MS/Art8/2018/D8/Germany/Baltic Sea — Marine Information System for Europe

Member State report / Art8 / 2018 / D8 / Germany / Baltic 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	Baltic Sea
Reported by	Bundesministerium für Umwelt, Naturschutz und nukleare Sicherheit
Report date	2020-02-17
Report access	DE_ART8_GES.xml

Kuestengewaesser (BALDE_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	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	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 - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Marine species	Marine species	Marine species
Element	1,1,1-Trichloroethane	1,2-Dichloroethane	1,2-Dichloroethene	2,4-dichlorophenoxyacetic acid, 2-4 D	Alachlor	Ametryn	Anthracene	Anthracene	Arsenic and its compounds	Atrazine	Azinphos-ethyl	Azinphos-methyl	Bentazone	Bis(2-methoxyethyl) phthalate	Bromacil	Bromoxynil	Cadmium and its compounds	Cadmium and its compounds	Cadmium and its compounds	Cesium-137	Cesium-137	Chlordane	Chlorfenvinphos	Chloridazon	Chloroalkanes C10-13	Chlorotoluron	Chlorpyrifos	Chromium and its compounds	Copper and its compounds	Coumaphos	Demeton	Demeton-S-methyl	Demeton-S-methylsulfon	Dibutyltin	Dichloromethane	Dichlorprop (2,4-DP)	Dichlorvos	Diflufenican	Dimethoate	Disulfoton	Diuron	Endosulfan	Epoxiconazole	Ethylbenzene	Etrimfos	Fenitrothion	Fenthion	Fluoranthene	Fluoranthene	Hexachlorobenzene	Hexachlorobutadiene	Hexachlorocyclohexane	Hexazinone	Isoproturon	Lead and its compounds	Lead and its compounds	Lead and its compounds	Linuron	MCPA	Malathion	Mecoprop	Metazachlor	Methabenzthiazuron	Methamidophos	Metolachlor	Metribuzin	Mevinphos	Monolinuron	Naphthalene	Nickel and its compounds	Nonylphenol	Octylphenol (4‐(1,1',3,3'‐tetramethylbutyl)‐phenol)	Omethoate	Parathion	Parathion-methyl	Pentachlorobenzene	Pentachlorophenol	Phoxim	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)	Prometryn	Propanil	Propiconazole	Selenium and its compounds	Simazine	Tetrabutyltin	Tetrabutyltin	Thallium	Toluene	Tri-n-butyl phosphate	Triazophos	Trichlorfon	Trichlorobenzenes (all isomers)	Trichloromethane	Trifluralin	Triphenyltin and compounds	Triphenyltin and compounds	Zinc and its compounds	m-Xylene	o-Xylene	p-Xylene	Benzo(a)pyrene	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	Hexabromocyclododecanes (HBCDD)	Hexabromocyclododecanes (HBCDD)	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Perfluorooctane sulfonic acid (PFOS) and its derivatives	Total PAHs (Benzo(a)pyrene, Benzo(b)fluoranthene, Benzo(k)fluoranthene, Benzo(ghi)perylene, Indeno(1,2,3-cd)pyrene)	Tributyltin compounds	Tributyltin compounds	Haliaeetus albicilla	Haliaeetus albicilla	Haliaeetus albicilla
Element code	CAS_71-55-6	CAS_107-06-2	CAS_540-59-0	CAS_94-75-7	CAS_15972-60-8	CAS_834-12-8	CAS_120-12-7	CAS_120-12-7	CAS_7440-38-2	CAS_1912-24-9	CAS_2642-71-9	CAS_86-50-0	CAS_25057-89-0	BMOEP	CAS_314-40-9	CAS_1689-84-5	CAS_7440-43-9	CAS_7440-43-9	CAS_7440-43-9	CS002370	CS002370	CAS_57-74-9	CAS_470-90-6	CAS_1698-60-8	CAS_85535-84-8	CAS_15545-48-9	CAS_2921-88-2	CAS_7440-47-3	CAS_7440-50-8	CAS_56-72-4	DEMT	CAS_919-86-8	CAS_17040-19-6	CAS_1002-53-5	CAS_75-09-2	CAS_120-36-5	CAS_62-73-7	CAS_83164-33-4	CAS_60-51-5	CAS_298-04-4	CAS_330-54-1	CAS_115-29-7	CAS_133855-98-8	CAS_100-41-4	ETRMF	CAS_122-14-5	CAS_55-38-9	CAS_206-44-0	CAS_206-44-0	CAS_118-74-1	CAS_87-68-3	CAS_608-73-1	CAS_51235-04-2	CAS_34123-59-6	CAS_7439-92-1	CAS_7439-92-1	CAS_7439-92-1	CAS_330-55-2	CAS_94-74-6	CAS_121-75-5	CAS_7085-19-0	CAS_67129-08-2	CAS_18691-97-9	CAS_10265-92-6	CAS_51218-45-2	CAS_21087-64-9	CAS_7786-34-7	CAS_1746-81-2	CAS_91-20-3	CAS_7440-02-0	NOPHE	CAS_140-66-9	CAS_1113-02-6	CAS_56-38-2	CAS_298-00-0	CAS_608-93-5	CAS_87-86-5	PHXM	CAS_137641-05-5	CAS_23103-98-2	EEA_33-38-5	EEA_33-38-5	EEA_33-38-5	CAS_7287-19-6	CAS_709-98-8	CAS_60207-90-1	CAS_7782-49-2	CAS_122-34-9	CAS_1461-25-2	CAS_1461-25-2	CAS_7440-28-0	CAS_108-88-3	TBP	CAS_24017-47-8	TRCF	CAS_12002-48-1	CAS_67-66-3	CAS_1582-09-8	EEA_33-61-4	EEA_33-61-4	CAS_7440-66-6	CAS_108-38-3	CAS_95-47-6	CAS_106-42-3	CAS_50-32-8	EEA_32-04-2	EEA_32-04-2	EEA_32-04-2	CAS_76-44-8	CAS_1024-57-3	EEA_33-57-8	EEA_33-57-8	CAS_7439-97-6	CAS_7439-97-6	CAS_7439-97-6	CAS_1763-23-1	EEA_33-56-7	TBTIN	TBTIN	232053	232053	232053
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	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	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	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	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	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://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	Contaminants (D8-D9) http://vocab.ices.dk/?ref=37	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	Contaminants (D8-D9) http://vocab.ices.dk/?ref=37	Contaminants (D8-D9) http://vocab.ices.dk/?ref=37	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	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	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	ICES	ICES	ICES	ICES	ICES	ICES	ICES	HELCOM	HELCOM	HELCOM
Criterion	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C2	D8C2	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 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 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 sediment	Concentration in water	Concentration in water	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 water	Concentration in water	Concentration in water	Concentration in water	Concentration in water	Concentration in water	Concentration in water	Concentration in biota	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 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 water	Concentration in water	Concentration in water	Concentration in water	Concentration in sediment	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 water	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 biota	Concentration in biota	Concentration in sediment	Concentration in water	Concentration in water	Concentration in water	Concentration in sediment	Concentration in biota	Concentration in water	Concentration in biota	Concentration in sediment	Concentration in water	Concentration in water	Concentration in sediment	Concentration in water	Other	Other	Other
