MS/Art8/2018/D8/Germany/NE Atlantic: Greater North Sea — Marine Information System for Europe

Member State report / Art8 / 2018 / D8 / Germany / NE Atlantic: Greater North Sea

Report type	Member State report to Commission
MSFD Article	Art. 8 Initial assessment (and Art. 17 updates)
Report due	2018-10-15
GES Descriptor	D8 Contaminants
Member State	Germany
Region/subregion	NE Atlantic: Greater North Sea
Reported by	Bundesministerium für Umwelt, Naturschutz und nukleare Sicherheit
Report date	2020-02-17
Report access	DE_ART8_GES.xml

Kuestengewaesser Nordsee (ANSDE_CW)

Simplified table

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
Feature	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 - 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	Marine species
Element	1,2,4,5-Tetrachlorobenzene	1,2-Dichlorobenzene	1,3-Dichlorobenzene	1,4-Dichlorobenzene	Aldrin	Aniline	Arsenic and its compounds	Bentazone	Bromoxynil	Cadmium and its compounds	Cadmium and its compounds	Cadmium and its compounds	Cesium-137	Cesium-137	Chlordane	Chloridazon	Chlorobenzene	Chlorpyrifos	Chromium and its compounds	Copper and its compounds	DDT, p,p'	Diazinon	Dibutyltin ion	Dibutyltin ion	Dieldrin	Diflufenican	Endosulfan	Endrin	Epoxiconazole	Free cyanide	Hexachlorobenzene	Hexachlorobenzene	Hexachlorobutadiene	Hexachlorobutadiene	Hexachlorocyclohexane	Hexachloroethane	Isodrin	Isoproturon	Lead and its compounds	Lead and its compounds	Lead and its compounds	MCPA	Mecoprop	Metolachlor	Metribuzin	Nickel and its compounds	Pentachlorobenzene	Phenanthrene	Picolinafen	Pirimicarb	Polychlorinated biphenyls (7 PCB: 28,52,101,118,138,153,180)	Polychlorinated biphenyls (7 PCB: 28,52,101,118,138,153,180)	Polychlorinated biphenyls (7 PCB: 28,52,101,118,138,153,180)	Propiconazole	Tetrabutyltin	Tetrabutyltin	Total DDT (DDT, p,p' + DDT, o,p' + DDE, p,p' + DDD, p,p')	Trichlorobenzenes (all isomers)	Trifluralin	Triphenyltin and compounds	Triphenyltin and compounds	Zinc and its compounds	Brominated diphenylethers (congener numbers 28, 47, 99, 100, 153 and 154)	Brominated diphenylethers (congener numbers 28, 47, 99, 100, 153 and 154)	Brominated diphenylethers (congener numbers 28, 47, 99, 100, 153 and 154)	Heptachlor	Heptachlor epoxide	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Total PAHs (Benzo(a)pyrene, Benzo(b)fluoranthene, Benzo(k)fluoranthene, Benzo(ghi)perylene, Indeno(1,2,3-cd)pyrene)	Total PAHs (Benzo(a)pyrene, Benzo(b)fluoranthene, Benzo(k)fluoranthene, Benzo(ghi)perylene, Indeno(1,2,3-cd)pyrene)	Total PAHs (Benzo(a)pyrene, Benzo(b)fluoranthene, Benzo(k)fluoranthene, Benzo(ghi)perylene, Indeno(1,2,3-cd)pyrene)	Tributyltin compounds	Tributyltin-cation	Littorina littorea
Element code	TECB	CAS_95-50-1	CAS_541-73-1	CAS_106-46-7	CAS_309-00-2	ANL	CAS_7440-38-2	CAS_25057-89-0	CAS_1689-84-5	CAS_7440-43-9	CAS_7440-43-9	CAS_7440-43-9	CS002370	CS002370	CAS_57-74-9	CAS_1698-60-8	CAS_108-90-7	CAS_2921-88-2	CAS_7440-47-3	CAS_7440-50-8	CAS_50-29-3	CAS_333-41-5	DBSN+	DBSN+	CAS_60-57-1	CAS_83164-33-4	CAS_115-29-7	CAS_72-20-8	CAS_133855-98-8	CAS_57-12-5	CAS_118-74-1	CAS_118-74-1	CAS_87-68-3	CAS_87-68-3	CAS_608-73-1	HCE	CAS_465-73-6	CAS_34123-59-6	CAS_7439-92-1	CAS_7439-92-1	CAS_7439-92-1	CAS_94-74-6	CAS_7085-19-0	CAS_51218-45-2	CAS_21087-64-9	CAS_7440-02-0	CAS_608-93-5	CAS_85-01-8	CAS_137641-05-5	CAS_23103-98-2	EEA_33-38-5	EEA_33-38-5	EEA_33-38-5	CAS_60207-90-1	CAS_1461-25-2	CAS_1461-25-2	EEA_32-03-1	CAS_12002-48-1	CAS_1582-09-8	EEA_33-61-4	EEA_33-61-4	CAS_7440-66-6	EEA_32-04-2	EEA_32-04-2	EEA_32-04-2	CAS_76-44-8	CAS_1024-57-3	CAS_7439-97-6	CAS_7439-97-6	CAS_7439-97-6	EEA_33-56-7	EEA_33-56-7	EEA_33-56-7	TBTIN	CAS_36643-28-4	140262
Element code source	Contaminants (D8-D9) http://vocab.ices.dk/?ref=37	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Contaminants (D8-D9) http://vocab.ices.dk/?ref=37	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Contaminants (D8-D9) http://seadatanet.maris2.nl/v_bodc_vocab_v2/vocab_relations.asp?lib=P02	Contaminants (D8-D9) http://seadatanet.maris2.nl/v_bodc_vocab_v2/vocab_relations.asp?lib=P02	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Contaminants (D8-D9) http://vocab.ices.dk/?ref=37	Contaminants (D8-D9) http://vocab.ices.dk/?ref=37	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Contaminants (D8-D9) http://vocab.ices.dk/?ref=37	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Contaminants (D8-D9) http://vocab.ices.dk/?ref=37	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Species (D1) http://www.marinespecies.org/
Element 2
Element 2 code
Element 2 code source
Element source	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	Other	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	OSPAR
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	D8C2
Parameter	Concentration in water	Concentration in water	Concentration in water	Concentration in water	Concentration in water	Concentration in water	Concentration in sediment	Concentration in water	Concentration in water	Concentration in biota	Concentration in sediment	Concentration in water	Concentration in biota	Concentration in water	Concentration in water	Concentration in water	Concentration in water	Concentration in water	Concentration in sediment	Concentration in sediment	Concentration in water	Concentration in water	Concentration in sediment	Concentration in water	Concentration in water	Concentration in water	Concentration in water	Concentration in water	Concentration in water	Concentration in water	Concentration in sediment	Concentration in water	Concentration in sediment	Concentration in water	Concentration in water	Concentration in water	Concentration in water	Concentration in water	Concentration in biota	Concentration in sediment	Concentration in water	Concentration in water	Concentration in water	Concentration in water	Concentration in water	Concentration in water	Concentration in water	Concentration in water	Concentration in water	Concentration in water	Concentration in biota	Concentration in sediment	Concentration in water	Concentration in water	Concentration in sediment	Concentration in water	Concentration in water	Concentration in water	Concentration in water	Concentration in sediment	Concentration in water	Concentration in sediment	Concentration in biota	Concentration in sediment	Concentration in water	Concentration in water	Concentration in water	Concentration in biota	Concentration in sediment	Concentration in water	Concentration in biota	Concentration in sediment	Concentration in water	Concentration in sediment	Concentration in water	Other
Parameter other																																																																												VAS defens Sequence Index (VDS)
Threshold value upper													0.159																																																							20.0
Threshold value lower
Threshold qualitative
Threshold value source	Other (specify)	Other (specify)	Other (specify)	Other (specify)	Other (specify)	Other (specify)	Other (specify)	Other (specify)	Other (specify)	OSPAR Convention	OSPAR Convention	Other (specify)	Other (specify)	Other (specify)	Other (specify)	Other (specify)	Other (specify)	Other (specify)	Other (specify)	Other (specify)	Other (specify)	Other (specify)	Other (specify)	Other (specify)	Other (specify)	Other (specify)	Other (specify)	Other (specify)	Other (specify)	Other (specify)	Other (specify)	Other (specify)	Other (specify)	Other (specify)	Other (specify)	Other (specify)	Other (specify)	Other (specify)	OSPAR Convention	OSPAR Convention	Other (specify)	Other (specify)	Other (specify)	Other (specify)	Other (specify)	Other (specify)	Other (specify)	Other (specify)	Other (specify)	Other (specify)	OSPAR Convention	OSPAR Convention	Other (specify)	Other (specify)	Other (specify)	Other (specify)	Other (specify)	Other (specify)	Other (specify)	Other (specify)	Other (specify)	Other (specify)			Other (specify)	Other (specify)	Other (specify)	Other (specify)	OSPAR Convention	Other (specify)	OSPAR Convention	OSPAR Convention	Other (specify)		Other (specify)	OSPAR Convention
