a-MRU017 IE-D8T1b-1-MRU017 IE-D8T1b-MRU017 IE-D8T2-MRU017
Test TV	NA	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	No	No	Yes	Yes	No	No	Yes	NA	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	No	Yes	Yes	Yes	Yes	Yes	NA	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	No	No	Yes	Yes	Yes	No	No	No	Yes	Yes	NA	NA	Yes	Yes	Yes	No	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	NA	No	Yes	Yes	NA
Test results	False	False	False	False	False	False	False	False	False	Correct	False	False	False	False	False	Correct	False	False	False	False	Correct	False	False	False	False	False	False	False	False	False	False	False	Correct	Correct	False	False	False	False	False	False	False	False	False	False	False	False	False	Correct	False	Correct	False	False	False	False	False	False	False	False	False	False	Correct	False	Correct	False	False	False	Correct	False	Correct	False	False	Correct	False	False	False	False	Correct	False	False	False	False	False	False	False	False	False	False	Correct	Correct	Correct	False	Correct	False	Correct	False	Correct	False	Correct	False	False	False	False	False	False	Correct	False

ACS-IE-MS-018

Simplified table

Regional assessment area	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast	OSPAR-Irish and Scottish West Coast
Component MRUs
GES component	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8
Feature	Contaminants - UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Species	Acute pollution events
Element	Imposex	1,2,3-Trichlorobenzene	1,2,4-Trichlorobenzene	1,2-Dichloroethane	1,3,5-Trichlorobenzene	4-Nonylphenol	Aclonifen	Anthracene	Anthracene	Anthracene	Atrazine	BDE 85 (2,2’,3,4,4’-pentabromodiphenyl ether)	BDE-183 (2,2',3,4,4',5',6-heptabromodiphenyl ether)	BDE-66 (2,3',4,4'-tetrabromodiphenyl ether)	Benz(a)anthracene	Benz(a)anthracene	Benzene	Bifenox	Cadmium and its compounds	Cadmium and its compounds	Cadmium and its compounds	Carbon tetrachloride	Chrysene	Chrysene	Cypermethrin	Di(2-ethylhexyl)phthalate (DEHP)	Dichloromethane	Dichlorvos	Dicofol	Diuron	Environmental UPBT contaminants - WFD UPBT substances	Fluoranthene	Fluoranthene	Fluoranthene	Hexachlorobenzene	Hexachlorobenzene	Isoproturon	Lead and its compounds	Lead and its compounds	Lead and its compounds	Naphthalene	Naphthalene	Nickel and its compounds	Nickel and its compounds	Nonylphenol	PAH	Phenanthrene	Phenanthrene	Pyrene	Pyrene	Quinoxyfen	Simazine	Terbutryn	Tetrachloroethylene	Trichloroethylene	Zinc and its compounds	Zinc and its compounds	BDE 100 (2,2’,4,4’,6-pentabromodiphenyl ether)	BDE 153 (2,2’,4,4’,5,5’-hexabromodiphenyl ether)	BDE 154 (2,2’,4,4’,5,6’-hexabromodiphenyl ether)	BDE 154 (2,2’,4,4’,5,6’-hexabromodiphenyl ether)	BDE 28 (2,4,4-tribromodiphenyl ether)	BDE 28 (2,4,4-tribromodiphenyl ether)	BDE 47 (2,2’,4,4’-tetrabromodiphenyl ether)	BDE 47 (2,2’,4,4’-tetrabromodiphenyl ether)	BDE 99 (2,2’,4,4’,5-pentabromodiphenyl ether)	BDE 99 (2,2’,4,4’,5-pentabromodiphenyl ether)	Benzo(a)pyrene	Benzo(a)pyrene	Benzo(a)pyrene	Benzo(b)fluoranthene	Benzo(g,h,i)perylene	Benzo(g,h,i)perylene	Benzo(g,h,i)perylene	Benzo(k)fluoranthene	Hexabromocyclododecanes (HBCDD)	Indeno(1,2,3,-cd)pyrene	Indeno(1,2,3,-cd)pyrene	Indeno(1,2,3,-cd)pyrene	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	PAH	PBDE	PCB 101 (2,2’,4,5,5’-pentachlorobiphenyl)	PCB 101 (2,2’,4,5,5’-pentachlorobiphenyl)	PCB 118 (2,3’,4,4’,5-pentachlorobiphenyl)	PCB 118 (2,3’,4,4’,5-pentachlorobiphenyl)	PCB 138 (2,2’,3,4,4’,5’-hexachlorobiphenyl)	PCB 138 (2,2’,3,4,4’,5’-hexachlorobiphenyl)	PCB 153 (2,2’,4,4’,5,5’-hexachlorobiphenyl)	PCB 153 (2,2’,4,4’,5,5’-hexachlorobiphenyl)	PCB 180 (2,2’,3,4,4’,5,5’-heptachlorobiphenyl)	PCB 180 (2,2’,3,4,4’,5,5’-heptachlorobiphenyl)	PCB 28 (2,4,4’-trichlorobiphenyl)	PCB 28 (2,4,4’-trichlorobiphenyl)	PCB 52 (2,2’,5,5’-tetrachlorobiphenyl)	PCB 52 (2,2’,5,5’-tetrachlorobiphenyl)	PFOS	Polychlorinated biphenyls (7 PCB: 28,52,101,118,138,153,180)	TBT	TBT	TBT	Imposex
Element extent
Trend element	Improving																		Improving	Improving											Not assessed							Improving	Improving				Not assessed	Not assessed		Improving																														Not assessed				Not assessed	Not assessed	Not assessed	Stable	Not assessed															Not assessed	Improving	Not assessed	Not assessed	Not assessed
Element 2	Nucella lapillus									Mytilus spp						Mytilus spp					Mytilus spp			Mytilus spp										Mytilus spp		Mytilus spp				Mytilus spp								Mytilus spp		Mytilus spp																																																						Nucella lapillus
Element source	OSPAR																		OSPAR; EQS Directive (2013/39/EU)	OSPAR; EQS Directive (2013/39/EU)											EQS Directive (2013/39/EU)							OSPAR; EQS Directive (2013/39/EU)	OSPAR; EQS Directive (2013/39/EU)				OSPAR; EQS Directive (2013/39/EU)	OSPAR; EQS Directive (2013/39/EU)		OSPAR; EQS Directive (2013/39/EU)																														EQS Directive (2013/39/EU)				OSPAR; EQS Directive (2013/39/EU)	OSPAR; EQS Directive (2013/39/EU)	OSPAR; EQS Directive (2013/39/EU)	OSPAR; EQS Directive (2013/39/EU)	OSPAR															EQS Directive (2013/39/EU)	OSPAR	EQS Directive (2013/39/EU)	EQS Directive (2013/39/EU)	EQS Directive (2013/39/EU)
Criterion		D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C2	D8C3
Parameter		Concentration in water	Concentration in water	Concentration in water	Concentration in water	Concentration in water	Concentration in water	CONC-S-63	Concentration in water	CONC-B-Other	Concentration in water	CONC-S-63	CONC-S-63	CONC-S-63	CONC-S-63	CONC-B-Other	Concentration in water	Concentration in water	CONC-S-63	Concentration in water	CONC-B-Other	Concentration in water	CONC-S-63	CONC-B-Other	Concentration in water	Concentration in water	Concentration in water	Concentration in water	Concentration in water	Concentration in water		CONC-S-63	Concentration in water	CONC-B-Other	CONC-S-63	CONC-B-Other	Concentration in water	CONC-S-63	Concentration in water	CONC-B-Other	CONC-S-63	Concentration in water	CONC-S-63	Concentration in water	Concentration in water		CONC-S-63	CONC-B-Other	CONC-S-63	CONC-B-Other	Concentration in water	Concentration in water	Concentration in water	Concentration in water	Concentration in water	CONC-B-Other	CONC-S-63	CONC-S-63	CONC-S-63	CONC-B-Other	CONC-S-63	CONC-B-Other	CONC-S-63	CONC-B-Other	CONC-S-63	CONC-B-Other	CONC-S-63	CONC-B-Other	CONC-S-63	Concentration in water	Concentration in water	CONC-B-Other	CONC-S-63	Concentration in water	Concentration in water	Concentration in water	CONC-B-Other	CONC-S-63	Concentration in water	CONC-B-Other	CONC-S-63	Concentration in water			CONC-B-Other	CONC-S-63	CONC-B-Other	CONC-S-63	CONC-B-Other	CONC-S-63	CONC-B-Other	CONC-S-63	CONC-B-Other	CONC-S-63	CONC-B-Other	CONC-S-63	CONC-B-Other	CONC-S-63	Concentration in water		CONC-B-Other	CONC-S-63	Concentration in water	Imposex