Parameter other																																																																																																																								Breeding success	Brood size	Productivity
Threshold value upper
Threshold value lower
Threshold qualitative
Threshold value source	Other (specify)	Other (specify)	Other (specify)	Other (specify)	Other (specify)	Other (specify)	Helsinki Convention	Other (specify)	Other (specify)	Other (specify)	Other (specify)	Other (specify)	Other (specify)	Other (specify)	Other (specify)	Other (specify)	Other (specify)	Helsinki Convention	Helsinki Convention	Helsinki Convention	Helsinki 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)	Helsinki Convention	Other (specify)	Other (specify)	Other (specify)	Other (specify)	Other (specify)	Helsinki Convention	Helsinki 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)		Helsinki 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)	Helsinki Convention	Helsinki Convention		Other (specify)	Other (specify)	Other (specify)	Helsinki Convention	Helsinki Convention	Other (specify)	Other (specify)		Helsinki Convention	Other (specify)	Helsinki Convention	Helsinki Convention			Helsinki Convention
Threshold value source other	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, Annex 7	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,...	EQS, OesterV, 2011, Annex 7					EQS, OesterV, 2011,...	EQS, OesterV, 2011, Annex 7	EQS, OesterV, 2011,...	EQS, OesterV, 2011, Annex 7	EQS, OesterV, 2011,...	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,...	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, 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,...	EQS, OesterV, 2011,...	EQS, OesterV, 2011,...	EQS, OesterV, 2011,...	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, Annex 7	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, Annex 7	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,...	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,...	EQS, OesterV, 2011,...	EQS, OesterV, 2011,...				EQS, OesterV, 2011, Annex 7	EQS, OesterV, 2011,...	EQS, OesterV, 2011,...			EQS, OesterV, 2011, Annex 7	UQN, OGewV, 2011 Anlage 7			EQS, OesterV, 2011, Annex 7
Value achieved upper
Value achieved lower
Value unit
Value unit other
Proportion threshold value
Proportion value achieved
Proportion threshold value unit
Trend	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	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	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
Parameter achieved	Yes	Yes	Yes	Yes	Yes	Yes	No	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	No	No	No	No	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	No	Yes	Yes	Yes	No	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	No	No	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Not assessed	Yes	No	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	No	Not assessed	Yes	Yes	Yes	Yes	Yes	Yes	No	Not assessed	No	No	No	No	Not assessed	Not assessed	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 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 trend has not been assessed.	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.	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 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 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.	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.	Der Trend wurde nicht bewertet. Schwellenwert noch nicht regional abgestimmt. Helsinki Convention	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 trend has not been assessed.	The trend has not been assessed.	Der Trend wurde nicht bewertet. Schwellenwert noch nicht regional abgestimmt. Helsinki 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.	Der Trend wurde nicht bewertet. In die Bewertung der HELCOM-Becken mit Anteilen deutscher Gewässer sind keine deutschen Daten eingeflossen. Ein Handlungsbedarf ist daher zunächst über ein eigenes Monitoring zu prüfen/ bestätigen.	Der Trend wurde nicht bewertet. In die Bewertung der HELCOM-Becken mit Anteilen deutscher Gewässer sind keine deutschen Daten eingeflossen. Ein Handlungsbedarf ist daher zunächst über ein eigenes Monitoring zu prüfen/ bestätigen.	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 has not been assessed. Threshold not yet regionalised.	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 has not been assessed.	Der Trend wurde nicht bewertet. In die Bewertung der HELCOM-Becken mit Anteilen deutscher Gewässer sind keine deutschen Daten eingeflossen. Ein Handlungsbedarf ist daher zunächst über ein eigenes Monitoring zu prüfen/ bestätigen.	Der Trend wurde nicht bewertet. Schwellenwert noch nicht regional abgestimmt. Helsinki Convention	Der Trend wurde nicht bewertet. Schwellenwert noch nicht regional abgestimmt. Helsinki Convention
Related indicator							Polyaromatic hydrocarbons (PAH) and their metabolites											Metals (lead, cadmium and mercury)	Metals (lead, cadmium and mercury)	Radioactive substances: Cesium-137 in fish and surface seawater	Radioactive substances: Cesium-137 in fish and surface seawater																												Polyaromatic hydrocarbons (PAH) and their metabolites						Metals (lead, cadmium and mercury)	Metals (lead, cadmium and mercury)																									PCB, Dioxin and Furan	PCB, Dioxin and Furan																							Polyaromatic hydrocarbons (PAH) and their metabolites	Polybrominated diphenyl Ethers (PBDE)	Polybrominated diphenyl Ethers (PBDE)				Hexabromocyclodocecane (HBCDD)	Hexabromocyclodocecane (HBCDD)			Metals (lead, cadmium and mercury)	Perfluorooctane sulphonate (PFOS)		Tributyltin (TBT) and Imposex	Tributyltin (TBT) and Imposex	White-tailed eagle productivity	White-tailed eagle productivity	White-tailed eagle productivity
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	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	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).	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).