Threshold value source other	EQS, OesterV, 2011,...	EQS, OesterV, 2011,...	EQS, OesterV, 2011,...	EQS, OesterV, 2011,...	EQS, OesterV, 2011, Annex 7	EQS, OesterV, 2011,...	EQS, OesterV, 2011,...	EQS, OesterV, 2011,...	EQS, OesterV, 2011,...			EQS, OesterV, 2011, Annex 7	National	National	EQS, OesterV, 2011,...	EQS, OesterV, 2011,...	EQS, OesterV, 2011,...	EQS, OesterV, 2011, Annex 7	EQS, OesterV, 2011,...	EQS, OesterV, 2011,...	EQS, OesterV, 2011, Annex 7	EQS, OesterV, 2011,...	EQS, OesterV, 2011,...	EQS, OesterV, 2011,...	EQS, OesterV, 2011, Annex 7	EQS, OesterV, 2011,...	EQS, OesterV, 2011, Annex 7	EQS, OesterV, 2011, Annex 7	EQS, OesterV, 2011,...	EQS, OesterV, 2011,...	EQS, OesterV, 2011, Annex 7	EQS, OesterV, 2011, Annex 7	EQS, OesterV, 2011, Annex 7	EQS, OesterV, 2011, Annex 7	EQS, OesterV, 2011, Annex 7	EQS, OesterV, 2011,...	EQS, OesterV, 2011, Annex 7	EQS, OesterV, 2011, Annex 7			EQS, OesterV, 2011, Annex 7	EQS, OesterV, 2011,...	EQS, OesterV, 2011,...	EQS, OesterV, 2011,...	EQS, OesterV, 2011,...	EQS, OesterV, 2011, Annex 7	EQS, OesterV, 2011, Annex 7	EQS, OesterV, 2011,...	EQS, OesterV, 2011,...	EQS, OesterV, 2011,...			EQS, OesterV, 2011,...	EQS, OesterV, 2011,...	EQS, OesterV, 2011,...	EQS, OesterV, 2011,...	EQS, OesterV, 2011, Annex 7	EQS, OesterV, 2011, Annex 7	EQS, OesterV, 2011, Annex 7	EQS, OesterV, 2011,...	EQS, OesterV, 2011,...	EQS, OesterV, 2011,...			EQS, OesterV, 2011, Annex 7	EQS, OesterV, 2011,...	EQS, OesterV, 2011,...	EQS, OesterV, 2011, Annex 7		EQS, OesterV, 2011, Annex 7			EQS, OesterV, 2011, Annex 7		EQS, OesterV, 2011, Annex 7
Value achieved upper																																																																				99.0
Value achieved lower																																																																				70.5
Value unit													Other
Value unit other													Bq/kg WW
Proportion threshold value
Proportion value achieved
Proportion threshold value unit
Trend	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Improving	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Improving	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Improving	Unknown	Improving
Parameter achieved	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Not assessed	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	No	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	No	No	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Not assessed	Not assessed	Yes	Yes	Yes	No	No	Yes	Yes	Yes	No	Not assessed	Yes	Yes
Description parameter	The assessment was carried out on the basis of the WFD management plans for 2015 (http://wasserblick.net/servlet/is/148547/). The trend has not been assessed.	The assessment was carried out on the basis of the WFD management plans for 2015 (http://wasserblick.net/servlet/is/148547/). The trend has not been assessed.	The assessment was carried out on the basis of the WFD management plans for 2015 (http://wasserblick.net/servlet/is/148547/). The trend has not been assessed.	The assessment was carried out on the basis of the WFD management plans for 2015 (http://wasserblick.net/servlet/is/148547/). The trend has not been assessed.	The assessment was carried out on the basis of the WFD management plans for 2015 (http://wasserblick.net/servlet/is/148547/). The trend has not been assessed.	The assessment was carried out on the basis of the WFD management plans for 2015 (http://wasserblick.net/servlet/is/148547/). The trend has not been assessed.	The assessment was carried out on the basis of the WFD management plans for 2015 (http://wasserblick.net/servlet/is/148547/). The trend has not been assessed.	The assessment was carried out on the basis of the WFD management plans for 2015 (http://wasserblick.net/servlet/is/148547/). The trend has not been assessed.	The assessment was carried out on the basis of the WFD management plans for 2015 (http://wasserblick.net/servlet/is/148547/). The trend has not been assessed.			The assessment was carried out on the basis of the WFD management plans for 2015 (http://wasserblick.net/servlet/is/148547/). The trend has not been assessed.	The trend was...	Threshold not yet agreed. (Federal Ministry for the Environment, Nature Conservation, Building and Nuclear Safety, Environmental Radioactivity and Radiation Pollution. 2015 Annual Report. http://nbn-resolving.de/urn:nbn:de:0221-2017072814305)	The assessment was carried out on the basis of the WFD management plans for 2015 (http://wasserblick.net/servlet/is/148547/). The trend has not been assessed.	The assessment was carried out on the basis of the WFD management plans for 2015 (http://wasserblick.net/servlet/is/148547/). The trend has not been assessed.	The assessment was carried out on the basis of the WFD management plans for 2015 (http://wasserblick.net/servlet/is/148547/). The trend has not been assessed.	The assessment was carried out on the basis of the WFD management plans for 2015 (http://wasserblick.net/servlet/is/148547/). The trend has not been assessed.	The assessment was carried out on the basis of the WFD management plans for 2015 (http://wasserblick.net/servlet/is/148547/). The trend has not been assessed.	The assessment was carried out on the basis of the WFD management plans for 2015 (http://wasserblick.net/servlet/is/148547/). The trend has not been assessed.	The assessment was carried out on the basis of the WFD management plans for 2015 (http://wasserblick.net/servlet/is/148547/). The trend has not been assessed.	The assessment was carried out on the basis of the WFD management plans for 2015 (http://wasserblick.net/servlet/is/148547/). The trend has not been assessed.	The assessment was carried out on the basis of the WFD management plans for 2015 (http://wasserblick.net/servlet/is/148547/). The trend has not been assessed.	The assessment was carried out on the basis of the WFD management plans for 2015 (http://wasserblick.net/servlet/is/148547/). The trend has not been assessed.	The assessment was carried out on the basis of the WFD management plans for 2015 (http://wasserblick.net/servlet/is/148547/). The trend has not been assessed.	The assessment was carried out on the basis of the WFD management plans for 2015 (http://wasserblick.net/servlet/is/148547/). The trend has not been assessed.	The assessment was carried out on the basis of the WFD management plans for 2015 (http://wasserblick.net/servlet/is/148547/). The trend has not been assessed.	The assessment was carried out on the basis of the WFD management plans for 2015 (http://wasserblick.net/servlet/is/148547/). The trend has not been assessed.	The assessment was carried out on the basis of the WFD management plans for 2015 (http://wasserblick.net/servlet/is/148547/). The trend has not been assessed.	The assessment was carried out on the basis of the WFD management plans for 2015 (http://wasserblick.net/servlet/is/148547/). The trend has not been assessed.	The assessment was carried out on the basis of the WFD management plans for 2015 (http://wasserblick.net/servlet/is/148547/). The trend has not been assessed.	The assessment was carried out on the basis of the WFD management plans for 2015 (http://wasserblick.net/servlet/is/148547/). The trend has not been assessed.	The assessment was carried out on the basis of the WFD management plans for 2015 (http://wasserblick.net/servlet/is/148547/). The trend has not been assessed.	The assessment was carried out on the basis of the WFD management plans for 2015 (http://wasserblick.net/servlet/is/148547/). The trend has not been assessed.	The assessment was carried out on the basis of the WFD management plans for 2015 (http://wasserblick.net/servlet/is/148547/). The trend has not been assessed.	