Threshold value upper		0.4	0.4	10.0	0.4	2.0	0.12	85.0	0.1	290.0	2.0	1.0	14000.0	97.5	261.0	80.0	50.0	0.004	1.2	0.45	960.0	12.0	384.0	8.1	6e-05	1.3	20.0	7e-05	3.2e-05	0.2		600.0	0.12	110.0	0.16	0.63	1.0	47.0	14.0	1300.0	160.0	130.0	36.0	34.0	2.0		240.0	1700.0	665.0	100.0	0.54	4.0	0.034	10.0	10.0	63000.0	150.0	1.0	1100.0	6.8	1100.0	204.06	110.0	74.82	110.0	1.7	1.0	600.0	430.0	0.027	0.017	2.5	103.0	0.00017	0.017	0.05	2.4	103.0	0.00017	123.0	0.15	0.07			10.28	3.0	2.12	0.6	26.9	7.9	134.7	40.0	39.87	12.0	5.69	1.7	9.18	2.7	7.2		12.0	0.8	0.0015	2.0
Threshold value lower
Threshold value operator		<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=		<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=		<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=			<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=	<=		<=	<=	<=	<=
Threshold qualitative
Threshold value source		EQS Directive (2013/39/EU)	EQS Directive (2013/39/EU)	EQS Directive (2013/39/EU)	EQS Directive (2013/39/EU)	EQS Directive (2013/39/EU)	EQS Directive (2013/39/EU)	OSPAR Convention	EQS Directive (2013/39/EU)	OSPAR Convention	EQS Directive (2013/39/EU)	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	EQS Directive (2013/39/EU)	EQS Directive (2013/39/EU)	OSPAR Convention	EQS Directive (2013/39/EU)	OSPAR Convention	EQS Directive (2013/39/EU)	OSPAR Convention	OSPAR Convention	EQS Directive (2013/39/EU)	EQS Directive (2013/39/EU)	EQS Directive (2013/39/EU)	EQS Directive (2013/39/EU)	EQS Directive (2013/39/EU)	EQS Directive (2013/39/EU)		OSPAR Convention	EQS Directive (2013/39/EU)	OSPAR Convention	OSPAR Convention	OSPAR Convention	EQS Directive (2013/39/EU)	OSPAR Convention	EQS Directive (2013/39/EU)	OSPAR Convention	OSPAR Convention	EQS Directive (2013/39/EU)	OSPAR Convention	EQS Directive (2013/39/EU)	EQS Directive (2013/39/EU)		OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	EQS Directive (2013/39/EU)	EQS Directive (2013/39/EU)	EQS Directive (2013/39/EU)	EQS Directive (2013/39/EU)	EQS Directive (2013/39/EU)	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	EQS Directive (2013/39/EU)	EQS Directive (2013/39/EU)	OSPAR Convention	OSPAR Convention	EQS Directive (2013/39/EU)	EQS Directive (2013/39/EU)	EQS Directive (2013/39/EU)	OSPAR Convention	OSPAR Convention	EQS Directive (2013/39/EU)	OSPAR Convention	OSPAR Convention	EQS Directive (2013/39/EU)			OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention	EQS Directive (2013/39/EU)		OSPAR Convention	OSPAR Convention	EQS Directive (2013/39/EU)	OSPAR Convention
Value achieved upper		0.005	0.005	0.03	0.005	0.085	0.01	3.756544503	0.002	1.512969338	0.005	0.130890052	0.130890052	0.130890052	14.26701571	3.456391536	0.03	0.002	0.700050761	0.05	636.0993581	0.05	18.32460733	8.290031341	0.0005	0.055	0.03	0.0001	0.0001	0.01		30.7591623	0.002	20.31314246	0.130890052	0.266751955	0.01	70.26045016	0.18	658.9815942	6.010928962	0.005	43.61414791	0.18	0.005		15.57591623	26.56508412	23.69109948	32.22541971	0.02	0.005	0.01	0.05	0.05	106804.387	123.5583756	0.130890052	0.130890052	0.181185195	0.130890052	0.223927289	0.130890052	0.346351869	0.130890052	0.304595609	0.130890052	2.895271203	14.52879581	0.002	0.002	5.465475612		0.002	0.002	0.000179	2.832283487	17.53926702	0.003	83.41741495	0.11318328	0.00104			0.276643091	0.104712042	0.366352789	0.104712042	0.797048226	0.104712042	1.556452383	0.104712042	0.07920759	0.104712042	0.16220445	0.104712042	0.200119823	0.104712042	0.0001225			6.544502618	3e-05	0.361666667
Value achieved lower
Value unit		microgram per litre	microgram per litre	microgram per litre	microgram per litre	microgram per litre	microgram per litre	microgram per kilogram of dry weight	microgram per litre	microgram per kilogram of dry weight	microgram per litre	microgram per kilogram of dry weight	microgram per kilogram of dry weight	microgram per kilogram of dry weight	microgram per kilogram of dry weight	microgram per kilogram of dry weight	microgram per litre	microgram per litre	mg/kg dw	microgram per litre	microgram per kilogram of dry weight	microgram per litre	microgram per kilogram of dry weight	microgram per kilogram of dry weight	microgram per litre	microgram per litre	microgram per litre	microgram per litre	microgram per litre	microgram per litre		microgram per kilogram of dry weight	microgram per litre	microgram per kilogram of wet weight	microgram per kilogram of dry weight	microgram per kilogram of wet weight	microgram per litre	mg/kg dw	microgram per litre	microgram per kilogram of dry weight	microgram per kilogram of dry weight	microgram per litre	mg/kg dw	microgram per litre	microgram per litre		microgram per kilogram of dry weight	microgram per kilogram of dry weight	microgram per kilogram of dry weight	microgram per kilogram of dry weight	microgram per litre	microgram per litre	microgram per litre	microgram per litre	microgram per litre	microgram per kilogram of dry weight	mg/kg dw	microgram per kilogram of dry weight	microgram per kilogram of dry weight	ug/kg lw	microgram per kilogram of dry weight	ug/kg lw	microgram per kilogram of dry weight	ug/kg lw	microgram per kilogram of dry weight	ug/kg lw	microgram per kilogram of dry weight	microgram per kilogram of wet weight	microgram per kilogram of dry weight	microgram per litre	microgram per litre	microgram per litre	microgram per kilogram of dry weight	microgram per litre	microgram per litre	microgram per litre	microgram per kilogram of dry weight	microgram per kilogram of dry weight	microgram per litre	microgram per kilogram of wet weight	mg/kg dw	microgram per litre			ug/kg lw	microgram per kilogram of dry weight	ug/kg lw	microgram per kilogram of dry weight	ug/kg lw	microgram per kilogram of dry weight	ug/kg lw	microgram per kilogram of dry weight	ug/kg lw	microgram per kilogram of dry weight	ug/kg lw	microgram per kilogram of dry weight	ug/kg lw	microgram per kilogram of dry weight	microgram per litre		microgram per kilogram of dry weight	microgram per kilogram of dry weight	microgram per litre	index VDSI