Element status	Good	Good	Good	Good	Good	Good	Not good	Not good	Good	Good	Good	Good	Good	Good	Good	Good	Not good	Not good	Not good	Not good	Not good	Good	Good	Good	Good	Good	Good	Good	Good	Good	Good	Good	Good	Not good	Good	Good	Good	Not 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	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	Good	Good	Good	Good	Good	Good	Good	Good	Good	Good	Good	Good	Good	Not good	Not good	Not good	Good	Good	Good	Good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Good	Good	Good
Description element
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	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.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, 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	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.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, the individual results are aggregated according to the principle "one out - all out". This applies to spatial aggregation and aggregation between indicators and criteria.	For the assessment of the good state in relation to pollutants, 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 expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to be achieved later than 2020, no Article 14 exception reported	GES expected to 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	GES achieved	GES achieved
Description overall status	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.	Die Bewertung erfolgte anhand der WRRL-Bewirtschaftungspläne 2015.
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	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	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	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, 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	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5

AWZ (BALDE_EEZ)

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
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 - 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
Element	Anthracene	Cadmium and its compounds	Cadmium and its compounds	Cadmium and its compounds	Cesium-137	Cesium-137	Fluoranthene	Lead and its compounds	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)	Benzo(a)pyrene	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)	Hexabromocyclododecanes (HBCDD)	Hexabromocyclododecanes (HBCDD)	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Perfluorooctane sulfonic acid (PFOS) and its derivatives	Perfluorooctane sulfonic acid (PFOS) and its derivatives	Tributyltin compounds	Tributyltin compounds
Element code	CAS_120-12-7	CAS_7440-43-9	CAS_7440-43-9	CAS_7440-43-9	CS002370	CS002370	CAS_206-44-0	CAS_7439-92-1	CAS_7439-92-1	CAS_7439-92-1	EEA_33-38-5	EEA_33-38-5	EEA_33-38-5	CAS_50-32-8	EEA_32-04-2	EEA_32-04-2	EEA_32-04-2	EEA_33-57-8	EEA_33-57-8	CAS_7439-97-6	CAS_7439-97-6	CAS_7439-97-6	CAS_1763-23-1	CAS_1763-23-1	TBTIN	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	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	Contaminants (D8-D9) http://vocab.ices.dk/?ref=37	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	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	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1
Parameter	Concentration in sediment	Concentration in sediment	Concentration in biota	Concentration in water	Concentration in biota	Concentration in water	Concentration in biota	Concentration in water	Concentration in sediment	Concentration in biota	Concentration in biota	Concentration in sediment	Concentration in water	Concentration in biota	Concentration in sediment	Concentration in water	Concentration in biota	Concentration in biota	Concentration in sediment	Concentration in water	Concentration in biota	Concentration in sediment	Concentration in biota	Concentration in water	Concentration in sediment	Concentration in water
Parameter other
Threshold value upper
Threshold value lower
Threshold qualitative
Threshold value source	Helsinki Convention	Helsinki Convention	Helsinki Convention	Helsinki Convention	Helsinki Convention	Helsinki Convention	Helsinki Convention	Helsinki Convention	Helsinki Convention	Helsinki Convention	Helsinki Convention			Helsinki Convention	Helsinki Convention		Helsinki Convention	Helsinki Convention	Helsinki Convention		Helsinki Convention		Helsinki Convention	Helsinki Convention	Helsinki Convention	Helsinki Convention
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	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown
Parameter achieved	No	No	No	Yes	No	No	Yes	No	No	No	No	Not assessed	Not assessed	Yes	Yes	Not assessed	No	Yes	Yes	Not assessed	No	Not assessed	Yes	Not assessed	No	No
Description parameter	The trend has not been assessed.	The trend has not been assessed.	The trend has not been assessed.	The trend has not been assessed.	The trend has not been assessed.	The trend has not been assessed.	The trend has not been assessed.	The trend has not been assessed.	The trend has not been assessed.	The trend has not been assessed.	The trend has not been assessed.	Der Trend wurde nicht bewertet. Schwellenwert noch nicht regional abgestimmt. Helsinki Convention	The trend has not been assessed.	The trend has not been assessed.	Der Trend wurde nicht bewertet. In die Bewertung der HELCOM-Becken mit Anteilen deutscher Gewässer sind keine deutschen Daten eingeflossen. Ein Handlungsbedarf ist daher zunächst über ein eigenes Monitoring zu prüfen/ bestätigen.	