The assessment was carried out on the basis of the WFD management plans for 2015 (http://wasserblick.net/servlet/is/148547/). The trend has not been assessed.	The assessment was carried out on the basis of the WFD management plans for 2015 (http://wasserblick.net/servlet/is/148547/). The trend has not been assessed.	The assessment was carried out on the basis of the WFD management plans for 2015 (http://wasserblick.net/servlet/is/148547/). The trend has not been assessed.			The assessment was carried out on the basis of the WFD management plans for 2015 (http://wasserblick.net/servlet/is/148547/). The trend has not been assessed.	The assessment was carried out on the basis of the WFD management plans for 2015 (http://wasserblick.net/servlet/is/148547/). The trend has not been assessed.	The assessment was carried out on the basis of the WFD management plans for 2015 (http://wasserblick.net/servlet/is/148547/). The trend has not been assessed.	The assessment was carried out on the basis of the WFD management plans for 2015 (http://wasserblick.net/servlet/is/148547/). The trend has not been assessed.	The assessment was carried out on the basis of the WFD management plans for 2015 (http://wasserblick.net/servlet/is/148547/). The trend has not been assessed.	The assessment was carried out on the basis of the WFD management plans for 2015 (http://wasserblick.net/servlet/is/148547/). The trend has not been assessed.	The assessment was carried out on the basis of the WFD management plans for 2015 (http://wasserblick.net/servlet/is/148547/). The trend has not been assessed.	The assessment was carried out on the basis of the WFD management plans for 2015 (http://wasserblick.net/servlet/is/148547/). The trend has not been assessed.	The assessment was carried out on the basis of the WFD management plans for 2015 (http://wasserblick.net/servlet/is/148547/). The trend has not been assessed.	The assessment was carried out on the basis of the WFD management plans for 2015 (http://wasserblick.net/servlet/is/148547/). The trend has not been assessed.	PCB-118	PCB-118	The assessment was carried out on the basis of the WFD management plans for 2015 (http://wasserblick.net/servlet/is/148547/). The trend has not been assessed.	The assessment was carried out on the basis of the WFD management plans for 2015 (http://wasserblick.net/servlet/is/148547/). The trend has not been assessed.	The assessment was carried out on the basis of the WFD management plans for 2015 (http://wasserblick.net/servlet/is/148547/). The trend has not been assessed.	The assessment was carried out on the basis of the WFD management plans for 2015 (http://wasserblick.net/servlet/is/148547/). The trend has not been assessed.	The assessment was carried out on the basis of the WFD management plans for 2015 (http://wasserblick.net/servlet/is/148547/). The trend has not been assessed.	The assessment was carried out on the basis of the WFD management plans for 2015 (http://wasserblick.net/servlet/is/148547/). The trend has not been assessed.	The assessment was carried out on the basis of the WFD management plans for 2015 (http://wasserblick.net/servlet/is/148547/). The trend has not been assessed.	The assessment was carried out on the basis of the WFD management plans for 2015 (http://wasserblick.net/servlet/is/148547/). The trend has not been assessed.	The assessment was carried out on the basis of the WFD management plans for 2015 (http://wasserblick.net/servlet/is/148547/). The trend has not been assessed.	The assessment was carried out on the basis of the WFD management plans for 2015 (http://wasserblick.net/servlet/is/148547/). The trend has not been assessed.	Threshold not yet regionalised. OSPAR Convention	Threshold not yet regionalised. OSPAR Convention	The assessment was carried out on the basis of the WFD management plans for 2015 (http://wasserblick.net/servlet/is/148547/). The trend has not been assessed.	The assessment was carried out on the basis of the WFD management plans for 2015 (http://wasserblick.net/servlet/is/148547/). The trend has not been assessed.	The assessment was carried out on the basis of the WFD management plans for 2015 (http://wasserblick.net/servlet/is/148547/). The trend has not been assessed.	For mercury, the assessment in biota (dab and flounder) with the EQS of 20 μg/kg wet weight takes place. The tests showed significant overshootings in the EQS. The concentrations in the coastal waters of Lower Saxony are between 70,5 and 93 μg/kg (median values 2013-2015), depending on the monitoring station, and in the area of the coastal waters of Schleswig-Holstein Eider between 92,7 and 99 μg/kg wet weight (median values 2011-2012).		The assessment was carried out on the basis of the WFD management plans for 2015 (http://wasserblick.net/servlet/is/148547/). The trend has not been assessed.	The trend has not been assessed.	The trend has not been assessed.	The assessment was carried out on the basis of the WFD management plans for 2015 (http://wasserblick.net/servlet/is/148547/). The trend has not been assessed.	Threshold not yet regionalised. OSPAR Convention	The assessment was carried out on the basis of the WFD management plans for 2015 (http://wasserblick.net/servlet/is/148547/). The trend has not been assessed.
Related indicator										Status and Trend for Heavy Metals (Mercury, Cadmium, and Lead) in Fish and Shellfish	Status and Trend for Heavy Metals (Cadmium, Mercury and Lead) in Sediment		Nordsee Caesium-137	Nordsee Caesium-137																									Status and Trend for Heavy Metals (Mercury, Cadmium, and Lead) in Fish and Shellfish	Status and Trend for Heavy Metals (Cadmium, Mercury and Lead) in Sediment											Status and Trends of Polychlorinated Biphenyls (PCB) in Fish and Shellfish	Status and Trends of Polychlorinated Biphenyls (PCB) in Sediment											Trends in Concentrations of Polybrominated Diphenyl Ethers (PBDEs) in Fish and Shellfish	Trends in Concentrations of Polybrominated Diphenyl Ethers (PBDEs) in Sediments					Status and Trend for Heavy Metals (Cadmium, Mercury and Lead) in Sediment		Status and Trends in the Concentrations of Polycyclic Aromatic Hydrocarbons (PAHs) in Shellfish	Status and Trends in the Concentrations of Polycyclic Aromatic Hydrocarbons (PAHs) in Sediment		Trends of Organotin in Sediments in the Southern North Sea		Status and Trends in the Levels of Imposex in Marine Gastropods (TBT in Shellfish)
Criteria status	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Good
Description criteria	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).	Threshold not yet regionalised. The status status is defined by the ?one out?.	Threshold not yet regionalised. The status status is defined by the ?one out?.	Threshold not yet regionalised. The status status is defined by the ?one out?.	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).	Threshold not yet regionalised. The status status is defined by the ?one out?.	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).
Element status	Good	Good	Good	Good	Good	Good	Good	Good	Good	Good	Good	Good	Good	Good	Good	Good	Good	Good	Good	Good	Good	Good	Good	Good	Good	Good	Good	Good	Good	Good	Good	Good	Good	Good	Good	Good	Good	Good	Not good	Not good	Not good	Good	Good	Good	Good	Good	Good	Good	Good	Good	Not good	Not good	Not good	Good	Good	Good	Good	Good	Good	Good	Good	Good	Good	Good	Good	Good	Good	Not good	Not good	Not good	Not good	Not good	Not good	Not assessed	Good	Good
Description element																																																									Source element: EQS, OesterV, 2011, Annex 7
Integration rule type parameter	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO
Integration rule description parameter	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.
Integration rule type criteria	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO
Integration rule description criteria	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.
