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

Member State report / Art8 / 2018 / D8 / Sweden / 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	Sweden
Region/subregion	Baltic Sea
Reported by	Havs- och vattenmyndigheten
Report date	2020-07-06
Report access	msfd2018-ART8GES_SE_200706.xml

BAL-SE-AA-B_Alands_hav

Simplified table

GES component	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 - 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	Marine species	Acute pollution events
Element	Anthracene	Cadmium and its compounds	Cesium-137	Copper and its compounds	Fluoranthene	Hexachlorobenzene	Lead and its compounds	Non-dioxin like PCB (sum of 6 PCB: 28, 52, 101, 138, 153 and 180)	Benzo(a)pyrene	Dioxins and dioxin-like compounds (7 PCDDs + 10 PCDFs + 12 PCB-DLs)	Hexabromocyclododecanes (HBCDD)	Mercury and its compounds	Pentabromodiphenylether	Perfluorooctane sulfonic acid (PFOS) and its derivatives	Tributyltin compounds	Haliaeetus albicilla	Haliaeetus albicilla	Haliaeetus albicilla	Monoporeia affinis
Element code	CAS_120-12-7	CAS_7440-43-9	CS002370	CAS_7440-50-8	CAS_206-44-0	CAS_118-74-1	CAS_7439-92-1	SCB6	CAS_50-32-8	EEA_33-58-9	EEA_33-57-8	CAS_7439-97-6	CAS_32534-81-9	CAS_1763-23-1	TBTIN	232053	232053	232053	103077
Element code source	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Contaminants (D8-D9) http://seadatanet.maris2.nl/v_bodc_vocab_v2/vocab_relations.asp?lib=P02	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) 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	Species (D1) http://www.marinespecies.org/	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	EU	EU	HELCOM	EU	EU	EU	EU	EU	EU	EU	EU	EU	EU	EU	EU	HELCOM	HELCOM	HELCOM	HELCOM
Criterion	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C2	D8C2	D8C2	D8C2	D8C3
Parameter	Concentration in sediment	Concentration in sediment	Other	Concentration in sediment	Concentration in sediment	Concentration in biota	Concentration in sediment	Concentration in biota	Concentration in biota	Concentration in biota	Concentration in biota	Concentration in biota	Concentration in biota	Concentration in biota	Concentration in sediment	Other	Other	Other	Other	Other
Parameter other			Concentration in biota (herring)													Brood size	Breeding success	Productivity	proportion of malformed embryos and the proportion of females with more than one malformed embryo	Volume of oil
Threshold value upper	24.0	2.3	2.5	52.0	2000.0	10.0	120.0	75.0	5.0	6.5	167.0	20.0	0.0085	9.1	1.6	1.64	59.0	0.97		0.14
Threshold value lower
Threshold qualitative																			proportion of malformed embryos (threshold 5,9%) and the proportion of females with more than one malformed embryo (threshold 30%)
Threshold value source	National	National	Helsinki Convention	National	National	National	National	National	National	National	National	National	National	National	National	Helsinki Convention	Helsinki Convention	Helsinki Convention	National	Helsinki Convention
Threshold value source other
Value achieved upper	1.4	0.3	4.4397	27.5	42.0		29.0								1.3	1.65	67.96	1.12		0.72
Value achieved lower
Value unit	microgram per kilogram of dry weight	Other	Other	Other	microgram per kilogram of dry weight	microgram per kilogram of wet weight	Other	microgram per kilogram of wet weight	microgram per kilogram of wet weight	microgram per kilogram of wet weight	microgram per kilogram of wet weight	microgram per kilogram of wet weight	microgram per kilogram of wet weight	microgram per kilogram of wet weight	microgram per kilogram of dry weight	Other	percentage	Other		Other
Value unit other		milligram per kilogram of dry weight	Bq kg-1 wet weight	milligram per kilogram of dry weight			milligram per kilogram of dry weight									nestlings		nestlings		m3
Proportion threshold value
Proportion value achieved
Proportion threshold value unit
Trend	Unknown	Unknown	Improving	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Improving
Parameter achieved	Yes	Yes	No	Yes	Yes	Not assessed	Yes	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Yes	Yes	Yes	Yes	Not assessed	No
Description parameter			Concentration in herring, Clupea harengus
Related indicator	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1B Halter av radionuklider/ 8.1B Radionuclides in biota an water	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.2B Produktivitet hos havsörn/ 8.2B Productivity of white-tailed eagles	8.2B Produktivitet hos havsörn/ 8.2B Productivity of white-tailed eagles	8.2B Produktivitet hos havsörn/ 8.2B Productivity of white-tailed eagles	8.2C Störningar i reproduktionen hos vitmärla/ 8.2C Disturbances in the reproduction of Monoporeia affinis	8.3A Volymer av upptäckta olagliga eller olycksrelaterade utsläpp av olja och oljeliknande produkter/ 8.3A Volumes of illegal or accident related emissions of oil and oil-like products detected
Criteria status	Good	Good	Not good	Good	Good	Not assessed	Good	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Good	Good	Good	Good	Not assessed	Not good
Description criteria																			Criteria assessment based on two parameters: proportion of malformed embryos (threshold 5,9%) and the proportion of females with more than one malformed embryo (threshold 30%)
Element status	Good	Good	Not good	Good	Good	Not assessed	Good	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Good	Good	Good	Good	Not assessed
Description element
Integration rule type parameter	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	Not relevant
Integration rule description parameter
Integration rule type criteria	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant
Integration rule description criteria
GES extent threshold	100.00	100.00	100.00	100.00	100.00	100.00	100.00	100.00	100.00	100.00	100.00	100.00	100.00	100.00	100.00
GES extent achieved	83.00	83.00	83.00	83.00	83.00	83.00	83.00	83.00	100.00	100.00	100.00	100.00	100.00	100.00	100.00
GES extent unit	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant
GES achieved	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	Not assessed	Not assessed	Not assessed	Not assessed	GES expected to be achieved later than 2020, Article 14 exception reported
Description overall status	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Indicators under D8C2 are not integrated to criteria level	Indicators under D8C2 are not integrated to criteria level	Indicators under D8C2 are not integrated to criteria level	Indicators under D8C2 are not integrated to criteria level	The national legislation sets down a different assessment level for D8C3. The national legislation may be revised as regard the level of assessment in line with the present reporting.
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
Related pressures	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - 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	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, 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	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt

BAL-SE-AA-B_Arkonahavet_och_S_Oresund

Simplified table

GES component	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 - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Marine species	Acute pollution events
Element	Anthracene	Cadmium and its compounds	Cesium-137	Cesium-137	Cesium-137	Copper and its compounds	Fluoranthene	Hexachlorobenzene	Lead and its compounds	Non-dioxin like PCB (sum of 6 PCB: 28, 52, 101, 138, 153 and 180)	Benzo(a)pyrene	Dioxins and dioxin-like compounds (7 PCDDs + 10 PCDFs + 12 PCB-DLs)	Hexabromocyclododecanes (HBCDD)	Mercury and its compounds	Pentabromodiphenylether	Perfluorooctane sulfonic acid (PFOS) and its derivatives	Tributyltin compounds	Peringia ulvae
Element code	CAS_120-12-7	CAS_7440-43-9	CS002370	CS002370	CS002370	CAS_7440-50-8	CAS_206-44-0	CAS_118-74-1	CAS_7439-92-1	SCB6	CAS_50-32-8	EEA_33-58-9	EEA_33-57-8	CAS_7439-97-6	CAS_32534-81-9	CAS_1763-23-1	TBTIN	151628
Element code source	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Contaminants (D8-D9) http://seadatanet.maris2.nl/v_bodc_vocab_v2/vocab_relations.asp?lib=P02	Contaminants (D8-D9) http://seadatanet.maris2.nl/v_bodc_vocab_v2/vocab_relations.asp?lib=P02	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	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	Species (D1) http://www.marinespecies.org/
Element 2
Element 2 code
Element 2 code source
Element source	EU	EU	HELCOM	HELCOM	HELCOM	EU	EU	EU	EU	EU	EU	EU	EU	EU	EU	EU	EU	HELCOM
Criterion	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C2	D8C3
Parameter	Concentration in sediment	Concentration in sediment	Other	Other	Concentration in water	Concentration in sediment	Concentration in sediment	Concentration in biota	Concentration in sediment	Concentration in biota	Concentration in biota	Concentration in biota	Concentration in biota	Concentration in biota	Concentration in biota	Concentration in biota	Concentration in sediment	Other	Other
Parameter other			Concentration in biota (flatfish)	Concentration in biota (herring)														Imposex	Volume of oil
Threshold value upper	24.0	2.3	2.9	2.5	15.0	52.0	2000.0	10.0	120.0	75.0	5.0	6.5	167.0	20.0	0.0085	9.1	1.6	0.1	7.7
Threshold value lower
Threshold qualitative
Threshold value source	National	National	Helsinki Convention	Helsinki Convention	Helsinki Convention	National	National	National	National	National	National	National	National	National	National	National	National	National	Helsinki Convention
Threshold value source other
Value achieved upper	12.6	0.4	2.721	1.4391384615	26.449430769	23.4	219.0	2.1	79.4	8.3		2.0	1.0	9.9	0.51	0.8	5.5	0.3	5.86
Value achieved lower
Value unit	microgram per kilogram of dry weight	Other	Other	Other	Other	Other	microgram per kilogram of dry weight	microgram per kilogram of wet weight	Other	microgram per kilogram of wet weight	microgram per kilogram of wet weight	microgram per kilogram of wet weight	microgram per kilogram of wet weight	microgram per kilogram of wet weight	microgram per kilogram of wet weight	microgram per kilogram of wet weight	microgram per kilogram of dry weight	Other	Other
Value unit other		milligram per kilogram of dry weight	Bq kg-1	Bq kg-1 wet weight	Bq/m3	milligram per kilogram of dry weight			milligram per kilogram of dry weight									Vas Deferens Sequence Index	m3
Proportion threshold value
Proportion value achieved
Proportion threshold value unit
Trend	Unknown	Unknown	Improving	Improving	Improving	Unknown	Unknown	Stable	Unknown	Stable	Unknown	Stable	Stable	Stable	Stable	Stable	Unknown	Stable	Improving
Parameter achieved	Yes	Yes	Yes	Yes	No	Yes	Yes	Yes	Yes	Yes	Not assessed	Yes	Yes	Yes	No	Yes	No	No	Yes
Description parameter			Concentration in flatfish, Pleuronectes platessa	Concentration in herring, Clupea harengus	Concentrations in seawater			”Stable” trend means that over the last 10 years period generally no significant trends can be seen regarding concentrations of these contaminants in biota.		”Stable” trend means that over the last 10 years period generally no significant trends can be seen regarding concentrations of these contaminants in biota.		Values are TEQ (WHO PCDD/F-PCB). ”Stable” trend means that over the last 10 years period generally no significant trends can be seen regarding concentrations of these contaminants in biota.	”Stable” trend means that over the last 10 years period generally no significant trends can be seen regarding concentrations of these contaminants in biota.	”Stable” trend means that over the last 10 years period generally no significant trends can be seen regarding concentrations of these contaminants in biota.	”Stable” trend means that over the last 10 years period generally no significant trends can be seen regarding concentrations of these contaminants in biota.	”Stable” trend means that over the last 10 years period generally no significant trends can be seen regarding concentrations of these contaminants in biota.		Trend: stable since 2009.
Related indicator	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1B Halter av radionuklider/ 8.1B Radionuclides in biota an water	8.1B Halter av radionuklider/ 8.1B Radionuclides in biota an water	8.1B Halter av radionuklider/ 8.1B Radionuclides in biota an water	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.2A Effekter av organiska tennföreningar på snäckor (imposex)/ 8.2A Effects of organic tin compounds (imposex) on marine snails	8.3A Volymer av upptäckta olagliga eller olycksrelaterade utsläpp av olja och oljeliknande produkter/ 8.3A Volumes of illegal or accident related emissions of oil and oil-like products detected
Criteria status	Good	Good	Not good	Not good	Not good	Good	Good	Good	Good	Good	Not assessed	Good	Good	Good	Not good	Good	Not good	Not good	Good
Description criteria
Element status	Good	Good	Not good	Not good	Not good	Good	Good	Good	Good	Good	Not assessed	Good	Good	Good	Not 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	Not relevant
Integration rule description parameter
Integration rule type criteria	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant
Integration rule description criteria
GES extent threshold	100.00	100.00	100.00	100.00	100.00	100.00	100.00	100.00	100.00	100.00	100.00	100.00	100.00	100.00	100.00	100.00	100.00
GES extent achieved	87.50	87.50	87.50	87.50	87.50	87.50	87.50	87.50	87.50	87.50	66.70	66.70	66.70	66.70	66.70	66.70	66.70
GES extent unit	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Not relevant	Not relevant
GES achieved	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	Not assessed	GES achieved
Description overall status	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Indicators under D8C2 are not integrated to criteria level	The national legislation sets down a different assessment level for D8C3. The national legislation may be revised as regard the level of assessment in line with the present reporting.
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
Related pressures	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - 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	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, 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	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt

BAL-SE-AA-B_Bornholmshavet_och_Hanobukten

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
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 - 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	Marine species	Marine species	Acute pollution events
Element	Anthracene	Cadmium and its compounds	Cesium-137	Cesium-137	Cesium-137	Copper and its compounds	Fluoranthene	Hexachlorobenzene	Lead and its compounds	Non-dioxin like PCB (sum of 6 PCB: 28, 52, 101, 138, 153 and 180)	Benzo(a)pyrene	Dioxins and dioxin-like compounds (7 PCDDs + 10 PCDFs + 12 PCB-DLs)	Hexabromocyclododecanes (HBCDD)	Mercury and its compounds	Pentabromodiphenylether	Perfluorooctane sulfonic acid (PFOS) and its derivatives	Tributyltin compounds	Haliaeetus albicilla	Haliaeetus albicilla	Haliaeetus albicilla	Monoporeia affinis	Peringia ulvae
Element code	CAS_120-12-7	CAS_7440-43-9	CS002370	CS002370	CS002370	CAS_7440-50-8	CAS_206-44-0	CAS_118-74-1	CAS_7439-92-1	SCB6	CAS_50-32-8	EEA_33-58-9	EEA_33-57-8	CAS_7439-97-6	CAS_32534-81-9	CAS_1763-23-1	TBTIN	232053	232053	232053	103077	151628
Element code source	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Contaminants (D8-D9) http://seadatanet.maris2.nl/v_bodc_vocab_v2/vocab_relations.asp?lib=P02	Contaminants (D8-D9) http://seadatanet.maris2.nl/v_bodc_vocab_v2/vocab_relations.asp?lib=P02	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	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	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	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	EU	EU	HELCOM	HELCOM	HELCOM	EU	EU	EU	EU	EU	EU	EU	EU	EU	EU	EU	EU	HELCOM	HELCOM	HELCOM	HELCOM	HELCOM
Criterion	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C2	D8C2	D8C2	D8C2	D8C2	D8C3
Parameter	Concentration in sediment	Concentration in sediment	Other	Other	Concentration in water	Concentration in sediment	Concentration in sediment	Concentration in biota	Concentration in sediment	Concentration in biota	Concentration in biota	Concentration in biota	Concentration in biota	Concentration in biota	Concentration in biota	Concentration in biota	Concentration in sediment	Other	Other	Other	Other	Other	Other
Parameter other			Concentration in biota (flatfish)	Concentration in biota (herring)														Brood size	Breeding success	Productivity	proportion of malformed embryos and the proportion of females with more than one malformed embryo	Imposex	Volume of oil
Threshold value upper	24.0	2.3	2.9	2.5	15.0	52.0	2000.0	10.0	120.0	75.0	5.0	6.5	167.0	20.0	0.0085	9.1	1.6	1.64	59.0	0.97		0.1	2.87
Threshold value lower
Threshold qualitative																					proportion of malformed embryos (threshold 5,9%) and the proportion of females with more than one malformed embryo (threshold 30%)
Threshold value source	National	National	Helsinki Convention	Helsinki Convention	Helsinki Convention	National	National	National	National	National	National	National	National	National	National	National	National	Helsinki Convention	Helsinki Convention	Helsinki Convention	National	National	Helsinki Convention
Threshold value source other
Value achieved upper	6.3	0.9	3.5725454546	4.0583333333	25.829985749	27.1	110.0	1.9	53.1	8.7		1.7	0.8	15.1	0.4	0.7	7.2	1.65	67.96	1.12		0.2	1.45
Value achieved lower
Value unit	microgram per kilogram of dry weight	Other	Other	Other	Other	Other	microgram per kilogram of dry weight	microgram per kilogram of wet weight	Other	microgram per kilogram of wet weight	microgram per kilogram of wet weight	microgram per kilogram of wet weight	microgram per kilogram of wet weight	microgram per kilogram of wet weight	microgram per kilogram of wet weight	microgram per kilogram of wet weight	microgram per kilogram of dry weight	Other	percentage	Other		Other	Other
Value unit other		milligram per kilogram of dry weight	Bq kg-1 wet weight	Bq kg-1 wet weight	Bq/m3	milligram per kilogram of dry weight			milligram per kilogram of dry weight									nestlings		nestlings		Vas Deferens Sequence Index	m3
Proportion threshold value
Proportion value achieved
Proportion threshold value unit
Trend	Unknown	Unknown	Improving	Improving	Improving	Unknown	Unknown	Stable	Unknown	Stable	Unknown	Stable	Stable	Stable	Stable	Stable	Unknown	Unknown	Unknown	Unknown	Unknown	Stable	Improving
Parameter achieved	Yes	Yes	No	No	No	Yes	Yes	Yes	Yes	Yes	Not assessed	Yes	Yes	Yes	No	Yes	No	Yes	Yes	Yes	Not assessed	No	Yes
Description parameter			Concentration in flatfish, Pleuronectes platessa	Concentration in herring, Clupea harengus	Concentrations in seawater			”Stable” trend means that over the last 10 years period generally no significant trends can be seen regarding concentrations of these contaminants in biota.		”Stable” trend means that over the last 10 years period generally no significant trends can be seen regarding concentrations of these contaminants in biota.		Values are TEQ (WHO PCDD/F-PCB). ”Stable” trend means that over the last 10 years period generally no significant trends can be seen regarding concentrations of these contaminants in biota.	”Stable” trend means that over the last 10 years period generally no significant trends can be seen regarding concentrations of these contaminants in biota.	”Stable” trend means that over the last 10 years period generally no significant trends can be seen regarding concentrations of these contaminants in biota.	”Stable” trend means that over the last 10 years period generally no significant trends can be seen regarding concentrations of these contaminants in biota.	”Stable” trend means that over the last 10 years period generally no significant trends can be seen regarding concentrations of these contaminants in biota.						Trend: stable since 2009.
Related indicator	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1B Halter av radionuklider/ 8.1B Radionuclides in biota an water	8.1B Halter av radionuklider/ 8.1B Radionuclides in biota an water	8.1B Halter av radionuklider/ 8.1B Radionuclides in biota an water	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.2B Produktivitet hos havsörn/ 8.2B Productivity of white-tailed eagles	8.2B Produktivitet hos havsörn/ 8.2B Productivity of white-tailed eagles	8.2B Produktivitet hos havsörn/ 8.2B Productivity of white-tailed eagles	8.2C Störningar i reproduktionen hos vitmärla/ 8.2C Disturbances in the reproduction of Monoporeia affinis	8.2A Effekter av organiska tennföreningar på snäckor (imposex)/ 8.2A Effects of organic tin compounds (imposex) on marine snails	8.3A Volymer av upptäckta olagliga eller olycksrelaterade utsläpp av olja och oljeliknande produkter/ 8.3A Volumes of illegal or accident related emissions of oil and oil-like products detected
Criteria status	Good	Good	Not good	Not good	Not good	Good	Good	Good	Good	Good	Not assessed	Good	Good	Good	Not good	Good	Not good	Good	Good	Good	Not assessed	Not good	Good
Description criteria																					Criteria assessment based on two parameters: proportion of malformed embryos (threshold 5,9%) and the proportion of females with more than one malformed embryo (threshold 30%)
Element status	Good	Good	Not good	Not good	Not good	Good	Good	Good	Good	Good	Not assessed	Good	Good	Good	Not good	Good	Not good	Good	Good	Good	Not assessed	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	Not relevant
Integration rule description parameter
Integration rule type criteria	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant
Integration rule description criteria
GES extent threshold	100.00	100.00	100.00	100.00	100.00	100.00	100.00	100.00	100.00	100.00	100.00	100.00	100.00	100.00	100.00	100.00	100.00
GES extent achieved	87.50	87.50	87.50	87.50	87.50	87.50	87.50	87.50	87.50	87.50	66.70	66.70	66.70	66.70	66.70	66.70	66.70
GES extent unit	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant
GES achieved	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	GES achieved
Description overall status	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Indicators under D8C2 are not integrated to criteria level	Indicators under D8C2 are not integrated to criteria level	Indicators under D8C2 are not integrated to criteria level	Indicators under D8C2 are not integrated to criteria level	Indicators under D8C2 are not integrated to criteria level	The national legislation sets down a different assessment level for D8C3. The national legislation may be revised as regard the level of assessment in line with the present reporting.
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
Related pressures	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - 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	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, 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	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt

BAL-SE-AA-B_Bottenhavet

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
Feature	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Marine species	Marine species	Marine species	Marine species	Acute pollution events
Element	Anthracene	Cadmium and its compounds	Cesium-137	Cesium-137	Copper and its compounds	Fluoranthene	Hexachlorobenzene	Lead and its compounds	Non-dioxin like PCB (sum of 6 PCB: 28, 52, 101, 138, 153 and 180)	Benzo(a)pyrene	Dioxins and dioxin-like compounds (7 PCDDs + 10 PCDFs + 12 PCB-DLs)	Hexabromocyclododecanes (HBCDD)	Mercury and its compounds	Pentabromodiphenylether	Perfluorooctane sulfonic acid (PFOS) and its derivatives	Tributyltin compounds	Haliaeetus albicilla	Haliaeetus albicilla	Haliaeetus albicilla	Monoporeia affinis
Element code	CAS_120-12-7	CAS_7440-43-9	CS002370	CS002370	CAS_7440-50-8	CAS_206-44-0	CAS_118-74-1	CAS_7439-92-1	SCB6	CAS_50-32-8	EEA_33-58-9	EEA_33-57-8	CAS_7439-97-6	CAS_32534-81-9	CAS_1763-23-1	TBTIN	232053	232053	232053	103077
Element code source	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Contaminants (D8-D9) http://seadatanet.maris2.nl/v_bodc_vocab_v2/vocab_relations.asp?lib=P02	Contaminants (D8-D9) http://seadatanet.maris2.nl/v_bodc_vocab_v2/vocab_relations.asp?lib=P02	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	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	Species (D1) http://www.marinespecies.org/	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	EU	EU	HELCOM	HELCOM	EU	EU	EU	EU	EU	EU	EU	EU	EU	EU	EU	EU	HELCOM	HELCOM	HELCOM	HELCOM
Criterion	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C2	D8C2	D8C2	D8C2	D8C3
Parameter	Concentration in sediment	Concentration in sediment	Other	Concentration in water	Concentration in sediment	Concentration in sediment	Concentration in biota	Concentration in sediment	Concentration in biota	Concentration in biota	Concentration in biota	Concentration in biota	Concentration in biota	Concentration in biota	Concentration in biota	Concentration in sediment	Other	Other	Other	Other	Other
Parameter other			Concentration in biota (herring)														Productivity	Brood size	Breeding success	proportion of malformed embryos and the proportion of females with more than one malformed embryo	Volume of oil
Threshold value upper	24.0	2.3	2.5	15.0	52.0	2000.0	10.0	120.0	75.0	5.0	6.5	167.0	20.0	0.0085	9.1	1.6	0.97	1.64	59.0		0.19
Threshold value lower
Threshold qualitative																				proportion of malformed embryos (threshold 5,9%) and the proportion of females with more than one malformed embryo (threshold 30%)
Threshold value source	National	National	Helsinki Convention	Helsinki Convention	National	National	National	National	National	National	National	National	National	National	National	National	Helsinki Convention	Helsinki Convention	Helsinki Convention	National	Helsinki Convention
Threshold value source other
Value achieved upper	2.4	0.4	5.8083733333	30.993217391	38.5	51.0	1.8	28.0	7.7		1.83	0.47	27.5	0.46	0.41		1.06	1.55	67.94		0.3
Value achieved lower
Value unit	microgram per kilogram of dry weight	Other	Other	Other	Other	microgram per kilogram of dry weight	microgram per kilogram of wet weight	Other	microgram per kilogram of wet weight	microgram per kilogram of wet weight	microgram per kilogram of wet weight	microgram per kilogram of wet weight	microgram per kilogram of wet weight	microgram per kilogram of wet weight	microgram per kilogram of wet weight	microgram per kilogram of dry weight	Other	Other	percentage		Other
Value unit other		milligram per kilogram of dry weight	Bq kg-1 wet weight	Bq/m3	milligram per kilogram of dry weight			milligram per kilogram of dry weight									nestlings	nestlings			m3
Proportion threshold value
Proportion value achieved
Proportion threshold value unit
Trend	Unknown	Unknown	Improving	Improving	Unknown	Unknown	Stable	Unknown	Stable	Unknown	Stable	Stable	Stable	Stable	Stable	Unknown	Unknown	Unknown	Unknown	Unknown	Improving
Parameter achieved	Yes	Yes	No	No	Yes	Yes	Yes	Yes	Yes	Not assessed	Yes	Yes	No	No	Yes	Unknown	Yes	No	Yes	No	No
Description parameter			Concentration in herring, Clupea harengus	Concentrations in seawater			”Stable” trend means that over the last 10 years period generally no significant trends can be seen regarding concentrations of these contaminants in biota.		”Stable” trend means that over the last 10 years period generally no significant trends can be seen regarding concentrations of these contaminants in biota.		Values are TEQ (WHO PCDD/F-PCB). ”Stable” trend means that over the last 10 years period generally no significant trends can be seen regarding concentrations of these contaminants in biota.	”Stable” trend means that over the last 10 years period generally no significant trends can be seen regarding concentrations of these contaminants in biota.	”Stable” trend means that over the last 10 years period generally no significant trends can be seen regarding concentrations of these contaminants in biota.	”Stable” trend means that over the last 10 years period generally no significant trends can be seen regarding concentrations of these contaminants in biota.	”Stable” trend means that over the last 10 years period generally no significant trends can be seen regarding concentrations of these contaminants in biota.
Related indicator	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1B Halter av radionuklider/ 8.1B Radionuclides in biota an water	8.1B Halter av radionuklider/ 8.1B Radionuclides in biota an water	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.2B Produktivitet hos havsörn/ 8.2B Productivity of white-tailed eagles	8.2B Produktivitet hos havsörn/ 8.2B Productivity of white-tailed eagles	8.2B Produktivitet hos havsörn/ 8.2B Productivity of white-tailed eagles	8.2C Störningar i reproduktionen hos vitmärla/ 8.2C Disturbances in the reproduction of Monoporeia affinis	8.3A Volymer av upptäckta olagliga eller olycksrelaterade utsläpp av olja och oljeliknande produkter/ 8.3A Volumes of illegal or accident related emissions of oil and oil-like products detected
Criteria status	Good	Good	Not good	Not good	Good	Good	Good	Good	Good	Not assessed	Good	Good	Not good	Not good	Good	Unknown	Not good	Not good	Not good	Not good	Not good
Description criteria																				Criteria assessment based on two parameters: proportion of malformed embryos (threshold 5,9%) and the proportion of females with more than one malformed embryo (threshold 30%)
Element status	Good	Good	Not good	Not good	Good	Good	Good	Good	Good	Not assessed	Good	Good	Not good	Not good	Good	Unknown	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	Not relevant
Integration rule description parameter
Integration rule type criteria	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant
Integration rule description criteria
GES extent threshold	100.00	100.00	100.00	100.00	100.00	100.00	100.00	100.00	100.00	100.00	100.00	100.00	100.00	100.00	100.00	100.00
GES extent achieved	87.50	87.50	87.50	87.50	87.50	87.50	87.50	87.50	87.50	60.00	60.00	60.00	60.00	60.00	60.00	60.00
GES extent unit	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant
GES achieved	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	Not assessed	Not assessed	Not assessed	Not assessed	GES expected to be achieved later than 2020, Article 14 exception reported
Description overall status	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Indicators under D8C2 are not integrated to criteria level	Indicators under D8C2 are not integrated to criteria level	Indicators under D8C2 are not integrated to criteria level	Indicators under D8C2 are not integrated to criteria level	The national legislation sets down a different assessment level for D8C3. The national legislation may be revised as regard the level of assessment in line with the present reporting.
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
Related pressures	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - 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	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, 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	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt

BAL-SE-AA-B_Bottenviken

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
Feature	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Marine species	Marine species	Marine species	Marine species	Acute pollution events
Element	Anthracene	Cadmium and its compounds	Cesium-137	Cesium-137	Copper and its compounds	Fluoranthene	Hexachlorobenzene	Lead and its compounds	Non-dioxin like PCB (sum of 6 PCB: 28, 52, 101, 138, 153 and 180)	Benzo(a)pyrene	Dioxins and dioxin-like compounds (7 PCDDs + 10 PCDFs + 12 PCB-DLs)	Hexabromocyclododecanes (HBCDD)	Mercury and its compounds	Pentabromodiphenylether	Perfluorooctane sulfonic acid (PFOS) and its derivatives	Tributyltin compounds	Haliaeetus albicilla	Haliaeetus albicilla	Haliaeetus albicilla	Monoporeia affinis
Element code	CAS_120-12-7	CAS_7440-43-9	CS002370	CS002370	CAS_7440-50-8	CAS_206-44-0	CAS_118-74-1	CAS_7439-92-1	SCB6	CAS_50-32-8	EEA_33-58-9	EEA_33-57-8	CAS_7439-97-6	CAS_32534-81-9	CAS_1763-23-1	TBTIN	232053	232053	232053	103077
Element code source	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Contaminants (D8-D9) http://seadatanet.maris2.nl/v_bodc_vocab_v2/vocab_relations.asp?lib=P02	Contaminants (D8-D9) http://seadatanet.maris2.nl/v_bodc_vocab_v2/vocab_relations.asp?lib=P02	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	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	Species (D1) http://www.marinespecies.org/	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	EU	EU	HELCOM	HELCOM	EU	EU	EU	EU	EU	EU	EU	EU	EU	EU	EU	EU	HELCOM	HELCOM	HELCOM	HELCOM
Criterion	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C2	D8C2	D8C2	D8C2	D8C3
Parameter	Concentration in sediment	Concentration in sediment	Concentration in water	Other	Concentration in sediment	Concentration in sediment	Concentration in biota	Concentration in sediment	Concentration in biota	Concentration in biota	Concentration in biota	Concentration in biota	Concentration in biota	Concentration in biota	Concentration in biota	Concentration in sediment	Other	Other	Other	Other	Other
Parameter other				Concentration in biota (herring)													Breeding success	Brood size	Productivity	proportion of malformed embryos and the proportion of females with more than one malformed embryo	Volume of oil
Threshold value upper	24.0	2.3	15.0	2.5	52.0	2000.0	10.0	120.0	75.0	5.0	6.5	167.0	20.0	0.0085	9.1	1.6	59.0	1.64	0.97		0.11
Threshold value lower
Threshold qualitative																				proportion of malformed embryos (threshold 5,9%) and the proportion of females with more than one malformed embryo (threshold 30%)
Threshold value source	National	National	Helsinki Convention	Helsinki Convention	National	National	National	National	National	National	National	National	National	National	National	National	Helsinki Convention	Helsinki Convention	Helsinki Convention	National	Helsinki Convention
Threshold value source other
Value achieved upper	1.2	1.6	21.082307692	5.2617333333	44.9	22.0	1.2	68.0	5.8		2.4	0.56	30.5	0.51	0.44	1.1	67.93	1.56	1.05		0.29
Value achieved lower
Value unit	microgram per kilogram of dry weight	Other	Other	Other	Other	microgram per kilogram of dry weight	microgram per kilogram of wet weight	Other	microgram per kilogram of wet weight	microgram per kilogram of wet weight	microgram per kilogram of wet weight	microgram per kilogram of wet weight	microgram per kilogram of wet weight	microgram per kilogram of wet weight	microgram per kilogram of wet weight	microgram per kilogram of dry weight	percentage	Other	Other		Other
Value unit other		milligram per kilogram of dry weight	Bq/m3	Bq kg-1 wet weight	milligram per kilogram of dry weight			milligram per kilogram of dry weight										nestlings	nestlings		m3
Proportion threshold value
Proportion value achieved
Proportion threshold value unit
Trend	Unknown	Unknown	Improving	Improving	Unknown	Unknown	Stable	Unknown	Stable	Unknown	Stable	Stable	Stable	Stable	Stable	Unknown	Unknown	Unknown	Unknown	Unknown	Improving
Parameter achieved	Yes	Yes	No	No	Yes	Yes	Yes	Yes	Yes	Not assessed	Yes	Yes	No	No	Yes	Yes	Yes	No	Yes	Not assessed	No
Description parameter			Concentrations in seawater	Concentration in herring, Clupea harengus			”Stable” trend means that over the last 10 years period generally no significant trends can be seen regarding concentrations of these contaminants in biota.		”Stable” trend means that over the last 10 years period generally no significant trends can be seen regarding concentrations of these contaminants in biota.		Values are TEQ (WHO PCDD/F-PCB). ”Stable” trend means that over the last 10 years period generally no significant trends can be seen regarding concentrations of these contaminants in biota.	”Stable” trend means that over the last 10 years period generally no significant trends can be seen regarding concentrations of these contaminants in biota.	”Stable” trend means that over the last 10 years period generally no significant trends can be seen regarding concentrations of these contaminants in biota.	”Stable” trend means that over the last 10 years period generally no significant trends can be seen regarding concentrations of these contaminants in biota.	”Stable” trend means that over the last 10 years period generally no significant trends can be seen regarding concentrations of these contaminants in biota.
Related indicator	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1B Halter av radionuklider/ 8.1B Radionuclides in biota an water	8.1B Halter av radionuklider/ 8.1B Radionuclides in biota an water	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.2B Produktivitet hos havsörn/ 8.2B Productivity of white-tailed eagles	8.2B Produktivitet hos havsörn/ 8.2B Productivity of white-tailed eagles	8.2B Produktivitet hos havsörn/ 8.2B Productivity of white-tailed eagles	8.2C Störningar i reproduktionen hos vitmärla/ 8.2C Disturbances in the reproduction of Monoporeia affinis	8.3A Volymer av upptäckta olagliga eller olycksrelaterade utsläpp av olja och oljeliknande produkter/ 8.3A Volumes of illegal or accident related emissions of oil and oil-like products detected
Criteria status	Good	Good	Not good	Not good	Good	Good	Good	Good	Good	Not assessed	Good	Good	Not good	Not good	Good	Good	Not good	Not good	Not good	Not assessed	Not good
Description criteria																				Criteria assessment based on two parameters: proportion of malformed embryos (threshold 5,9%) and the proportion of females with more than one malformed embryo (threshold 30%)
Element status	Good	Good	Not good	Not good	Good	Good	Good	Good	Good	Not assessed	Good	Good	Not good	Not good	Good	Good	Not good	Not good	Not good	Not assessed
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	Not relevant
Integration rule description parameter
Integration rule type criteria	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant
Integration rule description criteria
GES extent threshold	100.00	100.00	100.00	100.00	100.00	100.00	100.00	100.00	100.00	100.00	100.00	100.00	100.00	100.00	100.00	100.00
GES extent achieved	87.50	87.50	87.50	87.50	87.50	87.50	87.50	87.50	87.50	66.70	66.70	66.70	66.70	66.70	66.70	66.70
GES extent unit	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant
GES achieved	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	Not assessed	Not assessed	Not assessed	Not assessed	GES expected to be achieved later than 2020, Article 14 exception reported
Description overall status	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Indicators under D8C2 are not integrated to criteria level	Indicators under D8C2 are not integrated to criteria level	Indicators under D8C2 are not integrated to criteria level	Indicators under D8C2 are not integrated to criteria level	The national legislation sets down a different assessment level for D8C3. The national legislation may be revised as regard the level of assessment in line with the present reporting.
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
Related pressures	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - 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	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, 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	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt

BAL-SE-AA-B_N_Gotlandshavet

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
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 - 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	Marine species	Marine species	Acute pollution events
Element	Anthracene	Cadmium and its compounds	Cesium-137	Copper and its compounds	Fluoranthene	Hexachlorobenzene	Lead and its compounds	Non-dioxin like PCB (sum of 6 PCB: 28, 52, 101, 138, 153 and 180)	Benzo(a)pyrene	Dioxins and dioxin-like compounds (7 PCDDs + 10 PCDFs + 12 PCB-DLs)	Hexabromocyclododecanes (HBCDD)	Mercury and its compounds	Pentabromodiphenylether	Perfluorooctane sulfonic acid (PFOS) and its derivatives	Tributyltin compounds	Haliaeetus albicilla	Haliaeetus albicilla	Haliaeetus albicilla	Monoporeia affinis	Peringia ulvae
Element code	CAS_120-12-7	CAS_7440-43-9	CS002370	CAS_7440-50-8	CAS_206-44-0	CAS_118-74-1	CAS_7439-92-1	SCB6	CAS_50-32-8	EEA_33-58-9	EEA_33-57-8	CAS_7439-97-6	CAS_32534-81-9	CAS_1763-23-1	TBTIN	232053	232053	232053	103077	151628
Element code source	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Contaminants (D8-D9) http://seadatanet.maris2.nl/v_bodc_vocab_v2/vocab_relations.asp?lib=P02	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) 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	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	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	EU	EU	HELCOM	EU	EU	EU	EU	EU	EU	EU	EU	EU	EU	EU	EU	HELCOM	HELCOM	HELCOM	HELCOM	HELCOM
Criterion	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C2	D8C2	D8C2	D8C2	D8C2	D8C3
Parameter	Concentration in sediment	Concentration in sediment	Concentration in water	Concentration in sediment	Concentration in sediment	Concentration in biota	Concentration in sediment	Concentration in biota	Concentration in biota	Concentration in biota	Concentration in biota	Concentration in biota	Concentration in biota	Concentration in biota	Concentration in sediment	Other	Other	Other	Other	Other	Other
Parameter other																Productivity	Brood size	Breeding success	proportion of malformed embryos and the proportion of females with more than one malformed embryo	Imposex	Volume of oil
Threshold value upper	24.0	2.3	15.0	52.0	2000.0	10.0	120.0	75.0	5.0	6.5	167.0	20.0	0.0085	9.1	1.6	0.97	1.64	59.0		0.1	14.31
Threshold value lower
Threshold qualitative																			proportion of malformed embryos (threshold 5,9%) and the proportion of females with more than one malformed embryo (threshold 30%)
Threshold value source	National	National	Helsinki Convention	National	National	National	National	National	National	National	National	National	National	National	National	Helsinki Convention	Helsinki Convention	Helsinki Convention	National	National	Helsinki Convention
Threshold value source other
Value achieved upper	1.0	1.9	26.879071429	26.4	30.0	0.6	26.0	15.5		2.1	0.21	35.4	0.34	0.99	3.0	1.12	1.65	67.96		0.3	1.67
Value achieved lower
Value unit	microgram per kilogram of dry weight	Other	Other	Other	microgram per kilogram of dry weight	microgram per kilogram of wet weight	Other	microgram per kilogram of wet weight	microgram per kilogram of wet weight	microgram per kilogram of wet weight	microgram per kilogram of wet weight	microgram per kilogram of wet weight	microgram per kilogram of wet weight	microgram per kilogram of wet weight	microgram per kilogram of dry weight	Other	Other	percentage		Other	Other
Value unit other		milligram per kilogram of dry weight	Bq/m3	milligram per kilogram of dry weight			milligram per kilogram of dry weight									nestlings	nestlings			Vas Deferens Sequence Index	m3
Proportion threshold value
Proportion value achieved
Proportion threshold value unit
Trend	Unknown	Unknown	Improving	Unknown	Unknown	Stable	Unknown	Stable	Unknown	Stable	Stable	Stable	Stable	Stable	Unknown	Unknown	Unknown	Unknown	Unknown	Stable	Improving
Parameter achieved	Yes	Yes	No	Yes	Yes	Yes	Yes	Yes	Not assessed	Yes	Yes	No	No	Yes	No	Yes	Yes	Yes	No	No	Yes
Description parameter			Concentrations in seawater			”Stable” trend means that over the last 10 years period generally no significant trends can be seen regarding concentrations of these contaminants in biota.		”Stable” trend means that over the last 10 years period generally no significant trends can be seen regarding concentrations of these contaminants in biota.		Values are TEQ (WHO PCDD/F-PCB). ”Stable” trend means that over the last 10 years period generally no significant trends can be seen regarding concentrations of these contaminants in biota.	”Stable” trend means that over the last 10 years period generally no significant trends can be seen regarding concentrations of these contaminants in biota.	”Stable” trend means that over the last 10 years period generally no significant trends can be seen regarding concentrations of these contaminants in biota.	”Stable” trend means that over the last 10 years period generally no significant trends can be seen regarding concentrations of these contaminants in biota.	”Stable” trend means that over the last 10 years period generally no significant trends can be seen regarding concentrations of these contaminants in biota.						Trend: stable since 2009.
Related indicator	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1B Halter av radionuklider/ 8.1B Radionuclides in biota an water	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.2B Produktivitet hos havsörn/ 8.2B Productivity of white-tailed eagles	8.2B Produktivitet hos havsörn/ 8.2B Productivity of white-tailed eagles	8.2B Produktivitet hos havsörn/ 8.2B Productivity of white-tailed eagles	8.2C Störningar i reproduktionen hos vitmärla/ 8.2C Disturbances in the reproduction of Monoporeia affinis	8.2A Effekter av organiska tennföreningar på snäckor (imposex)/ 8.2A Effects of organic tin compounds (imposex) on marine snails	8.3A Volymer av upptäckta olagliga eller olycksrelaterade utsläpp av olja och oljeliknande produkter/ 8.3A Volumes of illegal or accident related emissions of oil and oil-like products detected
Criteria status	Good	Good	Not good	Good	Good	Good	Good	Good	Not assessed	Good	Good	Not good	Not good	Good	Not good	Good	Good	Good	Not good	Not good	Good
Description criteria																			Criteria assessment based on two parameters: proportion of malformed embryos (threshold 5,9%) and the proportion of females with more than one malformed embryo (threshold 30%)
Element status	Good	Good	Not good	Good	Good	Good	Good	Good	Not assessed	Good	Good	Not good	Not good	Good	Not good	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	Not relevant
Integration rule description parameter
Integration rule type criteria	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant
Integration rule description criteria
GES extent threshold	100.00	100.00	100.00	100.00	100.00	100.00	100.00	100.00	100.00	100.00	100.00	100.00	100.00	100.00	100.00
GES extent achieved	87.50	87.50	87.50	87.50	87.50	87.50	87.50	87.50	50.00	50.00	50.00	50.00	50.00	50.00	50.00
GES extent unit	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant
GES achieved	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	GES achieved
Description overall status	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Indicators under D8C2 are not integrated to criteria level	Indicators under D8C2 are not integrated to criteria level	Indicators under D8C2 are not integrated to criteria level	Indicators under D8C2 are not integrated to criteria level	Indicators under D8C2 are not integrated to criteria level	The national legislation sets down a different assessment level for D8C3. The national legislation may be revised as regard the level of assessment in line with the present reporting.
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
Related pressures	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - 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	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, 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	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt

BAL-SE-AA-B_N_Kvarken

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
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 - 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	Marine species	Marine species	Marine species	Marine species	Acute pollution events
Element	Anthracene	Cadmium and its compounds	Cesium-137	Copper and its compounds	Fluoranthene	Hexachlorobenzene	Lead and its compounds	Non-dioxin like PCB (sum of 6 PCB: 28, 52, 101, 138, 153 and 180)	Benzo(a)pyrene	Dioxins and dioxin-like compounds (7 PCDDs + 10 PCDFs + 12 PCB-DLs)	Hexabromocyclododecanes (HBCDD)	Mercury and its compounds	Pentabromodiphenylether	Perfluorooctane sulfonic acid (PFOS) and its derivatives	Tributyltin compounds	Haliaeetus albicilla	Haliaeetus albicilla	Haliaeetus albicilla	Monoporeia affinis	Zoarces viviparus	Zoarces viviparus	Zoarces viviparus
Element code	CAS_120-12-7	CAS_7440-43-9	CS002370	CAS_7440-50-8	CAS_206-44-0	CAS_118-74-1	CAS_7439-92-1	SCB6	CAS_50-32-8	EEA_33-58-9	EEA_33-57-8	CAS_7439-97-6	CAS_32534-81-9	CAS_1763-23-1	TBTIN	232053	232053	232053	103077	127123	127123	127123
Element code source	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Contaminants (D8-D9) http://seadatanet.maris2.nl/v_bodc_vocab_v2/vocab_relations.asp?lib=P02	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) 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	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	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	EU	EU	HELCOM	EU	EU	EU	EU	EU	EU	EU	EU	EU	EU	EU	EU	HELCOM	HELCOM	HELCOM	HELCOM	National	National	National
Criterion	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C2	D8C2	D8C2	D8C2	D8C2	D8C2	D8C2	D8C3
Parameter	Concentration in sediment	Concentration in sediment	Other	Concentration in sediment	Concentration in sediment	Concentration in biota	Concentration in sediment	Concentration in biota	Concentration in biota	Concentration in biota	Concentration in biota	Concentration in biota	Concentration in biota	Concentration in biota	Concentration in sediment	Other	Other	Other	Other	Other	Other	Other	Other
Parameter other			Concentration in biota (herring)													Brood size	Productivity	Breeding success	proportion of malformed embryos and the proportion of females with more than one malformed embryo	Proportion of malformed fry	Proportion of early dead fry	Proportion of late dead fry	Volume of oil
Threshold value upper	24.0	2.3	2.5	52.0	2000.0	10.0	120.0	75.0	5.0	6.5	167.0	20.0	0.0085	9.1	1.6	1.64	0.97	59.0		2.0	5.0	4.0	0.0007
Threshold value lower
Threshold qualitative																			proportion of malformed embryos (threshold 5,9%) and the proportion of females with more than one malformed embryo (threshold 30%)
Threshold value source	National	National	Helsinki Convention	National	National	National	National	National	National	National	National	National	National	National	National	Helsinki Convention	Helsinki Convention	Helsinki Convention	National	National	National	National	Helsinki Convention
Threshold value source other
Value achieved upper			5.2647					5.5		1.3	0.2	22.0	2.7	0.24		1.56	1.06	67.94					0.05
Value achieved lower
Value unit	microgram per kilogram of wet weight	Other	Other	Other	microgram per kilogram of wet weight	microgram per kilogram of wet weight	Other	microgram per kilogram of wet weight	microgram per kilogram of wet weight	microgram per kilogram of wet weight	microgram per kilogram of wet weight	microgram per kilogram of wet weight	microgram per kilogram of wet weight	microgram per kilogram of wet weight	microgram per kilogram of dry weight	Other	Other	percentage		percentage	percentage	percentage	Other
Value unit other		milligram per kilogram of dry weight	Bq kg-1 wet weight	milligram per kilogram of dry weight			milligram per kilogram of dry weight									nestlings	nestlings						m3
Proportion threshold value
Proportion value achieved
Proportion threshold value unit
Trend	Unknown	Unknown	Improving	Unknown	Unknown	Unknown	Unknown	Stable	Unknown	Stable	Stable	Stable	Stable	Stable	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Improving
Parameter achieved	Not assessed	Not assessed	No	Not assessed	Not assessed	Not assessed	Not assessed	Yes	Not assessed	Yes	Yes	No	No	Yes	Not assessed	No	Yes	Yes	No	Yes	Yes	Yes	No
Description parameter			Concentration in herring, Clupea harengus					”Stable” trend means that over the last 10 years period generally no significant trends can be seen regarding concentrations of these contaminants in biota.		Values are TEQ (WHO PCDD/F-PCB). ”Stable” trend means that over the last 10 years period generally no significant trends can be seen regarding concentrations of these contaminants in biota.	”Stable” trend means that over the last 10 years period generally no significant trends can be seen regarding concentrations of these contaminants in biota.	”Stable” trend means that over the last 10 years period generally no significant trends can be seen regarding concentrations of these contaminants in biota.	”Stable” trend means that over the last 10 years period generally no significant trends can be seen regarding concentrations of these contaminants in biota.	”Stable” trend means that over the last 10 years period generally no significant trends can be seen regarding concentrations of these contaminants in biota.						The national legislation sets down a different assessment level for fry malformations in eelpout, indicator 8.2D, under criterion D8C2. The national legislation may be revised as regard the level of assessment in line with the present reporting.	The national legislation sets down a different assessment level for fry malformations in eelpout, indicator 8.2D, under criterion D8C2. The national legislation may be revised as regard the level of assessment in line with the present reporting.	The national legislation sets down a different assessment level for fry malformations in eelpout, indicator 8.2D, under criterion D8C2. The national legislation may be revised as regard the level of assessment in line with the present reporting.
Related indicator	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1B Halter av radionuklider/ 8.1B Radionuclides in biota an water	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.2B Produktivitet hos havsörn/ 8.2B Productivity of white-tailed eagles	8.2B Produktivitet hos havsörn/ 8.2B Productivity of white-tailed eagles	8.2B Produktivitet hos havsörn/ 8.2B Productivity of white-tailed eagles	8.2C Störningar i reproduktionen hos vitmärla/ 8.2C Disturbances in the reproduction of Monoporeia affinis	8.2D Störningar i reproduktionen hos tånglake/ 8.2D Disturbances in the reproduction of eelpout	8.2D Störningar i reproduktionen hos tånglake/ 8.2D Disturbances in the reproduction of eelpout	8.2D Störningar i reproduktionen hos tånglake/ 8.2D Disturbances in the reproduction of eelpout	8.3A Volymer av upptäckta olagliga eller olycksrelaterade utsläpp av olja och oljeliknande produkter/ 8.3A Volumes of illegal or accident related emissions of oil and oil-like products detected
Criteria status	Not assessed	Not assessed	Not good	Not assessed	Not assessed	Not assessed	Not assessed	Good	Not assessed	Good	Good	Not good	Not good	Good	Not assessed	Not good	Not good	Not good	Not good	Good	Good	Good	Not good
Description criteria																			Criteria assessment based on two parameters: proportion of malformed embryos (threshold 5,9%) and the proportion of females with more than one malformed embryo (threshold 30%)
Element status	Not assessed	Not assessed	Not good	Not assessed	Not assessed	Not assessed	Not assessed	Good	Not assessed	Good	Good	Not good	Not good	Good	Not assessed	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	Not relevant
Integration rule description parameter
Integration rule type criteria	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant
Integration rule description criteria
GES extent threshold	100.00	100.00	100.00	100.00	100.00	100.00	100.00	100.00	100.00	100.00	100.00	100.00	100.00	100.00	100.00
GES extent achieved	50.00	50.00	50.00	50.00	50.00	50.00	50.00	50.00	60.00	60.00	60.00	60.00	60.00	60.00	60.00
GES extent unit	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant
GES achieved	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	GES expected to be achieved later than 2020, Article 14 exception reported
Description overall status	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Indicators under D8C2 are not integrated to criteria level	Indicators under D8C2 are not integrated to criteria level	Indicators under D8C2 are not integrated to criteria level	Indicators under D8C2 are not integrated to criteria level	Indicators under D8C2 are not integrated to criteria level	Indicators under D8C2 are not integrated to criteria level	Indicators under D8C2 are not integrated to criteria level	The national legislation sets down a different assessment level for D8C3. The national legislation may be revised as regard the level of assessment in line with the present reporting.
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
Related pressures	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - 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	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, 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	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt

BAL-SE-AA-B_O_Gotlandshavet

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
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 - 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	Marine species	Marine species	Acute pollution events
Element	Anthracene	Cadmium and its compounds	Cesium-137	Cesium-137	Cesium-137	Copper and its compounds	Fluoranthene	Hexachlorobenzene	Lead and its compounds	Non-dioxin like PCB (sum of 6 PCB: 28, 52, 101, 138, 153 and 180)	Benzo(a)pyrene	Dioxins and dioxin-like compounds (7 PCDDs + 10 PCDFs + 12 PCB-DLs)	Hexabromocyclododecanes (HBCDD)	Mercury and its compounds	Pentabromodiphenylether	Perfluorooctane sulfonic acid (PFOS) and its derivatives	Tributyltin compounds	Haliaeetus albicilla	Haliaeetus albicilla	Haliaeetus albicilla	Monoporeia affinis	Peringia ulvae
Element code	CAS_120-12-7	CAS_7440-43-9	CS002370	CS002370	CS002370	CAS_7440-50-8	CAS_206-44-0	CAS_118-74-1	CAS_7439-92-1	SCB6	CAS_50-32-8	EEA_33-58-9	EEA_33-57-8	CAS_7439-97-6	CAS_32534-81-9	CAS_1763-23-1	TBTIN	232053	232053	232053	103077	151628
Element code source	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Contaminants (D8-D9) http://seadatanet.maris2.nl/v_bodc_vocab_v2/vocab_relations.asp?lib=P02	Contaminants (D8-D9) http://seadatanet.maris2.nl/v_bodc_vocab_v2/vocab_relations.asp?lib=P02	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	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	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	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	EU	EU	HELCOM	HELCOM	HELCOM	EU	EU	EU	EU	EU	EU	EU	EU	EU	EU	EU	EU	HELCOM	HELCOM	HELCOM	HELCOM	HELCOM
Criterion	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C2	D8C2	D8C2	D8C2	D8C2	D8C3
Parameter	Concentration in sediment	Concentration in sediment	Concentration in water	Other	Other	Concentration in sediment	Concentration in sediment	Concentration in biota	Concentration in sediment	Concentration in biota	Concentration in biota	Concentration in biota	Concentration in biota	Concentration in biota	Concentration in biota	Concentration in biota	Concentration in sediment	Other	Other	Other	Other	Other	Other
Parameter other				Concentration in biota (flatfish)	Concentration in biota (herring)													Productivity	Brood size	Breeding success	proportion of malformed embryos and the proportion of females with more than one malformed embryo	Imposex	Volume of oil
Threshold value upper	24.0	2.3	15.0	2.9	2.5	52.0	2000.0	10.0	120.0	75.0	5.0	6.5	167.0	20.0	0.0085	9.1	1.6	0.97	1.64	59.0		0.1	1.85
Threshold value lower
Threshold qualitative																					proportion of malformed embryos (threshold 5,9%) and the proportion of females with more than one malformed embryo (threshold 30%)
Threshold value source	National	National	Helsinki Convention	Helsinki Convention	Helsinki Convention	National	National	National	National	National	National	National	National	National	National	National	National	Helsinki Convention	Helsinki Convention	Helsinki Convention	National	National	Helsinki Convention
Threshold value source other
Value achieved upper	1.9	3.6	28.666023553	3.8266666667	3.60125	35.2	40.0	1.8	25.0	10.7		2.6	1.0	30.4	0.65	0.5	11.1	1.12	1.65	67.96			2.41
Value achieved lower
Value unit	microgram per kilogram of dry weight	Other	Other	Other	Other	Other	microgram per kilogram of dry weight	microgram per kilogram of wet weight	Other	microgram per kilogram of wet weight	microgram per kilogram of wet weight	microgram per kilogram of wet weight	microgram per kilogram of wet weight	microgram per kilogram of wet weight	microgram per kilogram of wet weight	microgram per kilogram of wet weight	microgram per kilogram of dry weight	Other	Other	percentage		Other	Other
Value unit other		milligram per kilogram of dry weight	Bq/m3	Bq kg-1	Bq kg-1 wet weight	milligram per kilogram of dry weight			milligram per kilogram of dry weight									nestlings	nestlings			Vas Deferens Sequence Index	m3
Proportion threshold value
Proportion value achieved
Proportion threshold value unit
Trend	Unknown	Unknown	Improving	Improving	Improving	Unknown	Unknown	Stable	Unknown	Stable	Unknown	Stable	Stable	Stable	Stable	Stable	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Improving
Parameter achieved	Yes	No	No	No	No	Yes	Yes	Yes	Yes	Yes	Not assessed	Yes	Yes	No	No	Yes	No	Yes	Yes	Yes	Not assessed	Not assessed	No
Description parameter			Concentrations in seawater	Concentration in flatfish, Pleuronectes platessa	Concentration in herring, Clupea harengus			”Stable” trend means that over the last 10 years period generally no significant trends can be seen regarding concentrations of these contaminants in biota.		”Stable” trend means that over the last 10 years period generally no significant trends can be seen regarding concentrations of these contaminants in biota.		Values are TEQ (WHO PCDD/F-PCB). ”Stable” trend means that over the last 10 years period generally no significant trends can be seen regarding concentrations of these contaminants in biota.	”Stable” trend means that over the last 10 years period generally no significant trends can be seen regarding concentrations of these contaminants in biota.	”Stable” trend means that over the last 10 years period generally no significant trends can be seen regarding concentrations of these contaminants in biota.	”Stable” trend means that over the last 10 years period generally no significant trends can be seen regarding concentrations of these contaminants in biota.	”Stable” trend means that over the last 10 years period generally no significant trends can be seen regarding concentrations of these contaminants in biota.
Related indicator	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1B Halter av radionuklider/ 8.1B Radionuclides in biota an water	8.1B Halter av radionuklider/ 8.1B Radionuclides in biota an water	8.1B Halter av radionuklider/ 8.1B Radionuclides in biota an water	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.2B Produktivitet hos havsörn/ 8.2B Productivity of white-tailed eagles	8.2B Produktivitet hos havsörn/ 8.2B Productivity of white-tailed eagles	8.2B Produktivitet hos havsörn/ 8.2B Productivity of white-tailed eagles	8.2C Störningar i reproduktionen hos vitmärla/ 8.2C Disturbances in the reproduction of Monoporeia affinis	8.2A Effekter av organiska tennföreningar på snäckor (imposex)/ 8.2A Effects of organic tin compounds (imposex) on marine snails	8.3A Volymer av upptäckta olagliga eller olycksrelaterade utsläpp av olja och oljeliknande produkter/ 8.3A Volumes of illegal or accident related emissions of oil and oil-like products detected
Criteria status	Good	Not good	Not good	Not good	Not good	Good	Good	Good	Good	Good	Not assessed	Good	Good	Not good	Not good	Good	Not good	Good	Good	Good	Not assessed	Not assessed	Not good
Description criteria																					Criteria assessment based on two parameters: proportion of malformed embryos (threshold 5,9%) and the proportion of females with more than one malformed embryo (threshold 30%)
Element status	Good	Not good	Not good	Not good	Not good	Good	Good	Good	Good	Good	Not assessed	Good	Good	Not good	Not good	Good	Not good	Good	Good	Good	Not assessed	Not assessed
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	Not relevant
Integration rule description parameter
Integration rule type criteria	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant
Integration rule description criteria
GES extent threshold	100.00	100.00	100.00	100.00	100.00	100.00	100.00	100.00	100.00	100.00	100.00	100.00	100.00	100.00	100.00	100.00	100.00
GES extent achieved	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	50.00	50.00	50.00	50.00	50.00	50.00	50.00
GES extent unit	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant
GES achieved	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	GES expected to be achieved later than 2020, Article 14 exception reported
Description overall status	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Indicators under D8C2 are not integrated to criteria level	Indicators under D8C2 are not integrated to criteria level	Indicators under D8C2 are not integrated to criteria level	Indicators under D8C2 are not integrated to criteria level	Indicators under D8C2 are not integrated to criteria level	The national legislation sets down a different assessment level for D8C3. The national legislation may be revised as regard the level of assessment in line with the present reporting.
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
Related pressures	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - 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	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, 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	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt

BAL-SE-AA-B_V_Gotlandshavet

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
Feature	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Contaminants - UPBT substances	Marine species	Marine species	Marine species	Marine species	Marine species	Marine species	Marine species	Marine species	Acute pollution events
Element	Anthracene	Cadmium and its compounds	Cesium-137	Cesium-137	Copper and its compounds	Fluoranthene	Hexachlorobenzene	Lead and its compounds	Non-dioxin like PCB (sum of 6 PCB: 28, 52, 101, 138, 153 and 180)	Benzo(a)pyrene	Dioxins and dioxin-like compounds (7 PCDDs + 10 PCDFs + 12 PCB-DLs)	Hexabromocyclododecanes (HBCDD)	Mercury and its compounds	Pentabromodiphenylether	Perfluorooctane sulfonic acid (PFOS) and its derivatives	Tributyltin compounds	Haliaeetus albicilla	Haliaeetus albicilla	Haliaeetus albicilla	Monoporeia affinis	Peringia ulvae	Zoarces viviparus	Zoarces viviparus	Zoarces viviparus
Element code	CAS_120-12-7	CAS_7440-43-9	CS002370	CS002370	CAS_7440-50-8	CAS_206-44-0	CAS_118-74-1	CAS_7439-92-1	SCB6	CAS_50-32-8	EEA_33-58-9	EEA_33-57-8	CAS_7439-97-6	CAS_32534-81-9	CAS_1763-23-1	TBTIN	232053	232053	232053	103077	151628	127123	127123	127123
Element code source	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Contaminants (D8-D9) http://seadatanet.maris2.nl/v_bodc_vocab_v2/vocab_relations.asp?lib=P02	Contaminants (D8-D9) http://seadatanet.maris2.nl/v_bodc_vocab_v2/vocab_relations.asp?lib=P02	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view	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	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	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	EU	EU	HELCOM	HELCOM	EU	EU	EU	EU	EU	EU	EU	EU	EU	EU	EU	EU	HELCOM	HELCOM	HELCOM	HELCOM	HELCOM	National	National	National
Criterion	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C2	D8C2	D8C2	D8C2	D8C2	D8C2	D8C2	D8C2	D8C3
Parameter	Concentration in sediment	Concentration in sediment	Concentration in water	Other	Concentration in sediment	Concentration in sediment	Concentration in biota	Concentration in sediment	Concentration in biota	Concentration in biota	Concentration in biota	Concentration in biota	Concentration in biota	Concentration in biota	Concentration in biota	Concentration in sediment	Other	Other	Other	Other	Other	Other	Other	Other	Other
Parameter other				Concentration in biota (herring)													Brood size	Breeding success	Productivity	proportion of malformed embryos and the proportion of females with more than one malformed embryo	Imposex	Proportion of late dead fry	Proportion of early dead fry	Proportion of malformed fry	Volume of oil
Threshold value upper	24.0	2.3	15.0	2.5	52.0	2000.0	10.0	120.0	75.0	5.0	6.5	167.0	20.0	0.0085	9.1	1.6	1.64	59.0	0.97		0.1	4.0	5.0	2.0	0.23
Threshold value lower
Threshold qualitative																				proportion of malformed embryos (threshold 5,9%) and the proportion of females with more than one malformed embryo (threshold 30%)
Threshold value source	National	National	Helsinki Convention	Helsinki Convention	National	National	National	National	National	National	National	National	National	National	National	National	Helsinki Convention	Helsinki Convention	Helsinki Convention	National	National	National	National	National	Helsinki Convention
Threshold value source other
Value achieved upper	2.4	3.5	27.23	3.85	34.6	50.0	1.65	29.0	6.5	0.2	2.4	0.71	18.1	0.4	0.7	10.5	1.65	67.96	1.12		0.3				0.44
Value achieved lower
Value unit	microgram per kilogram of dry weight	Other	Other	Other	Other	microgram per kilogram of dry weight	microgram per kilogram of wet weight	Other	microgram per kilogram of wet weight	microgram per kilogram of wet weight	microgram per kilogram of wet weight	microgram per kilogram of wet weight	microgram per kilogram of wet weight	microgram per kilogram of wet weight	microgram per kilogram of wet weight	microgram per kilogram of dry weight	Other	percentage	Other		Other	percentage	percentage	percentage	Other
Value unit other		milligram per kilogram of dry weight	Bq/m3	Bq kg-1 wet weight	milligram per kilogram of dry weight			milligram per kilogram of dry weight									nestlings		nestlings		Vas Deferens Sequence Index				m3
Proportion threshold value
Proportion value achieved
Proportion threshold value unit
Trend	Unknown	Unknown	Improving	Improving	Unknown	Unknown	Stable	Unknown	Unknown	Stable	Stable	Stable	Stable	Stable	Stable	Unknown	Unknown	Unknown	Unknown	Unknown	Stable	Unknown	Unknown	Unknown	Improving
Parameter achieved	Yes	No	No	No	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	Yes	No	Yes	No	Yes	Yes	Yes	Yes	No	Yes	Yes	Yes	No
Description parameter			Concentrations in seawater	Concentration in herring, Clupea harengus			”Stable” trend means that over the last 10 years period generally no significant trends can be seen regarding concentrations of these contaminants in biota.		”Stable” trend means that over the last 10 years period generally no significant trends can be seen regarding concentrations of these contaminants in biota.	”Stable” trend means that over the last 10 years period generally no significant trends can be seen regarding concentrations of these contaminants in biota.	Values are TEQ (WHO PCDD/F-PCB). ”Stable” trend means that over the last 10 years period generally no significant trends can be seen regarding concentrations of these contaminants in biota.	”Stable” trend means that over the last 10 years period generally no significant trends can be seen regarding concentrations of these contaminants in biota.	”Stable” trend means that over the last 10 years period generally no significant trends can be seen regarding concentrations of these contaminants in biota.	”Stable” trend means that over the last 10 years period generally no significant trends can be seen regarding concentrations of these contaminants in biota.	”Stable” trend means that over the last 10 years period generally no significant trends can be seen regarding concentrations of these contaminants in biota.						Trend: stable since 2009.	The national legislation sets down a different assessment level for fry malformations in eelpout, indicator 8.2D, under criterion D8C2. The national legislation may be revised as regard the level of assessment in line with the present reporting.	The national legislation sets down a different assessment level for fry malformations in eelpout, indicator 8.2D, under criterion D8C2. The national legislation may be revised as regard the level of assessment in line with the present reporting.	The national legislation sets down a different assessment level for fry malformations in eelpout, indicator 8.2D, under criterion D8C2. The national legislation may be revised as regard the level of assessment in line with the present reporting.
Related indicator	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1B Halter av radionuklider/ 8.1B Radionuclides in biota an water	8.1B Halter av radionuklider/ 8.1B Radionuclides in biota an water	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.1A Halter av farliga ämnen/ 8.1A Concentrations of hazardous substances	8.2B Produktivitet hos havsörn/ 8.2B Productivity of white-tailed eagles	8.2B Produktivitet hos havsörn/ 8.2B Productivity of white-tailed eagles	8.2B Produktivitet hos havsörn/ 8.2B Productivity of white-tailed eagles	8.2C Störningar i reproduktionen hos vitmärla/ 8.2C Disturbances in the reproduction of Monoporeia affinis	8.2A Effekter av organiska tennföreningar på snäckor (imposex)/ 8.2A Effects of organic tin compounds (imposex) on marine snails	8.2D Störningar i reproduktionen hos tånglake/ 8.2D Disturbances in the reproduction of eelpout	8.2D Störningar i reproduktionen hos tånglake/ 8.2D Disturbances in the reproduction of eelpout	8.2D Störningar i reproduktionen hos tånglake/ 8.2D Disturbances in the reproduction of eelpout	8.3A Volymer av upptäckta olagliga eller olycksrelaterade utsläpp av olja och oljeliknande produkter/ 8.3A Volumes of illegal or accident related emissions of oil and oil-like products detected
Criteria status	Good	Not good	Not good	Not good	Good	Good	Good	Good	Good	Good	Good	Good	Good	Not good	Good	Not good	Good	Good	Good	Good	Not good	Good	Good	Good	Not good
Description criteria																				Criteria assessment based on two parameters: proportion of malformed embryos (threshold 5,9%) and the proportion of females with more than one malformed embryo (threshold 30%)
Element status	Good	Not good	Not good	Not good	Good	Good	Good	Good	Good	Good	Good	Good	Good	Not good	Good	Not good	Good	Good	Good	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	Not relevant
Integration rule description parameter
Integration rule type criteria	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant
Integration rule description criteria
GES extent threshold	100.00	100.00	100.00	100.00	100.00	100.00	100.00	100.00	100.00	100.00	100.00	100.00	100.00	100.00	100.00	100.00
GES extent achieved	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	75.00	71.00	71.00	71.00	71.00	71.00	71.00	71.00
GES extent unit	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Proportion of substances in good status	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant
GES achieved	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	GES expected to be achieved later than 2020, Article 14 exception reported	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	GES expected to be achieved later than 2020, Article 14 exception reported
Description overall status	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Sweden has not used the prefilled data reported under the Water Framework Directive. The primary data sources for the assessment are the national monitoring programmes for metals and organic contaminants in sediment and biota, processed using protocols agreed in Helcom and Ospar. Because of differences in monitoring and data used for the respective assessment it has not been possible to systematically combine the results. However, threshold values for biota and sediment are the same as those used under the Water Framework Directive, whereby there is an agreement on substances that generally do not achieve threshold values. Additionally, in the national report it is noted that higher concentrations of contaminants may occur on local scales, and that this may be expressed on the level of water bodies under the Water Framework Directive. The national legislation sets down a different assessment level for substances under criterion D8C1 (except cesium-137) as well as for GES assessment. The national legislation may be revised as regard the level of assessment in line with the present reporting.	Indicators under D8C2 are not integrated to criteria level	Indicators under D8C2 are not integrated to criteria level	Indicators under D8C2 are not integrated to criteria level	Indicators under D8C2 are not integrated to criteria level	Indicators under D8C2 are not integrated to criteria level	Indicators under D8C2 are not integrated to criteria level	Indicators under D8C2 are not integrated to criteria level	Indicators under D8C2 are not integrated to criteria level	The national legislation sets down a different assessment level for D8C3. The national legislation may be revised as regard the level of assessment in line with the present reporting.
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
Related pressures	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - 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	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, 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	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt	BALSE-B.1_Tillförsel_farliga_ämnen_halt BALSE-B.2_Tillförsel_farliga_ämnen_effekt