Der Trend wurde nicht bewertet. Schwellenwert noch nicht regional abgestimmt. Helsinki Convention	The trend has not been assessed.	Der Trend wurde nicht bewertet. In die Bewertung der HELCOM-Becken mit Anteilen deutscher Gewässer sind keine deutschen Daten eingeflossen. Ein Handlungsbedarf ist daher zunächst über ein eigenes Monitoring zu prüfen/ bestätigen.	Der Trend wurde nicht bewertet. In die Bewertung der HELCOM-Becken mit Anteilen deutscher Gewässer sind keine deutschen Daten eingeflossen. Ein Handlungsbedarf ist daher zunächst über ein eigenes Monitoring zu prüfen/ bestätigen.	Der Trend wurde nicht bewertet. Schwellenwert noch nicht regional abgestimmt. Helsinki Convention	The trend has not been assessed.	Der Trend wurde nicht bewertet. Schwellenwert noch nicht regional abgestimmt. Helsinki Convention	Der Trend wurde nicht bewertet. In die Bewertung der HELCOM-Becken mit Anteilen deutscher Gewässer sind keine deutschen Daten eingeflossen. Ein Handlungsbedarf ist daher zunächst über ein eigenes Monitoring zu prüfen/ bestätigen.	Der Trend wurde nicht bewertet. Es liegen keine Daten vor.	The trend has not been assessed.	Der Trend wurde nicht bewertet. In die Bewertung der HELCOM-Becken mit Anteilen deutscher Gewässer sind keine deutschen Daten eingeflossen. Ein Handlungsbedarf ist daher zunächst über ein eigenes Monitoring zu prüfen/ bestätigen.
Related indicator	Polyaromatic hydrocarbons (PAH) and their metabolites	Metals (lead, cadmium and mercury)	Metals (lead, cadmium and mercury)	Metals (lead, cadmium and mercury)	Radioactive substances: Cesium-137 in fish and surface seawater	Radioactive substances: Cesium-137 in fish and surface seawater	Polyaromatic hydrocarbons (PAH) and their metabolites	Metals (lead, cadmium and mercury)	Metals (lead, cadmium and mercury)	Metals (lead, cadmium and mercury)	PCB, Dioxin and Furan	PCB, Dioxin and Furan	PCB, Dioxin and Furan	Polyaromatic hydrocarbons (PAH) and their metabolites	Polybrominated diphenyl Ethers (PBDE)	Polybrominated diphenyl Ethers (PBDE)	Polybrominated diphenyl Ethers (PBDE)	Hexabromocyclodocecane (HBCDD)	Hexabromocyclodocecane (HBCDD)	Metals (lead, cadmium and mercury)	Metals (lead, cadmium and mercury)	Metals (lead, cadmium and mercury)	Perfluorooctane sulphonate (PFOS)	Perfluorooctane sulphonate (PFOS)	Tributyltin (TBT) and Imposex	Tributyltin (TBT) and Imposex
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
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).
Element status	Not good	Not good	Not good	Not good	Not good	Not good	Good	Not good	Not good	Not good	Not good	Not good	Not good	Good	Not good	Not good	Not good	Good	Good	Not good	Not good	Not good	Good	Good	Not good	Not good
Description element
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
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.
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
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.
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
Description overall status	Die Bewertung erfolgte nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeitraum 2011-2016).	Die Bewertung erfolgte nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeitraum 2011-2016).	Die Bewertung erfolgte nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeitraum 2011-2016).	Die Bewertung erfolgte nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeitraum 2011-2016).	Die Bewertung erfolgte nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeitraum 2011-2016).	Die Bewertung erfolgte nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeitraum 2011-2016).	Die Bewertung erfolgte nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeitraum 2011-2016).	Die Bewertung erfolgte nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeitraum 2011-2016).	Die Bewertung erfolgte nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeitraum 2011-2016).	Die Bewertung erfolgte nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeitraum 2011-2016).	Die Bewertung erfolgte nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeitraum 2011-2016).	Die Bewertung erfolgte nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeitraum 2011-2016).	Die Bewertung erfolgte nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeitraum 2011-2016).	Die Bewertung erfolgte nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeitraum 2011-2016).	Die Bewertung erfolgte nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeitraum 2011-2016).	Die Bewertung erfolgte nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeitraum 2011-2016).	Die Bewertung erfolgte nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeitraum 2011-2016).	Die Bewertung erfolgte nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeitraum 2011-2016).	Die Bewertung erfolgte nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeitraum 2011-2016).	Die Bewertung erfolgte nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeitraum 2011-2016).	Die Bewertung erfolgte nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeitraum 2011-2016).	Die Bewertung erfolgte nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeitraum 2011-2016).	Die Bewertung erfolgte nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeitraum 2011-2016).	Die Bewertung erfolgte nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeitraum 2011-2016).	Die Bewertung erfolgte nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeitraum 2011-2016).	Die Bewertung erfolgte nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeitraum 2011-2016).