GES extent threshold
GES extent achieved
GES extent unit
GES achieved	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES achieved
Description overall status	The assessment was carried out on the basis of the WFD management plans for 2015 (reporting period 2007-2012).	The assessment was carried out on the basis of the WFD management plans for 2015 (reporting period 2007-2012).	The assessment was carried out on the basis of the WFD management plans for 2015 (reporting period 2007-2012).	The assessment was carried out on the basis of the WFD management plans for 2015 (reporting period 2007-2012).	The assessment was carried out on the basis of the WFD management plans for 2015 (reporting period 2007-2012).	The assessment was carried out on the basis of the WFD management plans for 2015 (reporting period 2007-2012).	The assessment was carried out on the basis of the WFD management plans for 2015 (reporting period 2007-2012).	The assessment was carried out on the basis of the WFD management plans for 2015 (reporting period 2007-2012).	The assessment was carried out on the basis of the WFD management plans for 2015 (reporting period 2007-2012).	The assessment was carried out on the basis of the WFD management plans for 2015 (reporting period 2007-2012).	The assessment was carried out on the basis of the WFD management plans for 2015 (reporting period 2007-2012).	The assessment was carried out on the basis of the WFD management plans for 2015 (reporting period 2007-2012).	The assessment was carried out on the basis of the WFD management plans for 2015 (reporting period 2007-2012).	The assessment was carried out on the basis of the WFD management plans for 2015 (reporting period 2007-2012).	The assessment was carried out on the basis of the WFD management plans for 2015 (reporting period 2007-2012).	The assessment was carried out on the basis of the WFD management plans for 2015 (reporting period 2007-2012).	The assessment was carried out on the basis of the WFD management plans for 2015 (reporting period 2007-2012).	The assessment was carried out on the basis of the WFD management plans for 2015 (reporting period 2007-2012).	The assessment was carried out on the basis of the WFD management plans for 2015 (reporting period 2007-2012).	The assessment was carried out on the basis of the WFD management plans for 2015 (reporting period 2007-2012).	The assessment was carried out on the basis of the WFD management plans for 2015 (reporting period 2007-2012).	The assessment was carried out on the basis of the WFD management plans for 2015 (reporting period 2007-2012).	The assessment was carried out on the basis of the WFD management plans for 2015 (reporting period 2007-2012).	The assessment was carried out on the basis of the WFD management plans for 2015 (reporting period 2007-2012).	The assessment was carried out on the basis of the WFD management plans for 2015 (reporting period 2007-2012).	The assessment was carried out on the basis of the WFD management plans for 2015 (reporting period 2007-2012).	The assessment was carried out on the basis of the WFD management plans for 2015 (reporting period 2007-2012).	The assessment was carried out on the basis of the WFD management plans for 2015 (reporting period 2007-2012).	The assessment was carried out on the basis of the WFD management plans for 2015 (reporting period 2007-2012).	The assessment was carried out on the basis of the WFD management plans for 2015 (reporting period 2007-2012).	The assessment was carried out on the basis of the WFD management plans for 2015 (reporting period 2007-2012).	The assessment was carried out on the basis of the WFD management plans for 2015 (reporting period 2007-2012).	The assessment was carried out on the basis of the WFD management plans for 2015 (reporting period 2007-2012).	The assessment was carried out on the basis of the WFD management plans for 2015 (reporting period 2007-2012).	The assessment was carried out on the basis of the WFD management plans for 2015 (reporting period 2007-2012).	The assessment was carried out on the basis of the WFD management plans for 2015 (reporting period 2007-2012).	The assessment was carried out on the basis of the WFD management plans for 2015 (reporting period 2007-2012).	The assessment was carried out on the basis of the WFD management plans for 2015 (reporting period 2007-2012).	The assessment was carried out on the basis of the WFD management plans for 2015 (reporting period 2007-2012).	The assessment was carried out on the basis of the WFD management plans for 2015 (reporting period 2007-2012).	The assessment was carried out on the basis of the WFD management plans for 2015 (reporting period 2007-2012).	The assessment was carried out on the basis of the WFD management plans for 2015 (reporting period 2007-2012).	The assessment was carried out on the basis of the WFD management plans for 2015 (reporting period 2007-2012).	The assessment was carried out on the basis of the WFD management plans for 2015 (reporting period 2007-2012).	The assessment was carried out on the basis of the WFD management plans for 2015 (reporting period 2007-2012).	The assessment was carried out on the basis of the WFD management plans for 2015 (reporting period 2007-2012).	The assessment was carried out on the basis of the WFD management plans for 2015 (reporting period 2007-2012).	The assessment was carried out on the basis of the WFD management plans for 2015 (reporting period 2007-2012).	The assessment was carried out on the basis of the WFD management plans for 2015 (reporting period 2007-2012).	The assessment was carried out on the basis of the WFD management plans for 2015 (reporting period 2007-2012).	The assessment was carried out on the basis of the WFD management plans for 2015 (reporting period 2007-2012).	The assessment was carried out on the basis of the WFD management plans for 2015 (reporting period 2007-2012).	The assessment was carried out on the basis of the WFD management plans for 2015 (reporting period 2007-2012).	The assessment was carried out on the basis of the WFD management plans for 2015 (reporting period 2007-2012).	The assessment was carried out on the basis of the WFD management plans for 2015 (reporting period 2007-2012).	The assessment was carried out on the basis of the WFD management plans for 2015 (reporting period 2007-2012).	The assessment was carried out on the basis of the WFD management plans for 2015 (reporting period 2007-2012).	The assessment was carried out on the basis of the WFD management plans for 2015 (reporting period 2007-2012).	The assessment was carried out on the basis of the WFD management plans for 2015 (reporting period 2007-2012).	The assessment was carried out on the basis of the WFD management plans for 2015 (reporting period 2007-2012).	The assessment was carried out on the basis of the WFD management plans for 2015 (reporting period 2007-2012).	The assessment was carried out on the basis of the WFD management plans for 2015 (reporting period 2007-2012).	The assessment was carried out on the basis of the WFD management plans for 2015 (reporting period 2007-2012).	The assessment was carried out on the basis of the WFD management plans for 2015 (reporting period 2007-2012).	The assessment was carried out on the basis of the WFD management plans for 2015 (reporting period 2007-2012).	The assessment was carried out on the basis of the WFD management plans for 2015 (reporting period 2007-2012).	The assessment was carried out on the basis of the WFD management plans for 2015 (reporting period 2007-2012).	The assessment was carried out on the basis of the WFD management plans for 2015 (reporting period 2007-2012).	The assessment was carried out on the basis of the WFD management plans for 2015 (reporting period 2007-2012).	The assessment was carried out on the basis of the WFD management plans for 2015 (reporting period 2007-2012).	The assessment was carried out on the basis of the WFD management plans for 2015 (reporting period 2007-2012).	The assessment was carried out on the basis of the WFD management plans for 2015 (reporting period 2007-2012).	The assessment was carried out on the basis of the WFD management plans for 2015 (reporting period 2007-2012).	The assessment was carried out on the basis of the WFD management plans for 2015 (reporting period 2007-2012).	The assessment was carried out on the basis of the WFD management plans for 2015 (reporting period 2007-2012).