Proportion threshold value
Proportion value achieved
Proportion threshold value unit
Trend parameter		Stable	Stable	Stable	Stable	Stable	Stable	Not relevant	Stable	Stable	Stable	Not relevant	Not relevant	Not relevant	Not relevant	Stable	Stable	Stable	Not relevant	Stable	Stable	Stable	Not relevant	Stable	Stable	Stable	Stable	Stable	Stable	Stable		Not relevant	Stable	Stable	Stable	Stable	Stable	Not relevant	Stable	Stable	Not relevant	Stable	Stable	Stable	Stable		Not relevant	Stable	Not relevant	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Not relevant	Not relevant	Not relevant	Stable	Not relevant	Stable	Not relevant	Stable	Not relevant	Stable	Not relevant	Stable	Not relevant	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Not relevant	Stable			Stable	Not relevant	Stable	Not relevant	Stable	Not relevant	Stable	Not relevant	Stable	Not relevant	Stable	Not relevant	Stable	Not relevant	Stable		Stable	Not relevant	Stable	Stable
Parameter achieved		Yes	Yes	Yes	Yes	Yes	Yes	Not assessed	Yes	Yes	Yes	Not assessed	Not assessed	Not assessed	Not assessed	Yes	Yes	Yes	Not assessed	Yes	Yes	Yes	Not assessed	Yes	Yes	Yes	Yes	Yes	Yes	Yes		Not assessed	Yes	Yes	Yes	Yes	Yes	Not assessed	Yes	Yes	Not assessed	Yes	Yes	Yes	Yes		Not assessed	Yes	Not assessed	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Not assessed	Not assessed	Not assessed	Yes	Not assessed	Yes	Not assessed	Yes	Not assessed	No	Not assessed	Yes	Not assessed	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	No	Not assessed	Yes			Yes	Not assessed	Yes	Not assessed	Yes	Not assessed	Yes	Not assessed	No	Not assessed	Yes	Not assessed	Yes	Not assessed	Yes		Yes	Not assessed	Yes	Yes
Description parameter		Parameter status is achieved for 1,2,3-Trichlorobenzene in ACS-IE-MS-018as assessments completed meet the minimum of 4 sites/assessments and also meet threshold criteria of 90% compliance.	Parameter status is achieved for 1,2,4-Trichlorobenzene in ACS-IE-MS-018as assessments completed meet the minimum of 4 sites/assessments and also meet threshold criteria of 90% compliance.	Parameter status is achieved for 1,2-Dichloroethane in ACS-IE-MS-018as assessments completed meet the minimum of 4 sites/assessments and also meet threshold criteria of 90% compliance.	Parameter status is achieved for 1,3,5-Trichlorobenzene in ACS-IE-MS-018as assessments completed meet the minimum of 4 sites/assessments and also meet threshold criteria of 90% compliance.	Parameter status is achieved for 4-Nonylphenol in ACS-IE-MS-018as assessments completed meet the minimum of 4 sites/assessments and also meet threshold criteria of 90% compliance.	Parameter status is achieved for Aclonifen in ACS-IE-MS-018as assessments completed meet the minimum of 4 sites/assessments and also meet threshold criteria of 90% compliance.	Parameter status is Not assessed for Anthracene in ACS-IE-MS-018as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is achieved for Anthracene in ACS-IE-MS-018as assessments completed meet the minimum of 4 sites/assessments and also meet threshold criteria of 90% compliance.	Parameter status is achieved for Anthracene in ACS-IE-MS-018as assessments completed meet the minimum of 4 sites/assessments and also meet threshold criteria of 90% compliance.	Parameter status is achieved for Atrazine in ACS-IE-MS-018as assessments completed meet the minimum of 4 sites/assessments and also meet threshold criteria of 90% compliance.	Parameter status is Not assessed for BDE 85 (2,2�,3,4,4�-pentabromodiphenyl ether) in ACS-IE-MS-018as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is Not assessed for BDE-183 (2,2',3,4,4',5',6-heptabromodiphenyl ether) in ACS-IE-MS-018as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is Not assessed for BDE-66 (2,3',4,4'-tetrabromodiphenyl ether) in ACS-IE-MS-018as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is Not assessed for Benz(a)anthracene in ACS-IE-MS-018as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is achieved for Benz(a)anthracene in ACS-IE-MS-018as assessments completed meet the minimum of 4 sites/assessments and also meet threshold criteria of 90% compliance.	Parameter status is achieved for Benzene in ACS-IE-MS-018as assessments completed meet the minimum of 4 sites/assessments and also meet threshold criteria of 90% compliance.	Parameter status is achieved for Bifenox in ACS-IE-MS-018as assessments completed meet the minimum of 4 sites/assessments and also meet threshold criteria of 90% compliance.	Parameter status is Not assessed for Cadmium and its compounds in ACS-IE-MS-018as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is achieved for Cadmium and its compounds in ACS-IE-MS-018as assessments completed meet the minimum of 4 sites/assessments and also meet threshold criteria of 90% compliance.	Assessments completed in ACS-IE-MS-018 for Cadmium and its compounds in this matrix meet the assemment threshold criteria of 90% compliance	Parameter status is achieved for carbon tetrachloride in ACS-IE-MS-018as assessments completed meet the minimum of 4 sites/assessments and also meet threshold criteria of 90% compliance.	Parameter status is Not assessed for Chrysene in ACS-IE-MS-018as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Assessments completed in ACS-IE-MS-018 for Chrysene in this matrix meet the assemment threshold criteria of 90% compliance	Parameter status is achieved for Cypermethrin in ACS-IE-MS-018as assessments completed meet the minimum of 4 sites/assessments and also meet threshold criteria of 90% compliance.	