Assessments period	2011-2016	2011-2016	2011-2016	2011-2016	2011-2016	2011-2016	2011-2016	2011-2016	2011-2016	2011-2016	2011-2016	2011-2016	2011-2016	2011-2016	2011-2016	2011-2016	2011-2016	2011-2016	2011-2016	2011-2016	2011-2016	2011-2016	2011-2016	2011-2016	2011-2016	2011-2016
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
Related targets	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5

Deutsche Ostsee (BALDE_MS)

Simplified table

GES component	D8	D8	D8
Feature	Acute pollution events	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	D8C3	D8C4
Parameter	Other	Other	Other
Parameter other	Number	Size	Not specified
Threshold value upper
Threshold value lower
Threshold qualitative
Threshold value source	Helsinki Convention	Helsinki Convention
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	Improving	Improving	Unknown
Parameter achieved	Not assessed	Not assessed	Not assessed
Description parameter
Related indicator	Operational Oil Spills from Ships	Operational Oil Spills from Ships
Criteria status	Not assessed	Not assessed	Not assessed
Description criteria	In the reporting period, there have been six damage situations in the German Baltic Sea waters since 2011 under the overall operational management of the accident command, which involved two oil pollution and two contaminant landings with paraffin. None of the six damage levels have caused significant acute marine pollution. This is due, among other things, to the high precautionary standard and the professional competence in the processing of shipwrecks, which have existed since the foundation of the accident command in the Federal Republic of Germany. The partners in the agreement on combating marine pollution have also agreed to take into account water, shore and beach pollution with paraffin under certain conditions, thereby classifying it as a complex pollutant accident, although it is not currently listed as a marine environment-hazardous pollutant according to MARPOL. Paraffin pollution on shores and beaches has occurred repeatedly on the Baltic Sea. However, the risk of environmental pollution from paraffin, such as the bonding of bird plumage, is considered to be very low even in summer due to the solidification of paraffin in the cool Baltic Sea water (UEG 2014). The duration and spatial extent of acute pollution (criterion D8C3) are already recorded by the statistics of the accident command; however, there is still no regional or subregional assessment.	In the reporting period, there have been six damage situations in the German Baltic Sea waters since 2011 under the overall operational management of the accident command, which involved two oil pollution and two contaminant landings with paraffin. None of the six damage levels have caused significant acute marine pollution. This is due, among other things, to the high precautionary standard and the professional competence in the processing of shipwrecks, which have existed since the foundation of the accident command in the Federal Republic of Germany. The partners in the agreement on combating marine pollution have also agreed to take into account water, shore and beach pollution with paraffin under certain conditions, thereby classifying it as a complex pollutant accident, although it is not currently listed as a marine environment-hazardous pollutant according to MARPOL. Paraffin pollution on shores and beaches has occurred repeatedly on the Baltic Sea. However, the risk of environmental pollution from paraffin, such as the bonding of bird plumage, is considered to be very low even in summer due to the solidification of paraffin in the cool Baltic Sea water (UEG 2014). The duration and spatial extent of acute pollution (criterion D8C3) are already recorded by the statistics of the accident command; however, there is still no regional or subregional assessment.	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	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.	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	2011-2015	2011-2015	2011-2015
Related pressures	Acute pollution events	Acute pollution events	Acute pollution events
Related targets	UZO2.4 UZO2.5	UZO2.4 UZO2.5	UZO2.4 UZO2.5

Küstenmeer Schlei/Trave (DE_CW_B0.9610)

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
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 - 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
Element	1,2-Dichloroethane	Alachlor	Anthracene	Anthracene	Atrazine	Bis(2-methoxyethyl) phthalate	Cadmium and its compounds	Cadmium and its compounds	Cadmium and its compounds	Cesium-137	Cesium-137	Chlorfenvinphos	Chloroalkanes C10-13	Chlorpyrifos	Dichloromethane	Diuron	Endosulfan	Fluoranthene	Fluoranthene	Hexachlorobenzene	Hexachlorobutadiene	Hexachlorocyclohexane	Isoproturon	Lead and its compounds	Lead and its compounds	Lead and its compounds	Naphthalene	Nickel and its compounds	Nonylphenol	Octylphenol (4‐(1,1',3,3'‐tetramethylbutyl)‐phenol)	Pentachlorobenzene	Pentachlorophenol	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)	Simazine	Trichlorobenzenes (all isomers)	Trichloromethane	Trifluralin	Benzo(a)pyrene	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)	Hexabromocyclododecanes (HBCDD)	Hexabromocyclododecanes (HBCDD)	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Perfluorooctane sulfonic acid (PFOS) and its derivatives	Total PAHs (Benzo(a)pyrene, Benzo(b)fluoranthene, Benzo(k)fluoranthene, Benzo(ghi)perylene, Indeno(1,2,3-cd)pyrene)	Tributyltin compounds	Tributyltin compounds