Assessments period	2007-2012	2007-2012	2007-2012	2007-2012	2007-2012	2007-2012	2007-2012	2007-2012	2007-2012	2007-2012	2007-2012	2007-2012	2007-2012	2007-2012	2007-2012	2007-2012	2007-2012	2007-2012	2007-2012	2007-2012	2007-2012	2007-2012	2007-2012	2007-2012	2007-2012	2007-2012	2007-2012	2007-2012	2007-2012	2007-2012	2007-2012	2007-2012	2007-2012	2007-2012	2007-2012	2007-2012	2007-2012	2007-2012	2007-2012	2007-2012	2007-2012	2007-2012	2007-2012	2007-2012	2007-2012	2007-2012	2007-2012	2007-2012	2007-2012	2007-2012	2007-2012	2007-2012	2007-2012	2007-2012	2007-2012	2007-2012	2007-2012	2007-2012	2007-2012	2007-2012	2007-2012	2007-2012	2007-2012	2007-2012	2007-2012	2007-2012	2007-2012	2007-2012	2007-2012	2007-2012	2007-2012	2007-2012	2007-2012	2007-2012	2007-2012	2011-2015
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
Related targets	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5

AWZ deutsche Nordsee (ANSDE_EEZ)

Simplified table

GES component	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8
Feature	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
Element	Cadmium and its compounds	Cadmium and its compounds	Cesium-137	Cesium-137	Lead and its compounds	Lead and its compounds	Polychlorinated biphenyls (7 PCB: 28,52,101,118,138,153,180)	Polychlorinated biphenyls (7 PCB: 28,52,101,118,138,153,180)	Polychlorinated biphenyls (7 PCB: 28,52,101,118,138,153,180)	Brominated diphenylethers (congener numbers 28, 47, 99, 100, 153 and 154)	Mercury and its compounds	Mercury and its compounds	Total PAHs (Benzo(a)pyrene, Benzo(b)fluoranthene, Benzo(k)fluoranthene, Benzo(ghi)perylene, Indeno(1,2,3-cd)pyrene)	Total PAHs (Benzo(a)pyrene, Benzo(b)fluoranthene, Benzo(k)fluoranthene, Benzo(ghi)perylene, Indeno(1,2,3-cd)pyrene)	Tributyltin compounds
Element code	CAS_7440-43-9	CAS_7440-43-9	CS002370	CS002370	CAS_7439-92-1	CAS_7439-92-1	EEA_33-38-5	EEA_33-38-5	EEA_33-38-5	EEA_32-04-2	CAS_7439-97-6	CAS_7439-97-6	EEA_33-56-7	EEA_33-56-7	TBTIN
Element code source	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Contaminants (D8-D9) http://seadatanet.maris2.nl/v_bodc_vocab_v2/vocab_relations.asp?lib=P02	Contaminants (D8-D9) http://seadatanet.maris2.nl/v_bodc_vocab_v2/vocab_relations.asp?lib=P02	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Contaminants (D8-D9) http://vocab.ices.dk/?ref=37
Element 2
Element 2 code
Element 2 code source
Element source	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES
Criterion	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1
Parameter	Concentration in biota	Concentration in sediment	Concentration in biota	Concentration in water	Concentration in biota	Concentration in sediment	Concentration in biota	Concentration in sediment	Concentration in water	Concentration in biota	Concentration in biota	Concentration in sediment	Concentration in biota	Concentration in sediment	Concentration in sediment
Parameter other
Threshold value upper			0.159
Threshold value lower
Threshold qualitative
Threshold value source	OSPAR Convention	OSPAR Convention	Other (specify)	Other (specify)	OSPAR Convention	OSPAR Convention	OSPAR Convention	OSPAR Convention			Other (specify)	OSPAR Convention	OSPAR Convention	OSPAR Convention
Threshold value source other			National	National							EQS, OesterV, 2011, Annex 7
Value achieved upper
Value achieved lower
Value unit			Other
Value unit other			Bq/kg WW
Proportion threshold value
Proportion value achieved
Proportion threshold value unit
Trend	Unknown	Unknown	Unknown	Improving	Unknown	Unknown	Unknown	Unknown	Unknown	Improving	Unknown	Unknown	Unknown	Unknown	Improving
Parameter achieved	Yes	Yes	No	Not assessed	Yes	No	No	No	Not assessed	Not assessed	No	No	Yes	Yes	Not assessed
Description parameter			The trend has not been assessed. The limit value was exceeded. (Federal Ministry for the Environment, Nature Conservation, Building and Nuclear Safety, Environmental Radioactivity and Radiation Pollution 2016 Annual Report, in press)	Threshold not yet agreed. (Federal Ministry for the Environment, Nature Conservation, Building and Nuclear Safety Environmental Radioactivity and Radiation Pollution. 2015 Annual Report?. http://nbn-resolving.de/urn:nbn:de:0221-2017072814305)			PCB-118	PCB-118	The trend has not been assessed. Threshold not yet regionalised.	Threshold not yet regionalised. OSPAR Convention					Threshold not yet regionalised. OSPAR Convention
Related indicator	Status and Trend for Heavy Metals (Mercury, Cadmium, and Lead) in Fish and Shellfish	Status and Trend for Heavy Metals (Cadmium, Mercury and Lead) in Sediment	Nordsee Caesium-137	Nordsee Caesium-137	Status and Trend for Heavy Metals (Mercury, Cadmium, and Lead) in Fish and Shellfish	Status and Trend for Heavy Metals (Cadmium, Mercury and Lead) in Sediment	Status and Trends of Polychlorinated Biphenyls (PCB) in Fish and Shellfish	Status and Trends of Polychlorinated Biphenyls (PCB) in Sediment		Trends in Concentrations of Polybrominated Diphenyl Ethers (PBDEs) in Fish and Shellfish	Status and Trend for Heavy Metals (Mercury, Cadmium, and Lead) in Fish and Shellfish	Status and Trend for Heavy Metals (Cadmium, Mercury and Lead) in Sediment	Status and Trends in the Concentrations of Polycyclic Aromatic Hydrocarbons (PAHs) in Shellfish	Status and Trends in the Concentrations of Polycyclic Aromatic Hydrocarbons (PAHs) in Sediment	Trends of Organotin in Sediments in the Southern North Sea
Criteria status	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good
Description criteria	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).	Threshold not yet regionalised.					Threshold not yet regionalised.
Element status	Good	Good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not assessed	Not good	Not good	Good	Good	Not assessed
Description element
Integration rule type parameter	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO
Integration rule description parameter	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.
Integration rule type criteria	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO
Integration rule description criteria	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.
GES extent threshold
GES extent achieved
GES extent unit
GES achieved	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported
Description overall status	The valuation was carried out after OSPAR Intermediate Interrate Assessment 2017 (reporting period 2011-2015).	The valuation was carried out after OSPAR Intermediate Interrate Assessment 2017 (reporting period 2011-2015).	The valuation was carried out after OSPAR Intermediate Interrate Assessment 2017 (reporting period 2011-2015).	The valuation was carried out after OSPAR Intermediate Interrate Assessment 2017 (reporting period 2011-2015).	The valuation was carried out after OSPAR Intermediate Interrate Assessment 2017 (reporting period 2011-2015).	The valuation was carried out after OSPAR Intermediate Interrate Assessment 2017 (reporting period 2011-2015).	The valuation was carried out after OSPAR Intermediate Interrate Assessment 2017 (reporting period 2011-2015).	The valuation was carried out after OSPAR Intermediate Interrate Assessment 2017 (reporting period 2011-2015).	The valuation was carried out after OSPAR Intermediate Interrate Assessment 2017 (reporting period 2011-2015).	The valuation was carried out after OSPAR Intermediate Interrate Assessment 2017 (reporting period 2011-2015).	The valuation was carried out after OSPAR Intermediate Interrate Assessment 2017 (reporting period 2011-2015).	The valuation was carried out after OSPAR Intermediate Interrate Assessment 2017 (reporting period 2011-2015).	The valuation was carried out after OSPAR Intermediate Interrate Assessment 2017 (reporting period 2011-2015).	The valuation was carried out after OSPAR Intermediate Interrate Assessment 2017 (reporting period 2011-2015).	The valuation was carried out after OSPAR Intermediate Interrate Assessment 2017 (reporting period 2011-2015).