Parameter status is achieved for Di(2-ethylhexyl)phthalate (DEHP) in ACS-IE-MS-018as assessments completed meet the minimum of 4 sites/assessments and also meet threshold criteria of 90% compliance.	Parameter status is achieved for Dichloromethane in ACS-IE-MS-018as assessments completed meet the minimum of 4 sites/assessments and also meet threshold criteria of 90% compliance.	Parameter status is achieved for Dichlorvos in ACS-IE-MS-018as assessments completed meet the minimum of 4 sites/assessments and also meet threshold criteria of 90% compliance.	Parameter status is achieved for Dicofol in ACS-IE-MS-018as assessments completed meet the minimum of 4 sites/assessments and also meet threshold criteria of 90% compliance.	Parameter status is achieved for Diuron in ACS-IE-MS-018as assessments completed meet the minimum of 4 sites/assessments and also meet threshold criteria of 90% compliance.		Parameter status is Not assessed for Fluoranthene in ACS-IE-MS-018as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is achieved for Fluoranthene in ACS-IE-MS-018as assessments completed meet the minimum of 4 sites/assessments and also meet threshold criteria of 90% compliance.	Parameter status is achieved for Fluoranthene in ACS-IE-MS-018as assessments completed meet the minimum of 4 sites/assessments and also meet threshold criteria of 90% compliance.	Assessments completed in ACS-IE-MS-018 for Hexachlorobenzene in this matrix meet the assemment threshold criteria of 90% compliance	Parameter status is achieved for Hexachlorobenzene in ACS-IE-MS-018as assessments completed meet the minimum of 4 sites/assessments and also meet threshold criteria of 90% compliance.	Parameter status is achieved for Isoproturon in ACS-IE-MS-018as assessments completed meet the minimum of 4 sites/assessments and also meet threshold criteria of 90% compliance.	Parameter status is Not assessed for Lead and its compounds in ACS-IE-MS-018as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is achieved for Lead and its compounds in ACS-IE-MS-018as assessments completed meet the minimum of 4 sites/assessments and also meet threshold criteria of 90% compliance.	Assessments completed in ACS-IE-MS-018 for Lead and its compounds in this matrix meet the assemment threshold criteria of 90% compliance	Parameter status is Not assessed for Naphthalene in ACS-IE-MS-018as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is achieved for Naphthalene in ACS-IE-MS-018as assessments completed meet the minimum of 4 sites/assessments and also meet threshold criteria of 90% compliance.	Assessments completed in ACS-IE-MS-018 for Nickel and its compounds in this matrix meet the assemment threshold criteria of 90% compliance	Parameter status is achieved for Nickel and its compounds in ACS-IE-MS-018as assessments completed meet the minimum of 4 sites/assessments and also meet threshold criteria of 90% compliance.	Parameter status is achieved for Nonylphenol in ACS-IE-MS-018as assessments completed meet the minimum of 4 sites/assessments and also meet threshold criteria of 90% compliance.		Parameter status is Not assessed for Phenanthrene in ACS-IE-MS-018as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is achieved for Phenanthrene in ACS-IE-MS-018as assessments completed meet the minimum of 4 sites/assessments and also meet threshold criteria of 90% compliance.	Parameter status is Not assessed for Pyrene in ACS-IE-MS-018as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is achieved for Pyrene in ACS-IE-MS-018as assessments completed meet the minimum of 4 sites/assessments and also meet threshold criteria of 90% compliance.	Parameter status is achieved for Quinoxyfen in ACS-IE-MS-018as assessments completed meet the minimum of 4 sites/assessments and also meet threshold criteria of 90% compliance.	Parameter status is achieved for Simazine in ACS-IE-MS-018as assessments completed meet the minimum of 4 sites/assessments and also meet threshold criteria of 90% compliance.	Parameter status is achieved for Terbutryn in ACS-IE-MS-018as assessments completed meet the minimum of 4 sites/assessments and also meet threshold criteria of 90% compliance.	Parameter status is achieved for Tetrachloroethylene in ACS-IE-MS-018as assessments completed meet the minimum of 4 sites/assessments and also meet threshold criteria of 90% compliance.	Parameter status is achieved for Trichloroethylene in ACS-IE-MS-018as assessments completed meet the minimum of 4 sites/assessments and also meet threshold criteria of 90% compliance.	Assessments completed in ACS-IE-MS-018 for Zinc and its compounds in this matrix meet the assemment threshold criteria of 90% compliance	Parameter status is Not assessed for Zinc and its compounds in ACS-IE-MS-018as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is Not assessed for BDE 100 (2,2�,4,4�,6-pentabromodiphenyl ether) in ACS-IE-MS-018as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is Not assessed for BDE 153 (2,2�,4,4�,5,5�-hexabromodiphenyl ether) in ACS-IE-MS-018as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is achieved for BDE 154 (2,2�,4,4�,5,6�-hexabromodiphenyl ether) in ACS-IE-MS-018as assessments completed meet the minimum of 4 sites/assessments and also meet threshold criteria of 90% compliance.	Parameter status is Not assessed for BDE 154 (2,2�,4,4�,5,6�-hexabromodiphenyl ether) in ACS-IE-MS-018as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is achieved for BDE 28 (2,4,4-tribromodiphenyl ether) in ACS-IE-MS-018as assessments completed meet the minimum of 4 sites/assessments and also meet threshold criteria of 90% compliance.	Parameter status is Not assessed for BDE 28 (2,4,4-tribromodiphenyl ether) in ACS-IE-MS-018as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is achieved for BDE 47 (2,2�,4,4�-tetrabromodiphenyl ether) in ACS-IE-MS-018as assessments completed meet the minimum of 4 sites/assessments and also meet threshold criteria of 90% compliance.	