Element code	CAS_107-06-2	CAS_15972-60-8	CAS_120-12-7	CAS_120-12-7	CAS_1912-24-9	BMOEP	CAS_7440-43-9	CAS_7440-43-9	CAS_7440-43-9	CS002370	CS002370	CAS_470-90-6	CAS_85535-84-8	CAS_2921-88-2	CAS_75-09-2	CAS_330-54-1	CAS_115-29-7	CAS_206-44-0	CAS_206-44-0	CAS_118-74-1	CAS_87-68-3	CAS_608-73-1	CAS_34123-59-6	CAS_7439-92-1	CAS_7439-92-1	CAS_7439-92-1	CAS_91-20-3	CAS_7440-02-0	NOPHE	CAS_140-66-9	CAS_608-93-5	CAS_87-86-5	EEA_33-38-5	EEA_33-38-5	EEA_33-38-5	CAS_122-34-9	CAS_12002-48-1	CAS_67-66-3	CAS_1582-09-8	CAS_50-32-8	EEA_32-04-2	EEA_32-04-2	EEA_32-04-2	EEA_33-57-8	EEA_33-57-8	CAS_7439-97-6	CAS_7439-97-6	CAS_7439-97-6	CAS_1763-23-1	EEA_33-56-7	TBTIN	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	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	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	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	Contaminants (D8-D9) http://vocab.ices.dk/?ref=37	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	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
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
Parameter	Concentration in water	Concentration in water	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 biota	Concentration in water	Concentration in water	Concentration in water	Concentration in water	Concentration in water	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 biota	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 biota	Concentration in water	Concentration in water	Concentration in water	Concentration in water	Concentration in water	Concentration in biota	Concentration in biota	Concentration in water	Concentration in sediment	Concentration in sediment	Concentration in biota	Concentration in biota	Concentration in sediment	Concentration in water	Concentration in water	Concentration in water	Concentration in water	Concentration in sediment
Parameter other
Threshold value upper
Threshold value lower
Threshold qualitative
Threshold value source	Other (specify)	Other (specify)	Helsinki Convention	Other (specify)	Other (specify)	Other (specify)	Helsinki Convention	Helsinki Convention	Other (specify)	Helsinki Convention	Helsinki Convention	Other (specify)	Other (specify)	Other (specify)	Other (specify)	Other (specify)	Other (specify)	Helsinki Convention	Other (specify)	Other (specify)	Other (specify)	Other (specify)	Other (specify)	Helsinki Convention	Helsinki Convention	Other (specify)	Other (specify)	Other (specify)	Other (specify)	Other (specify)	Other (specify)	Other (specify)		Helsinki Convention	Other (specify)	Other (specify)	Other (specify)	Other (specify)	Other (specify)	Helsinki Convention	Helsinki Convention	Other (specify)		Helsinki Convention	Helsinki Convention	Other (specify)		Other (specify)	Helsinki Convention	Other (specify)	Helsinki Convention	Helsinki Convention
Threshold value source other	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, 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				UQN, OGewV, 2011 Anlage 7		EQS, OesterV, 2011, Annex 7		EQS, OesterV, 2011, Annex 7
Value achieved upper
Value achieved lower
Value unit
Value unit other
Proportion threshold value
Proportion value achieved
Proportion threshold value unit
Trend	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown
Parameter achieved	Yes	Yes	No	Yes	Yes	Yes	No	No	Yes	No	No	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	No	No	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Not assessed	Yes	Not assessed	Yes	Yes	Yes	Yes	Yes	No	Yes	Not assessed	Yes	Yes	No	Not assessed	Yes	No	No	No	No
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 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 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.	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.	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 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 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.	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.	Der Trend wurde nicht bewertet. Schwellenwert noch nicht regional abgestimmt. Helsinki Convention	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 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.	Der Trend wurde nicht bewertet. Schwellenwert noch nicht regional abgestimmt. Helsinki Convention	Der Trend wurde nicht bewertet. In die Bewertung der HELCOM-Becken mit Anteilen deutscher Gewässer sind keine deutschen Daten eingeflossen. Ein Handlungsbedarf ist daher zunächst über ein eigenes Monitoring zu prüfen/ bestätigen.	Der Trend wurde nicht bewertet. In die Bewertung der HELCOM-Becken mit Anteilen deutscher Gewässer sind keine deutschen Daten eingeflossen. Ein Handlungsbedarf ist daher zunächst über ein eigenes Monitoring zu prüfen/ bestätigen.	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. Threshold not yet regionalised.	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 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.	Der Trend wurde nicht bewertet. In die Bewertung der HELCOM-Becken mit Anteilen deutscher Gewässer sind keine deutschen Daten eingeflossen. Ein Handlungsbedarf ist daher zunächst über ein eigenes Monitoring zu prüfen/ bestätigen.	The trend has not been assessed.
Related indicator			Polyaromatic hydrocarbons (PAH) and their metabolites				Metals (lead, cadmium and mercury)	Metals (lead, cadmium and mercury)		Radioactive substances: Cesium-137 in fish and surface seawater	Radioactive substances: Cesium-137 in fish and surface seawater							Polyaromatic hydrocarbons (PAH) and their metabolites						Metals (lead, cadmium and mercury)	Metals (lead, cadmium and mercury)								PCB, Dioxin and Furan	PCB, Dioxin and Furan						Polyaromatic hydrocarbons (PAH) and their metabolites	Polybrominated diphenyl Ethers (PBDE)		Polybrominated diphenyl Ethers (PBDE)	Hexabromocyclodocecane (HBCDD)	Hexabromocyclodocecane (HBCDD)		Metals (lead, cadmium and mercury)		Perfluorooctane sulphonate (PFOS)		Tributyltin (TBT) and Imposex	Tributyltin (TBT) and Imposex
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
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).