Assessments period	2011-2015	2011-2015	2011-2015	2011-2015	2011-2015	2011-2015	2011-2015	2011-2015	2011-2015	2011-2015	2011-2015	2011-2015	2011-2015	2011-2015	2011-2015
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
Related targets	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5

Deutsche Nordsee (ANSDE_MS)

Simplified table

GES component	D8	D8
Feature	Acute pollution events	Acute pollution events
Element
Element code
Element code source
Element 2
Element 2 code
Element 2 code source
Element source
Criterion	D8C3	D8C4
Parameter	Other	Other
Parameter other	Not specified	Not specified
Threshold value upper
Threshold value lower
Threshold qualitative
Threshold value source
Threshold value source other
Value achieved upper
Value achieved lower
Value unit
Value unit other
Proportion threshold value
Proportion value achieved
Proportion threshold value unit
Trend	Unknown	Unknown
Parameter achieved	Not assessed	Not assessed
Description parameter
Related indicator
Criteria status	Not assessed	Not assessed
Description criteria	Over the reporting period there have been more than 20 reports of damages to the Disaster Control Centre in the German North Sea waters since 2011, of which only two concerned pollutants (landings of paraffin). In the case of the other reports, there has been no release of pollutants and no acute pollution has taken place. This is due, inter alia, to the high level of the precautionary standard and the technical competence to deal with shipwrecks, which have existed since the establishment of the Disaster Control Centre in the Federal Republic of Germany. The partners of the marine pollution response agreement also agreed to take into account water, shore and beach contamination with paraffin, under certain conditions, and thus to be classified as a complex pollution accident although it is not currently listed as a marine pollutant under MARPOL. Paraffin contamination of shores and beaches has repeatedly occurred in the North Sea. However, the risk of damage to the environment caused by paraffin, such as the sticking together of bird plumage, is considered to be very low in the summer due to the solidification of the paraffins in cool North Sea waters (UEG 2014). The duration and spatial extent of acute pollution (criterion D8C3) are already covered by the statistics of the Disaster Control Centre.	D8C4 will only be triggered as secondary criterion when there has been significant acute contamination. The assessment covers the assessment of the status of species and habitats. The application of criterion D8C4 for the assessment of good environmental status for Descriptor 8 shall be decided at regional or sub-regional level in accordance with Commission Decision (EU) 2017/848. Since the beginning of 8, a monitoring plan has been in place to monitor the consequences of pollution accidents under criterion D4C2017, which will be used in the future in the event of complex pollution incidents.
Element status
Description element
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	Not assessed	Not assessed
Description overall status	The methodological standards for the assessment of criterion D8C3 are still to be developed at EU and regional or sub-regional level. D8C4 will only be triggered as secondary criterion when there has been significant acute contamination.	The methodological standards for the assessment of criterion D8C3 are still to be developed at EU and regional or sub-regional level. D8C4 will only be triggered as secondary criterion when there has been significant acute contamination.
Assessments period	2011-2016	2011-2016
Related pressures	Acute pollution events	Acute pollution events
Related targets	UZN2.4 UZN2.5	UZN2.4 UZN2.5

Hoheitsgewaesser Nordsee (ANSDE_TeW)

Simplified table

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
Feature	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	Marine species
Element	Aldrin	Cadmium and its compounds	Cadmium and its compounds	Cadmium and its compounds	Cesium-137	Cesium-137	Chlorpyrifos	DDT, p,p'	Dieldrin	Endosulfan	Endrin	Hexachlorobenzene	Hexachlorobenzene	Hexachlorobutadiene	Hexachlorobutadiene	Hexachlorocyclohexane	Isodrin	Isoproturon	Lead and its compounds	Lead and its compounds	Lead and its compounds	Nickel and its compounds	Pentachlorobenzene	Polychlorinated biphenyls (7 PCB: 28,52,101,118,138,153,180)	Polychlorinated biphenyls (7 PCB: 28,52,101,118,138,153,180)	Polychlorinated biphenyls (7 PCB: 28,52,101,118,138,153,180)	Total DDT (DDT, p,p' + DDT, o,p' + DDE, p,p' + DDD, p,p')	Trichlorobenzenes (all isomers)	Trifluralin	Brominated diphenylethers (congener numbers 28, 47, 99, 100, 153 and 154)	Brominated diphenylethers (congener numbers 28, 47, 99, 100, 153 and 154)	Brominated diphenylethers (congener numbers 28, 47, 99, 100, 153 and 154)	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Total PAHs (Benzo(a)pyrene, Benzo(b)fluoranthene, Benzo(k)fluoranthene, Benzo(ghi)perylene, Indeno(1,2,3-cd)pyrene)	Total PAHs (Benzo(a)pyrene, Benzo(b)fluoranthene, Benzo(k)fluoranthene, Benzo(ghi)perylene, Indeno(1,2,3-cd)pyrene)	Total PAHs (Benzo(a)pyrene, Benzo(b)fluoranthene, Benzo(k)fluoranthene, Benzo(ghi)perylene, Indeno(1,2,3-cd)pyrene)	Tributyltin compounds	Tributyltin-cation	Littorina littorea
Element code	CAS_309-00-2	CAS_7440-43-9	CAS_7440-43-9	CAS_7440-43-9	CS002370	CS002370	CAS_2921-88-2	CAS_50-29-3	CAS_60-57-1	CAS_115-29-7	CAS_72-20-8	CAS_118-74-1	CAS_118-74-1	CAS_87-68-3	CAS_87-68-3	CAS_608-73-1	CAS_465-73-6	CAS_34123-59-6	CAS_7439-92-1	CAS_7439-92-1	CAS_7439-92-1	CAS_7440-02-0	CAS_608-93-5	EEA_33-38-5	EEA_33-38-5	EEA_33-38-5	EEA_32-03-1	CAS_12002-48-1	CAS_1582-09-8	EEA_32-04-2	EEA_32-04-2	EEA_32-04-2	CAS_7439-97-6	CAS_7439-97-6	CAS_7439-97-6	EEA_33-56-7	EEA_33-56-7	EEA_33-56-7	TBTIN	CAS_36643-28-4	140262
Element code source	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Contaminants (D8-D9) http://seadatanet.maris2.nl/v_bodc_vocab_v2/vocab_relations.asp?lib=P02	Contaminants (D8-D9) http://seadatanet.maris2.nl/v_bodc_vocab_v2/vocab_relations.asp?lib=P02	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Contaminants (D8-D9) http://vocab.ices.dk/?ref=37	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Species (D1) http://www.marinespecies.org/
Element 2
Element 2 code
Element 2 code source
Element source	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	Other	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	OSPAR
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	D8C2
Parameter	Concentration in water	Concentration in biota	Concentration in sediment	Concentration in water	Concentration in biota	Concentration in water	Concentration in water	Concentration in water	Concentration in water	Concentration in water	Concentration in water	Concentration in sediment	Concentration in water	Concentration in sediment	Concentration in water	Concentration in water	Concentration in water	Concentration in water	Concentration in biota	Concentration in sediment	Concentration in water	Concentration in water	Concentration in water	Concentration in biota	Concentration in sediment	Concentration in water	Concentration in water	Concentration in water	Concentration in water	Concentration in biota	Concentration in sediment	Concentration in water	Concentration in biota	Concentration in sediment	Concentration in water	Concentration in biota	Concentration in sediment	Concentration in water	Concentration in sediment	Concentration in water	Other
Parameter other																																									VAS defens Sequence Index (VDS)
Threshold value upper					0.159																												20.0
Threshold value lower
Threshold qualitative
Threshold value source	Other (specify)	OSPAR Convention	OSPAR Convention	Other (specify)	Other (specify)	Other (specify)	Other (specify)	Other (specify)	Other (specify)	Other (specify)	Other (specify)	Other (specify)	Other (specify)	Other (specify)	Other (specify)	Other (specify)	Other (specify)	Other (specify)	OSPAR Convention	OSPAR Convention	Other (specify)	Other (specify)	Other (specify)	OSPAR Convention	OSPAR Convention	Other (specify)	Other (specify)	Other (specify)	Other (specify)			Other (specify)	Other (specify)	OSPAR Convention	Other (specify)	OSPAR Convention	OSPAR Convention	Other (specify)		Other (specify)	OSPAR Convention