Parameter status is Not assessed for BDE 47 (2,2�,4,4�-tetrabromodiphenyl ether) in ACS-IE-MS-018as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status was not achieved for BDE 99 (2,2�,4,4�,5-pentabromodiphenyl ether) in ACS-IE-MS-018. The number of assessments meet the minimum of 4 sites/assessments but the element fails to meet threshold criteria of 90% compliance.	Parameter status is Not assessed for BDE 99 (2,2�,4,4�,5-pentabromodiphenyl ether) in ACS-IE-MS-018as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is achieved for Benz(a)pyrene in ACS-IE-MS-018as assessments completed meet the minimum of 4 sites/assessments and also meet threshold criteria of 90% compliance.	Parameter status is Not assessed for Benz(a)pyrene in ACS-IE-MS-018as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is achieved for Benz(a)pyrene in ACS-IE-MS-018as assessments completed meet the minimum of 4 sites/assessments and also meet threshold criteria of 90% compliance.	Assessments completed in ACS-IE-MS-018 for Benzo(b)fluoranthene in this matrix meet the assemment threshold criteria of 90% compliance	Parameter status is achieved for Benzo(g,h,i)perylene in ACS-IE-MS-018as assessments completed meet the minimum of 4 sites/assessments and also meet threshold criteria of 90% compliance.	Assessments completed in ACS-IE-MS-018 for Benzo(g,h,i)perylene in this matrix meet the assemment threshold criteria of 90% compliance	Assessments completed in ACS-IE-MS-018 for Benzo(g,h,i)perylene in this matrix meet the assemment threshold criteria of 90% compliance	Assessments completed in ACS-IE-MS-018 for Benzo(k)fluoranthene in this matrix meet the assemment threshold criteria of 90% compliance	Parameter status is achieved for Hexabromocyclododecanes (HBCDD) in ACS-IE-MS-018as assessments completed meet the minimum of 4 sites/assessments and also meet threshold criteria of 90% compliance.	Assessments completed in ACS-IE-MS-018 for indeno[1,2,3-cd]pyrene; in this matrix meet the assemment threshold criteria of 90% compliance	Assessments completed in ACS-IE-MS-018 for indeno[1,2,3-cd]pyrene; in this matrix meet the assemment threshold criteria of 90% compliance	Assessments completed in ACS-IE-MS-018 for indeno[1,2,3-cd]pyrene; in this matrix meet the assemment threshold criteria of 90% compliance	Parameter status was not achieved for Mercury in ACS-IE-MS-018. The number of assessments meet the minimum of 4 sites/assessments but the element fails to meet threshold criteria of 90% compliance.	Parameter status is Not assessed for Mercury in ACS-IE-MS-018as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is achieved for Mercury in ACS-IE-MS-018as assessments completed meet the minimum of 4 sites/assessments and also meet threshold criteria of 90% compliance.			Parameter status is achieved for PCB 101 (2,2�,4,5,5�-pentachlorobiphenyl) in ACS-IE-MS-018as assessments completed meet the minimum of 4 sites/assessments and also meet threshold criteria of 90% compliance.	Parameter status is Not assessed for PCB 101 (2,2�,4,5,5�-pentachlorobiphenyl) in ACS-IE-MS-018as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is achieved for PCB 118 (2,3�,4,4�,5-pentachlorobiphenyl) in ACS-IE-MS-018as assessments completed meet the minimum of 4 sites/assessments and also meet threshold criteria of 90% compliance.	Parameter status is Not assessed for PCB 118 (2,3�,4,4�,5-pentachlorobiphenyl) in ACS-IE-MS-018as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is achieved for PCB 138 (2,2�,3,4,4�,5�-hexachlorobiphenyl) in ACS-IE-MS-018as assessments completed meet the minimum of 4 sites/assessments and also meet threshold criteria of 90% compliance.	Parameter status is Not assessed for PCB 138 (2,2�,3,4,4�,5�-hexachlorobiphenyl) in ACS-IE-MS-018as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is achieved for PCB 153 (2,2�,4,4�,5,5�-hexachlorobiphenyl) in ACS-IE-MS-018as assessments completed meet the minimum of 4 sites/assessments and also meet threshold criteria of 90% compliance.	Parameter status is Not assessed for PCB 153 (2,2�,4,4�,5,5�-hexachlorobiphenyl) in ACS-IE-MS-018as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status was not achieved for PCB 180 (2,2�,3,4,4�,5,5�-heptachlorobiphenyl) in ACS-IE-MS-018. The number of assessments meet the minimum of 4 sites/assessments but the element fails to meet threshold criteria of 90% compliance.	Parameter status is Not assessed for PCB 180 (2,2�,3,4,4�,5,5�-heptachlorobiphenyl) in ACS-IE-MS-018as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is achieved for PCB 28 (2,4,4�-trichlorobiphenyl) in ACS-IE-MS-018as assessments completed meet the minimum of 4 sites/assessments and also meet threshold criteria of 90% compliance.	Parameter status is Not assessed for PCB 28 (2,4,4�-trichlorobiphenyl) in ACS-IE-MS-018as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is achieved for PCB 52 (2,2�,5,5�-tetrachlorobiphenyl) in ACS-IE-MS-018as assessments completed meet the minimum of 4 sites/assessments and also meet threshold criteria of 90% compliance.	Parameter status is Not assessed for PCB 52 (2,2�,5,5�-tetrachlorobiphenyl) in ACS-IE-MS-018as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is achieved for PFOS in ACS-IE-MS-018as assessments completed meet the minimum of 4 sites/assessments and also meet threshold criteria of 90% compliance.		Assessments completed in ACS-IE-MS-018 for TBT in this matrix meet the assemment threshold criteria of 90% compliance	Parameter status is Not assessed for TBT in ACS-IE-MS-018as while monitoring data has been collected the number of assessments do not meet the minimum of 4 sites/assessments to assess compliance against the threshold.	Parameter status is achieved for TBT in ACS-IE-MS-018as assessments completed meet the minimum of 4 sites/assessments and also meet threshold criteria of 90% compliance.	Parameter status is achieved for Imposex in ACS-IE-MS-018as assessments completed meet the minimum of 4 sites/assessments and also meet threshold criteria of 90% compliance.