Element status	Good	Good	Not good	Not good	Good	Good	Not good	Not good	Not good	Not good	Not 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	Good	Good	Good	Good	Good	Not good	Not good	Not good	Good	Good	Not good	Not good	Not good	Not good	Not good	Not good	Not good
Description element		The criterion status results is based on the aggregation of the results of the elements (one-out all-out).
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
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.
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
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.
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
Description overall status	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2011-2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2011-2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2011-2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2011-2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2011-2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2011-2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2011-2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2011-2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2011-2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2011-2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2011-2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2011-2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2011-2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.
Assessments period	2007-2016	2007-2016	2007-2016	2007-2016	2007-2016	2007-2016	2007-2016	2007-2016	2007-2016	2007-2016	2007-2016	2007-2016	2007-2016	2007-2016	2007-2016	2007-2016	2007-2016	2007-2016	2007-2016	2007-2016	2007-2016	2007-2016	2007-2016	2007-2016	2007-2016	2007-2016	2007-2016	2007-2016	2007-2016	2007-2016	2007-2016	2007-2016	2007-2016	2007-2016	2007-2016	2007-2016	2007-2016	2007-2016	2007-2016	2007-2016	2007-2016	2007-2016	2007-2016	2007-2016	2007-2016	2007-2016	2007-2016	2007-2016	2007-2016	2007-2016	2007-2016	2007-2016
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
Related targets	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5

Küstenmeer Warnow-Peene (DE_CW_DEMV_WP_20)

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
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 - 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
Element	1,2-Dichloroethane	Alachlor	Anthracene	Anthracene	Atrazine	Bis(2-methoxyethyl) phthalate	Cadmium and its compounds	Cadmium and its compounds	Cadmium and its compounds	Cesium-137	Cesium-137	Chlorfenvinphos	Chloroalkanes C10-13	Chlorpyrifos	Dichloromethane	Diuron	Endosulfan	Fluoranthene	Fluoranthene	Hexachlorobenzene	Hexachlorobutadiene	Hexachlorocyclohexane	Isoproturon	Lead and its compounds	Lead and its compounds	Lead and its compounds	Naphthalene	Nickel and its compounds	Nonylphenol	Octylphenol (4‐(1,1',3,3'‐tetramethylbutyl)‐phenol)	Pentachlorobenzene	Pentachlorophenol	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)	Simazine	Trichlorobenzenes (all isomers)	Trichloromethane	Trifluralin	Benzo(a)pyrene	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)	Hexabromocyclododecanes (HBCDD)	Hexabromocyclododecanes (HBCDD)	Mercury and its compounds	Mercury and its compounds	Mercury and its compounds	Perfluorooctane sulfonic acid (PFOS) and its derivatives	Total PAHs (Benzo(a)pyrene, Benzo(b)fluoranthene, Benzo(k)fluoranthene, Benzo(ghi)perylene, Indeno(1,2,3-cd)pyrene)	Tributyltin compounds	Tributyltin compounds
Element code	CAS_107-06-2	CAS_15972-60-8	CAS_120-12-7	CAS_120-12-7	CAS_1912-24-9	BMOEP	CAS_7440-43-9	CAS_7440-43-9	CAS_7440-43-9	CS002370	CS002370	CAS_470-90-6	CAS_85535-84-8	CAS_2921-88-2	CAS_75-09-2	CAS_330-54-1	CAS_115-29-7	CAS_206-44-0	CAS_206-44-0	CAS_118-74-1	CAS_87-68-3	CAS_608-73-1	CAS_34123-59-6	CAS_7439-92-1	CAS_7439-92-1	CAS_7439-92-1	CAS_91-20-3	CAS_7440-02-0	NOPHE	CAS_140-66-9	CAS_608-93-5	CAS_87-86-5	EEA_33-38-5	EEA_33-38-5	EEA_33-38-5	CAS_122-34-9	CAS_12002-48-1	CAS_67-66-3	CAS_1582-09-8	CAS_50-32-8	EEA_32-04-2	EEA_32-04-2	EEA_32-04-2	EEA_33-57-8	EEA_33-57-8	CAS_7439-97-6	CAS_7439-97-6	CAS_7439-97-6	CAS_1763-23-1	EEA_33-56-7	TBTIN	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	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	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	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	Contaminants (D8-D9) http://vocab.ices.dk/?ref=37	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	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
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
Parameter	Concentration in water	Concentration in water	Concentration in water	Concentration in sediment	Concentration in water	Concentration in water	Concentration in sediment	Concentration in biota	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 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 biota	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 water	Concentration in water	Concentration in water	Concentration in biota	Concentration in sediment	Concentration in biota	Concentration in water	Concentration in sediment	Concentration in biota	Concentration in sediment	Concentration in biota	Concentration in water	Concentration in water	Concentration in water	Concentration in sediment	Concentration in water
Parameter other
Threshold value upper
Threshold value lower
Threshold qualitative
Threshold value source	Other (specify)	Other (specify)	Other (specify)	Helsinki Convention	Other (specify)	Other (specify)	Helsinki Convention	Helsinki Convention	Other (specify)	Helsinki Convention	Helsinki Convention	Other (specify)	Other (specify)	Other (specify)	Other (specify)	Other (specify)	Other (specify)	Helsinki Convention	Other (specify)	Other (specify)	Other (specify)	Other (specify)	Other (specify)	Other (specify)	Helsinki Convention	Helsinki Convention	Other (specify)	Other (specify)	Other (specify)	Other (specify)	Other (specify)	Other (specify)	Helsinki Convention		Other (specify)	Other (specify)	Other (specify)	Other (specify)	Other (specify)	Helsinki Convention		Helsinki Convention	Other (specify)	Helsinki Convention	Helsinki Convention		Other (specify)	Other (specify)	Helsinki Convention	Other (specify)	Helsinki Convention	Helsinki Convention