Threshold value source other	EQS, OesterV, 2011, Annex 7			EQS, OesterV, 2011, Annex 7	National	National	EQS, OesterV, 2011, Annex 7	EQS, OesterV, 2011, Annex 7	EQS, OesterV, 2011, Annex 7	EQS, OesterV, 2011, Annex 7	EQS, OesterV, 2011, Annex 7	EQS, OesterV, 2011, Annex 7	EQS, OesterV, 2011, Annex 7	EQS, OesterV, 2011, Annex 7	EQS, OesterV, 2011, Annex 7	EQS, OesterV, 2011, Annex 7	EQS, OesterV, 2011, Annex 7	EQS, OesterV, 2011, Annex 7			EQS, OesterV, 2011, Annex 7	EQS, OesterV, 2011, Annex 7	EQS, OesterV, 2011, Annex 7			EQS, OesterV, 2011,...	EQS, OesterV, 2011, Annex 7	EQS, OesterV, 2011, Annex 7	EQS, OesterV, 2011, Annex 7			EQS, OesterV, 2011, Annex 7	EQS, OesterV, 2011, Annex 7		EQS, OesterV, 2011, Annex 7			EQS, OesterV, 2011, Annex 7		EQS, OesterV, 2011, Annex 7
Value achieved upper																																	99.0
Value achieved lower																																	70.5
Value unit					Other
Value unit other					Bq/kg WW
Proportion threshold value
Proportion value achieved
Proportion threshold value unit
Trend	Unknown	Unknown	Unknown	Unknown	Unknown	Improving	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Improving	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Improving	Unknown	Improving
Parameter achieved	Yes	Yes	Yes	Yes	Yes	Not assessed	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	No	Yes	Yes	Yes	No	No	Yes	Yes	Yes	Yes	Not assessed	Not assessed	Yes	No	No	Yes	Yes	Yes	No	Not assessed	Yes	Yes
Description parameter	The assessment was carried out on the basis of the WFD management plans for 2015 (http://wasserblick.net/servlet/is/148547/). The trend has not been assessed.			The assessment was carried out on the basis of the WFD management plans for 2015 (http://wasserblick.net/servlet/is/148547/). The trend has not been assessed.	The trend was...	Threshold not yet agreed. (Federal Ministry for the Environment, Nature Conservation, Building and Nuclear Safety, Environmental Radioactivity and Radiation Pollution. 2015 Annual Report. http://nbn-resolving.de/urn:nbn:de:0221-2017072814305)	The assessment was carried out on the basis of the WFD management plans for 2015 (http://wasserblick.net/servlet/is/148547/). The trend has not been assessed.	The assessment was carried out on the basis of the WFD management plans for 2015 (http://wasserblick.net/servlet/is/148547/). The trend has not been assessed.	The assessment was carried out on the basis of the WFD management plans for 2015 (http://wasserblick.net/servlet/is/148547/). The trend has not been assessed.	The assessment was carried out on the basis of the WFD management plans for 2015 (http://wasserblick.net/servlet/is/148547/). The trend has not been assessed.	The assessment was carried out on the basis of the WFD management plans for 2015 (http://wasserblick.net/servlet/is/148547/). The trend has not been assessed.	The assessment was carried out on the basis of the WFD management plans for 2015 (http://wasserblick.net/servlet/is/148547/). The trend has not been assessed.	The assessment was carried out on the basis of the WFD management plans for 2015 (http://wasserblick.net/servlet/is/148547/). The trend has not been assessed.	The assessment was carried out on the basis of the WFD management plans for 2015 (http://wasserblick.net/servlet/is/148547/). The trend has not been assessed.	The assessment was carried out on the basis of the WFD management plans for 2015 (http://wasserblick.net/servlet/is/148547/). The trend has not been assessed.	The assessment was carried out on the basis of the WFD management plans for 2015 (http://wasserblick.net/servlet/is/148547/). The trend has not been assessed.	The assessment was carried out on the basis of the WFD management plans for 2015 (http://wasserblick.net/servlet/is/148547/). The trend has not been assessed.	The assessment was carried out on the basis of the WFD management plans for 2015 (http://wasserblick.net/servlet/is/148547/). The trend has not been assessed.			The assessment was carried out on the basis of the WFD management plans for 2015 (http://wasserblick.net/servlet/is/148547/). The trend has not been assessed.	The assessment was carried out on the basis of the WFD management plans for 2015 (http://wasserblick.net/servlet/is/148547/). The trend has not been assessed.	The assessment was carried out on the basis of the WFD management plans for 2015 (http://wasserblick.net/servlet/is/148547/). The trend has not been assessed.	PCB-118	PCB-118	The assessment was carried out on the basis of the WFD management plans for 2015 (http://wasserblick.net/servlet/is/148547/). The trend has not been assessed.	The assessment was carried out on the basis of the WFD management plans for 2015 (http://wasserblick.net/servlet/is/148547/). The trend has not been assessed.	The assessment was carried out on the basis of the WFD management plans for 2015 (http://wasserblick.net/servlet/is/148547/). The trend has not been assessed.	The assessment was carried out on the basis of the WFD management plans for 2015 (http://wasserblick.net/servlet/is/148547/). The trend has not been assessed.	Threshold not yet regionalised. OSPAR Convention	Threshold not yet regionalised. OSPAR Convention	The assessment was carried out on the basis of the WFD management plans for 2015 (http://wasserblick.net/servlet/is/148547/). The trend has not been assessed.	For mercury, the assessment in biota (dab and flounder) with the EQS of 20 μg/kg wet weight takes place. The tests showed significant overshootings in the EQS. The concentrations in the coastal waters of Lower Saxony are between 70,5 and 93 μg/kg (median values 2013-2015), depending on the monitoring station, and in the area of the coastal waters of Schleswig-Holstein Eider between 92,7 and 99 μg/kg wet weight (median values 2011-2012).		The assessment was carried out on the basis of the WFD management plans for 2015 (http://wasserblick.net/servlet/is/148547/). The trend has not been assessed.	The trend has not been assessed.	The trend has not been assessed.	The assessment was carried out on the basis of the WFD management plans for 2015 (http://wasserblick.net/servlet/is/148547/). The trend has not been assessed.	Threshold not yet regionalised. OSPAR Convention	The assessment was carried out on the basis of the WFD management plans for 2015 (http://wasserblick.net/servlet/is/148547/). The trend has not been assessed.
Related indicator		Status and Trend for Heavy Metals (Mercury, Cadmium, and Lead) in Fish and Shellfish	Status and Trend for Heavy Metals (Cadmium, Mercury and Lead) in Sediment		Nordsee Caesium-137	Nordsee Caesium-137													Status and Trend for Heavy Metals (Mercury, Cadmium, and Lead) in Fish and Shellfish	Status and Trend for Heavy Metals (Cadmium, Mercury and Lead) in Sediment				Status and Trends of Polychlorinated Biphenyls (PCB) in Fish and Shellfish	Status and Trends of Polychlorinated Biphenyls (PCB) in Sediment					Trends in Concentrations of Polybrominated Diphenyl Ethers (PBDEs) in Fish and Shellfish	Trends in Concentrations of Polybrominated Diphenyl Ethers (PBDEs) in Sediments			Status and Trend for Heavy Metals (Cadmium, Mercury and Lead) in Sediment		Status and Trends in the Concentrations of Polycyclic Aromatic Hydrocarbons (PAHs) in Shellfish	Status and Trends in the Concentrations of Polycyclic Aromatic Hydrocarbons (PAHs) in Sediment		Trends of Organotin in Sediments in the Southern North Sea		Status and Trends in the Levels of Imposex in Marine Gastropods (TBT in Shellfish)
Criteria status	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Good
Description criteria	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).				The criterion status results is based on the aggregation of the results of the elements (one-out all-out).	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).				The criterion status results is based on the aggregation of the results of the elements (one-out all-out).	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).	Threshold not yet regionalised. The status status is defined by the ?one out?.	Threshold not yet regionalised. The status status is defined by the ?one out?.	Threshold not yet regionalised. The status status is defined by the ?one out?.							Threshold not yet regionalised. The status status is defined by the ?one out?.	The criterion status results is based on the aggregation of the results of the elements (one-out all-out).