Related indicator
Criteria status																			Good	Good											Good							Good	Good				Good	Good		Good																														Good				Good	Good	Good	Good	Good															Good	Good	Not good	Not good	Not good	Good	Good, based on low risk
Description criteria																			The status of Cadmium and its compounds is Good in the Irish West Coast based on 100% of assessments meeting the 90% criteria. Trend status is Improving.	The status of Cadmium and its compounds is Good in the Irish West Coast based on 100% of assessments meeting the 90% criteria. Trend status is Improving.											The status of WFD PS is Good in the Irish West Coast based on 100% of assessments meeting the 90% criteria. Trend status is Stable.							The status of Lead and its compounds is Good in the Irish West Coast based on 92.9% of assessments meeting the 90% criteria. Trend status is Stable.	The status of Lead and its compounds is Good in the Irish West Coast based on 92.9% of assessments meeting the 90% criteria. Trend status is Stable.				The status of Nickel and its compounds is Good in the Irish West Coast based on 100% of assessments meeting the 90% criteria. Trend status is Not assessed.	The status of Nickel and its compounds is Good in the Irish West Coast based on 100% of assessments meeting the 90% criteria. Trend status is Not assessed.		The status of PAHs is Good in the Irish West Coast based on 97.8% of assessments meeting the 90% criteria. Trend status is Improving.																														The status of HBCDD is Good in the Irish West Coast based on 100% of assessments meeting the 90% criteria. Trend status is Unknown.				The status of Mercury and its compounds is Good in the Irish West Coast based on 90.5% of assessments meeting the 90% criteria. Trend status is Not assessed.	The status of Mercury and its compounds is Good in the Irish West Coast based on 90.5% of assessments meeting the 90% criteria. Trend status is Not assessed.	The status of Mercury and its compounds is Good in the Irish West Coast based on 90.5% of assessments meeting the 90% criteria. Trend status is Not assessed.	The status of PAHs is Good in the Irish West Coast based on 100% of assessments meeting the 90% criteria. Trend status is Stable.	The status of PBDEs is Good in the Irish West Coast based on 95.5% of assessments meeting the 90% criteria. Trend status is Not assessed.															The status of PFOS is Good in the Irish West Coast based on 91.7% of assessments meeting the 90% criteria. Trend status is Unknown.	The status of PCBs is Good in the Irish West Coast based on 98.4% of assessments meeting the 90% criteria. Trend status is Improving.	The status of TBT is Not good in the Irish West Coast based on 86.7% of assessments meeting the 90% criteria. Trend status is Unknown.	The status of TBT is Not good in the Irish West Coast based on 86.7% of assessments meeting the 90% criteria. Trend status is Unknown.	The status of TBT is Not good in the Irish West Coast based on 86.7% of assessments meeting the 90% criteria. Trend status is Unknown.	The status of Imposex is Good in the Irish West Coast based on 95.8% of assessments meeting the 90% criteria. Trend status is Improving.
Element status	Not relevant																		Not relevant	Not relevant											Not relevant							Not relevant	Not relevant				Not relevant	Not relevant		Not relevant																														Not relevant				Not relevant	Not relevant	Not relevant	Not relevant	Not relevant															Not relevant	Not relevant	Not relevant	Not relevant	Not relevant
Description element	A total of 95.8% of assessments for Imposex in the Irish West Coast was obtained relative to a 90% threshold.The trend is Improving																		A total of 100% of assessments for Cadmium and its compounds in the Irish West Coast was obtained relative to a 90% threshold.The trend is Improving	A total of 100% of assessments for Cadmium and its compounds in the Irish West Coast was obtained relative to a 90% threshold.The trend is Improving											A total of 100% of assessments for Environmental UPBT contaminants - WFD UPBT substances in the Irish West Coast was obtained relative to a 90% threshold.The trend is Not assessed							A total of 92.9% of assessments for Lead and its compounds in the Irish West Coast was obtained relative to a 90% threshold.The trend is Improving	A total of 92.9% of assessments for Lead and its compounds in the Irish West Coast was obtained relative to a 90% threshold.The trend is Improving				A total of 100% of assessments for Nickel and its compounds in the Irish West Coast was obtained relative to a 90% threshold.The trend is Not assessed	A total of 100% of assessments for Nickel and its compounds in the Irish West Coast was obtained relative to a 90% threshold.The trend is Not assessed		A total of 97.8% of assessments for PAH in the Irish West Coast was obtained relative to a 90% threshold.The trend is Improving																														A total of 100% of assessments for HBCDD in the Irish West Coast was obtained relative to a 90% threshold.The trend is Not assessed				A total of 90.5% of assessments for Mercury and its compounds in the Irish West Coast was obtained relative to a 90% threshold.The trend is Not assessed	A total of 90.5% of assessments for Mercury and its compounds in the Irish West Coast was obtained relative to a 90% threshold.The trend is Not assessed	A total of 90.5% of assessments for Mercury and its compounds in the Irish West Coast was obtained relative to a 90% threshold.The trend is Not assessed	100% of assessments of PAH in the Irish West Coast met with the 90% threshold value. Trends were Stable	95.5% of assessments of PBDE in the Irish West Coast met with the 90% threshold value. Trends were Not assessed															A total of 100% of assessments for PFOS in the Irish West Coast was obtained relative to a 90% threshold.The trend is Not assessed	A total of 98.4% of assessments for Polychlorinated biphenyls (7 PCB: 28,52,101,118,138,153,180) in the Irish West Coast was obtained relative to a 90% threshold.The trend is Improving	A total of 86.7% of assessments for TBT in the Irish West Coast was obtained relative to a 90% threshold.The trend is Not assessed	A total of 86.7% of assessments for TBT in the Irish West Coast was obtained relative to a 90% threshold.The trend is Not assessed	A total of 86.7% of assessments for TBT in the Irish West Coast was obtained relative to a 90% threshold.The trend is Not assessed
Source assessment feature	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD	National OSPAR WaterFD
Reporting method feature	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C	Type C
Trend feature	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed
Integration rule type parameter	Other	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	OOAO_HIE	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.	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. Sampling occurs in coastal WFD areas.