Threshold value source other	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, 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				UQN, OGewV, 2011 Anlage 7	EQS, OesterV, 2011, Annex 7		EQS, OesterV, 2011, Annex 7
Value achieved upper
Value achieved lower
Value unit
Value unit other
Proportion threshold value
Proportion value achieved
Proportion threshold value unit
Trend	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown
Parameter achieved	Yes	Yes	Yes	No	Yes	Yes	No	No	Yes	No	No	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	No	No	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Not assessed	Not assessed	Yes	Yes	Yes	Yes	Yes	Not assessed	No	Yes	Yes	Yes	Not assessed	No	Yes	No	No	No	No
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 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 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.	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.	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 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 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.	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 has not been assessed.	Der Trend wurde nicht bewertet. Schwellenwert noch nicht regional abgestimmt. Helsinki 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.	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 has not been assessed.	Der Trend wurde nicht bewertet. Schwellenwert noch nicht regional abgestimmt. Helsinki Convention	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.	Der Trend wurde nicht bewertet. In die Bewertung der HELCOM-Becken mit Anteilen deutscher Gewässer sind keine deutschen Daten eingeflossen. Ein Handlungsbedarf ist daher zunächst über ein eigenes Monitoring zu prüfen/ bestätigen.	Der Trend wurde nicht bewertet. In die Bewertung der HELCOM-Becken mit Anteilen deutscher Gewässer sind keine deutschen Daten eingeflossen. Ein Handlungsbedarf ist daher zunächst über ein eigenes Monitoring zu prüfen/ bestätigen.	The trend has not been assessed. Threshold not yet regionalised.	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 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 has not been assessed.	Der Trend wurde nicht bewertet. In die Bewertung der HELCOM-Becken mit Anteilen deutscher Gewässer sind keine deutschen Daten eingeflossen. Ein Handlungsbedarf ist daher zunächst über ein eigenes Monitoring zu prüfen/ bestätigen.
Related indicator				Polyaromatic hydrocarbons (PAH) and their metabolites			Metals (lead, cadmium and mercury)	Metals (lead, cadmium and mercury)		Radioactive substances: Cesium-137 in fish and surface seawater	Radioactive substances: Cesium-137 in fish and surface seawater							Polyaromatic hydrocarbons (PAH) and their metabolites							Metals (lead, cadmium and mercury)	Metals (lead, cadmium and mercury)							PCB, Dioxin and Furan	PCB, Dioxin and Furan						Polyaromatic hydrocarbons (PAH) and their metabolites	Polybrominated diphenyl Ethers (PBDE)	Polybrominated diphenyl Ethers (PBDE)		Hexabromocyclodocecane (HBCDD)	Hexabromocyclodocecane (HBCDD)	Metals (lead, cadmium and mercury)			Perfluorooctane sulphonate (PFOS)		Tributyltin (TBT) and Imposex	Tributyltin (TBT) and Imposex
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
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).
Element status	Good	Good	Not good	Not good	Good	Good	Not good	Not good	Not good	Not good	Not 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	Good	Good	Good	Good	Good	Not good	Not good	Not good	Good	Good	Not good	Not good	Not good	Not good	Not good	Not good	Not good
Description element
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
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.
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
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.
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
Description overall status	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2011-2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2011-2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2011-2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2011-2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2011-2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2011-2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2011-2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2011-2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2011-2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2011-2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2011-2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2011-2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.	Die Bewertung erfolgte entweder nach dem HELCOM State of the Baltic Sea 2018 (Berichtszeit 2011-2016) oder anhand der WRRL-Bewirtschaftungspläne 2015 (Berichtszeitraum 2007-2012). Die hier angegebenen Inhalte gelten für das gesamte Küstenmeer (< 12sm) der deutschen Ostsee. Um die gesamte Fläche abzudecken, wurden die Marine Reporting Units DE-CW_B0.9610 und DE_CW_DEMV_WP_20 mit dem gleichen Inhalt gefüllt.
Assessments period	2007-2016	2007-2016	2007-2016	2007-2016	2007-2016	2007-2016	2007-2016	2007-2016	2007-2016	2007-2016	2007-2016	2007-2016	2007-2016	2007-2016	2007-2016	2007-2016	2007-2016	2007-2016	2007-2016	2007-2016	2007-2016	2007-2016	2007-2016	2007-2016	2007-2016	2007-2016	2007-2016	2007-2016	2007-2016	2007-2016	2007-2016	2007-2016	2007-2016	2007-2016	2007-2016	2007-2016	2007-2016	2007-2016	2007-2016	2007-2016	2007-2016	2007-2016	2007-2016	2007-2016	2007-2016	2007-2016	2007-2016	2007-2016	2007-2016	2007-2016	2007-2016	2007-2016
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
Related targets	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5	UZO2.1 UZO2.2 UZO2.3 UZO2.4 UZO2.5