Element status	Good	Good	Good	Good	Good	Good	Good	Good	Good	Good	Good	Good	Good	Good	Good	Good	Good	Good	Not good	Not good	Not good	Good	Good	Not good	Not good	Not good	Good	Good	Good	Good	Good	Good	Not good	Not good	Not good	Not good	Not good	Not good	Not assessed	Good	Good
Description element																											Source element: EQS, OesterV, 2011, Annex 7
Integration rule type parameter	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO
Integration rule description parameter	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.
Integration rule type criteria	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO
Integration rule description criteria	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.
GES extent threshold
GES extent achieved
GES extent unit
GES achieved	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES achieved
Description overall status	The assessment was carried out either after the OSPAR Intermediate Assessment 2017 (reporting period 2011-2015) or the WFD Management Plans in 2015 (reporting period 2007-2012).	The assessment was carried out either after the OSPAR Intermediate Assessment 2017 (reporting period 2011-2015) or the WFD Management Plans in 2015 (reporting period 2007-2012).	The assessment was carried out either after the OSPAR Intermediate Assessment 2017 (reporting period 2011-2015) or the WFD Management Plans in 2015 (reporting period 2007-2012).	The assessment was carried out either after the OSPAR Intermediate Assessment 2017 (reporting period 2011-2015) or the WFD Management Plans in 2015 (reporting period 2007-2012).	The assessment was carried out either after the OSPAR Intermediate Assessment 2017 (reporting period 2011-2015) or the WFD Management Plans in 2015 (reporting period 2007-2012).	The assessment was carried out either after the OSPAR Intermediate Assessment 2017 (reporting period 2011-2015) or the WFD Management Plans in 2015 (reporting period 2007-2012).	The assessment was carried out either after the OSPAR Intermediate Assessment 2017 (reporting period 2011-2015) or the WFD Management Plans in 2015 (reporting period 2007-2012).	The assessment was carried out either after the OSPAR Intermediate Assessment 2017 (reporting period 2011-2015) or the WFD Management Plans in 2015 (reporting period 2007-2012).	The assessment was carried out either after the OSPAR Intermediate Assessment 2017 (reporting period 2011-2015) or the WFD Management Plans in 2015 (reporting period 2007-2012).	The assessment was carried out either after the OSPAR Intermediate Assessment 2017 (reporting period 2011-2015) or the WFD Management Plans in 2015 (reporting period 2007-2012).	The assessment was carried out either after the OSPAR Intermediate Assessment 2017 (reporting period 2011-2015) or the WFD Management Plans in 2015 (reporting period 2007-2012).	The assessment was carried out either after the OSPAR Intermediate Assessment 2017 (reporting period 2011-2015) or the WFD Management Plans in 2015 (reporting period 2007-2012).	The assessment was carried out either after the OSPAR Intermediate Assessment 2017 (reporting period 2011-2015) or the WFD Management Plans in 2015 (reporting period 2007-2012).	The assessment was carried out either after the OSPAR Intermediate Assessment 2017 (reporting period 2011-2015) or the WFD Management Plans in 2015 (reporting period 2007-2012).	The assessment was carried out either after the OSPAR Intermediate Assessment 2017 (reporting period 2011-2015) or the WFD Management Plans in 2015 (reporting period 2007-2012).	The assessment was carried out either after the OSPAR Intermediate Assessment 2017 (reporting period 2011-2015) or the WFD Management Plans in 2015 (reporting period 2007-2012).	The assessment was carried out either after the OSPAR Intermediate Assessment 2017 (reporting period 2011-2015) or the WFD Management Plans in 2015 (reporting period 2007-2012).	The assessment was carried out either after the OSPAR Intermediate Assessment 2017 (reporting period 2011-2015) or the WFD Management Plans in 2015 (reporting period 2007-2012).	The assessment was carried out either after the OSPAR Intermediate Assessment 2017 (reporting period 2011-2015) or the WFD Management Plans in 2015 (reporting period 2007-2012).	The assessment was carried out either after the OSPAR Intermediate Assessment 2017 (reporting period 2011-2015) or the WFD Management Plans in 2015 (reporting period 2007-2012).	The assessment was carried out either after the OSPAR Intermediate Assessment 2017 (reporting period 2011-2015) or the WFD Management Plans in 2015 (reporting period 2007-2012).	The assessment was carried out either after the OSPAR Intermediate Assessment 2017 (reporting period 2011-2015) or the WFD Management Plans in 2015 (reporting period 2007-2012).	The assessment was carried out either after the OSPAR Intermediate Assessment 2017 (reporting period 2011-2015) or the WFD Management Plans in 2015 (reporting period 2007-2012).	The assessment was carried out either after the OSPAR Intermediate Assessment 2017 (reporting period 2011-2015) or the WFD Management Plans in 2015 (reporting period 2007-2012).	The assessment was carried out either after the OSPAR Intermediate Assessment 2017 (reporting period 2011-2015) or the WFD Management Plans in 2015 (reporting period 2007-2012).	The assessment was carried out either after the OSPAR Intermediate Assessment 2017 (reporting period 2011-2015) or the WFD Management Plans in 2015 (reporting period 2007-2012).	The assessment was carried out either after the OSPAR Intermediate Assessment 2017 (reporting period 2011-2015) or the WFD Management Plans in 2015 (reporting period 2007-2012).	The assessment was carried out either after the OSPAR Intermediate Assessment 2017 (reporting period 2011-2015) or the WFD Management Plans in 2015 (reporting period 2007-2012).	The assessment was carried out either after the OSPAR Intermediate Assessment 2017 (reporting period 2011-2015) or the WFD Management Plans in 2015 (reporting period 2007-2012).	The assessment was carried out either after the OSPAR Intermediate Assessment 2017 (reporting period 2011-2015) or the WFD Management Plans in 2015 (reporting period 2007-2012).	The assessment was carried out either after the OSPAR Intermediate Assessment 2017 (reporting period 2011-2015) or the WFD Management Plans in 2015 (reporting period 2007-2012).	The assessment was carried out either after the OSPAR Intermediate Assessment 2017 (reporting period 2011-2015) or the WFD Management Plans in 2015 (reporting period 2007-2012).	The assessment was carried out either after the OSPAR Intermediate Assessment 2017 (reporting period 2011-2015) or the WFD Management Plans in 2015 (reporting period 2007-2012).	The assessment was carried out either after the OSPAR Intermediate Assessment 2017 (reporting period 2011-2015) or the WFD Management Plans in 2015 (reporting period 2007-2012).	The assessment was carried out either after the OSPAR Intermediate Assessment 2017 (reporting period 2011-2015) or the WFD Management Plans in 2015 (reporting period 2007-2012).	The assessment was carried out either after the OSPAR Intermediate Assessment 2017 (reporting period 2011-2015) or the WFD Management Plans in 2015 (reporting period 2007-2012).	The assessment was carried out either after the OSPAR Intermediate Assessment 2017 (reporting period 2011-2015) or the WFD Management Plans in 2015 (reporting period 2007-2012).	The assessment was carried out either after the OSPAR Intermediate Assessment 2017 (reporting period 2011-2015) or the WFD Management Plans in 2015 (reporting period 2007-2012).	The assessment was carried out either after the OSPAR Intermediate Assessment 2017 (reporting period 2011-2015) or the WFD Management Plans in 2015 (reporting period 2007-2012).	The assessment was carried out either after the OSPAR Intermediate Assessment 2017 (reporting period 2011-2015) or the WFD Management Plans in 2015 (reporting period 2007-2012).
Assessments period	2007-2015	2007-2015	2007-2015	2007-2015	2007-2015	2007-2015	2007-2015	2007-2015	2007-2015	2007-2015	2007-2015	2007-2015	2007-2015	2007-2015	2007-2015	2007-2015	2007-2015	2007-2015	2007-2015	2007-2015	2007-2015	2007-2015	2007-2015	2007-2015	2007-2015	2007-2015	2007-2015	2007-2015	2007-2015	2007-2015	2007-2015	2007-2015	2007-2015	2007-2015	2007-2015	2007-2015	2007-2015	2007-2015	2007-2015	2007-2015	2011-2015
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
Related targets	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5	UZN2.1 UZN2.2 UZN2.3 UZN2.4 UZN2.5