Integration rule type criteria
Integration rule description criteria
GES extent threshold
GES extent achieved	86.70	92.90	92.90	92.90	92.90	92.90	92.90	92.90	92.90	92.90	92.90	92.90	92.90	92.90	92.90	92.90	92.90	92.90	92.90	92.90	92.90	92.90	92.90	92.90	92.90	92.90	92.90	92.90	92.90	92.90	92.90	92.90	92.90	92.90	92.90	92.90	92.90	92.90	92.90	92.90	92.90	92.90	92.90	92.90	92.90	92.90	92.90	92.90	92.90	92.90	92.90	92.90	92.90	92.90	92.90	92.90	92.90	86.70	86.70	86.70	86.70	86.70	86.70	86.70	86.70	86.70	86.70	86.70	86.70	86.70	86.70	86.70	86.70	86.70	86.70	86.70	86.70	86.70	86.70	86.70	86.70	86.70	86.70	86.70	86.70	86.70	86.70	86.70	86.70	86.70	86.70	86.70	86.70	86.70	86.70	86.70	86.70	86.70	86.70	86.70	86.70	86.70	86.70
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	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	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed
Description overall status	UPBT concentrations in water, sediments and biota in the West Coast are mostly in GES. Legacy issues persist for TBT in this area where discreet failures for sediment were present. GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish west coast are in GES.GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish west coast are in GES.GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish west coast are in GES.GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish west coast are in GES.GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish west coast are in GES.GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish west coast are in GES.GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish west coast are in GES.GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish west coast are in GES.GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish west coast are in GES.GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish west coast are in GES.GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish west coast are in GES.GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish west coast are in GES.GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish west coast are in GES.GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish west coast are in GES.GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish west coast are in GES.GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish west coast are in GES.GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish west coast are in GES.GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish west coast are in GES.GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish west coast are in GES.GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish west coast are in GES.GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish west coast are in GES.GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish west coast are in GES.GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish west coast are in GES.GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish west coast are in GES.GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish west coast are in GES.GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish west coast are in GES.GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish west coast are in GES.GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish west coast are in GES.GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish west coast are in GES.GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish west coast are in GES.GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish west coast are in GES.GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish west coast are in GES.GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish west coast are in GES.GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish west coast are in GES.GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish west coast are in GES.GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish west coast are in GES.GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish west coast are in GES.GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish west coast are in GES.GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish west coast are in GES.GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish west coast are in GES.GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish west coast are in GES.GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish west coast are in GES.GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish west coast are in GES.GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish west coast are in GES.GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish west coast are in GES.GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish west coast are in GES.GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish west coast are in GES.GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish west coast are in GES.GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish west coast are in GES.GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish west coast are in GES.GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish west coast are in GES.GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish west coast are in GES.GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish west coast are in GES.GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish west coast are in GES.GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish west coast are in GES.GES extent thresholds have not been defined at a regional or EU level.	Non-UPBT concentrations in water and sediments in the Irish west coast are in GES.GES extent thresholds have not been defined at a regional or EU level.	UPBT concentrations in water, sediments and biota in the West Coast are mostly in GES. Legacy issues persist for TBT in this area where discreet failures for sediment were present. GES extent thresholds have not been defined at a regional or EU level.	UPBT concentrations in water, sediments and biota in the West Coast are mostly in GES. Legacy issues persist for TBT in this area where discreet failures for sediment were present. GES extent thresholds have not been defined at a regional or EU level.	UPBT concentrations in water, sediments and biota in the West Coast are mostly in GES. Legacy issues persist for TBT in this area where discreet failures for sediment were present. GES extent thresholds have not been defined at a regional or EU level.	UPBT concentrations in water, sediments and biota in the West Coast are mostly in GES. Legacy issues persist for TBT in this area where discreet failures for sediment were present. GES extent thresholds have not been defined at a regional or EU level.	UPBT concentrations in water, sediments and biota in the West Coast are mostly in GES. Legacy issues persist for TBT in this area where discreet failures for sediment were present. GES extent thresholds have not been defined at a regional or EU level.	UPBT concentrations in water, sediments and biota in the West Coast are mostly in GES. Legacy issues persist for TBT in this area where discreet failures for sediment were present. GES extent thresholds have not been defined at a regional or EU level.	UPBT concentrations in water, sediments and biota in the West Coast are mostly in GES. Legacy issues persist for TBT in this area where discreet failures for sediment were present. GES extent thresholds have not been defined at a regional or EU level.	UPBT concentrations in water, sediments and biota in the West Coast are mostly in GES. Legacy issues persist for TBT in this area where discreet failures for sediment were present. GES extent thresholds have not been defined at a regional or EU level.	UPBT concentrations in water, sediments and biota in the West Coast are mostly in GES. Legacy issues persist for TBT in this area where discreet failures for sediment were present. GES extent thresholds have not been defined at a regional or EU level.	UPBT concentrations in water, sediments and biota in the West Coast are mostly in GES. Legacy issues persist for TBT in this area where discreet failures for sediment were present. GES extent thresholds have not been defined at a regional or EU level.	UPBT concentrations in water, sediments and biota in the West Coast are mostly in GES. Legacy issues persist for TBT in this area where discreet failures for sediment were present. GES extent thresholds have not been defined at a regional or EU level.	UPBT concentrations in water, sediments and biota in the West Coast are mostly in GES. Legacy issues persist for TBT in this area where discreet failures for sediment were present. GES extent thresholds have not been defined at a regional or EU level.	UPBT concentrations in water, sediments and biota in the West Coast are mostly in GES. Legacy issues persist for TBT in this area where discreet failures for sediment were present. GES extent thresholds have not been defined at a regional or EU level.	UPBT concentrations in water, sediments and biota in the West Coast are mostly in GES. Legacy issues persist for TBT in this area where discreet failures for sediment were present. GES extent thresholds have not been defined at a regional or EU level.	UPBT concentrations in water, sediments and biota in the West Coast are mostly in GES. Legacy issues persist for TBT in this area where discreet failures for sediment were present. GES extent thresholds have not been defined at a regional or EU level.	UPBT concentrations in water, sediments and biota in the West Coast are mostly in GES. Legacy issues persist for TBT in this area where discreet failures for sediment were present. GES extent thresholds have not been defined at a regional or EU level.	UPBT concentrations in water, sediments and biota in the West Coast are mostly in GES. Legacy issues persist for TBT in this area where discreet failures for sediment were present. GES extent thresholds have not been defined at a regional or EU level.	UPBT concentrations in water, sediments and biota in the West Coast are mostly in GES. Legacy issues persist for TBT in this area where discreet failures for sediment were present. GES extent thresholds have not been defined at a regional or EU level.	UPBT concentrations in water, sediments and biota in the West Coast are mostly in GES. Legacy issues persist for TBT in this area where discreet failures for sediment were present. GES extent thresholds have not been defined at a regional or EU level.	UPBT concentrations in water, sediments and biota in the West Coast are mostly in GES. Legacy issues persist for TBT in this area where discreet failures for sediment were present. GES extent thresholds have not been defined at a regional or EU level.	UPBT concentrations in water, sediments and biota in the West Coast are mostly in GES. Legacy issues persist for TBT in this area where discreet failures for sediment were present. GES extent thresholds have not been defined at a regional or EU level.	UPBT concentrations in water, sediments and biota in the West Coast are mostly in GES. Legacy issues persist for TBT in this area where discreet failures for sediment were present. GES extent thresholds have not been defined at a regional or EU level.	UPBT concentrations in water, sediments and biota in the West Coast are mostly in GES. Legacy issues persist for TBT in this area where discreet failures for sediment were present. GES extent thresholds have not been defined at a regional or EU level.	UPBT concentrations in water, sediments and biota in the West Coast are mostly in GES. Legacy issues persist for TBT in this area where discreet failures for sediment were present. GES extent thresholds have not been defined at a regional or EU level.	UPBT concentrations in water, sediments and biota in the West Coast are mostly in GES. Legacy issues persist for TBT in this area where discreet failures for sediment were present. GES extent thresholds have not been defined at a regional or EU level.	UPBT concentrations in water, sediments and biota in the West Coast are mostly in GES. Legacy issues persist for TBT in this area where discreet failures for sediment were present. GES extent thresholds have not been defined at a regional or EU level.	UPBT concentrations in water, sediments and biota in the West Coast are mostly in GES. Legacy issues persist for TBT in this area where discreet failures for sediment were present. GES extent thresholds have not been defined at a regional or EU level.	UPBT concentrations in water, sediments and biota in the West Coast are mostly in GES. Legacy issues persist for TBT in this area where discreet failures for sediment were present. GES extent thresholds have not been defined at a regional or EU level.	UPBT concentrations in water, sediments and biota in the West Coast are mostly in GES. Legacy issues persist for TBT in this area where discreet failures for sediment were present. GES extent thresholds have not been defined at a regional or EU level.	UPBT concentrations in water, sediments and biota in the West Coast are mostly in GES. Legacy issues persist for TBT in this area where discreet failures for sediment were present. GES extent thresholds have not been defined at a regional or EU level.	UPBT concentrations in water, sediments and biota in the West Coast are mostly in GES. Legacy issues persist for TBT in this area where discreet failures for sediment were present. GES extent thresholds have not been defined at a regional or EU level.	UPBT concentrations in water, sediments and biota in the West Coast are mostly in GES. Legacy issues persist for TBT in this area where discreet failures for sediment were present. GES extent thresholds have not been defined at a regional or EU level.	UPBT concentrations in water, sediments and biota in the West Coast are mostly in GES. Legacy issues persist for TBT in this area where discreet failures for sediment were present. GES extent thresholds have not been defined at a regional or EU level.	UPBT concentrations in water, sediments and biota in the West Coast are mostly in GES. Legacy issues persist for TBT in this area where discreet failures for sediment were present. GES extent thresholds have not been defined at a regional or EU level.	UPBT concentrations in water, sediments and biota in the West Coast are mostly in GES. Legacy issues persist for TBT in this area where discreet failures for sediment were present. GES extent thresholds have not been defined at a regional or EU level.	UPBT concentrations in water, sediments and biota in the West Coast are mostly in GES. Legacy issues persist for TBT in this area where discreet failures for sediment were present. GES extent thresholds have not been defined at a regional or EU level.	UPBT concentrations in water, sediments and biota in the West Coast are mostly in GES. Legacy issues persist for TBT in this area where discreet failures for sediment were present. GES extent thresholds have not been defined at a regional or EU level.	UPBT concentrations in water, sediments and biota in the West Coast are mostly in GES. Legacy issues persist for TBT in this area where discreet failures for sediment were present. GES extent thresholds have not been defined at a regional or EU level.	UPBT concentrations in water, sediments and biota in the West Coast are mostly in GES. Legacy issues persist for TBT in this area where discreet failures for sediment were present. GES extent thresholds have not been defined at a regional or EU level.	UPBT concentrations in water, sediments and biota in the West Coast are mostly in GES. Legacy issues persist for TBT in this area where discreet failures for sediment were present. GES extent thresholds have not been defined at a regional or EU level.	UPBT concentrations in water, sediments and biota in the West Coast are mostly in GES. Legacy issues persist for TBT in this area where discreet failures for sediment were present. GES extent thresholds have not been defined at a regional or EU level.	UPBT concentrations in water, sediments and biota in the West Coast are mostly in GES. Legacy issues persist for TBT in this area where discreet failures for sediment were present. GES extent thresholds have not been defined at a regional or EU level.	UPBT concentrations in water, sediments and biota in the West Coast are mostly in GES. Legacy issues persist for TBT in this area where discreet failures for sediment were present. GES extent thresholds have not been defined at a regional or EU level.	UPBT concentrations in water, sediments and biota in the West Coast are mostly in GES. Legacy issues persist for TBT in this area where discreet failures for sediment were present. GES extent thresholds have not been defined at a regional or EU level.	UPBT concentrations in water, sediments and biota in the West Coast are mostly in GES. Legacy issues persist for TBT in this area where discreet failures for sediment were present. GES extent thresholds have not been defined at a regional or EU level.	UPBT concentrations in water, sediments and biota in the West Coast are mostly in GES. Legacy issues persist for TBT in this area where discreet failures for sediment were present. GES extent thresholds have not been defined at a regional or EU level.
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	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	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-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018	IE-D8T1a-1-MRU018 IE-D8T1a-MRU018 IE-D8T1b-1-MRU018 IE-D8T1b-MRU018 IE-D8T2-MRU018
Test TV	NA	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	No	No	Yes	Yes	No	No	Yes	NA	Yes	Yes	Yes	Yes	Yes	Yes	No	Yes	Yes	Yes	Yes	No	Yes	Yes	NA	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	No	Yes	No	Yes	Yes	No	Yes	No	Yes	Yes	Yes	NA	NA	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	NA	NA	No	Yes	Yes	NA
Test results	False	Correct	Correct	Correct	Correct	Correct	Correct	False	Correct	Correct	Correct	False	False	False	False	Correct	Correct	Correct	False	Correct	Correct	Correct	False	False	False	Correct	Correct	False	False	Correct	False	False	Correct	Correct	Correct	Correct	Correct	False	Correct	Correct	False	Correct	False	Correct	Correct	False	False	Correct	False	Correct	Correct	Correct	Correct	Correct	Correct	False	False	False	False	Correct	False	Correct	False	Correct	False	False	False	Correct	False	Correct	Correct	False	Correct	False	Correct	Correct	False	Correct	False	False	False	Correct	False	False	Correct	False	Correct	False	Correct	False	Correct	False	False	False	Correct	False	Correct	False	Correct	False	False	False	Correct	Correct	False