MS/Art8/2018/D6/Sweden/NE Atlantic: Greater North Sea

Member State report / Art8 / 2018 / D6 / Sweden / NE Atlantic: Greater North Sea

Report type	Member State report to Commission
MSFD Article	Art. 8 Initial assessment (and Art. 17 updates)
Report due	2018-10-15
GES Descriptor	D6 Sea-floor integrity/D1 Benthic habitats
Member State	Sweden
Region/subregion	NE Atlantic: Greater North Sea
Reported by	Havs- och vattenmyndigheten
Report date	2020-07-06
Report access	msfd2018-ART8GES_SE_200706.xml

ANS-SE-AA-BG_Vasterhavet

Simplified table

GES component	D6	D6	D6	D6	D6	D6	D6	D6	D6	D6	D6	D6	D6	D6	D6	D6	D6	D6	D6
Feature	Benthic broad habitats	Benthic broad habitats	Benthic broad habitats	Benthic broad habitats	Benthic broad habitats	Benthic broad habitats	Benthic broad habitats	Benthic broad habitats	Benthic broad habitats	Benthic broad habitats	Benthic broad habitats	Benthic broad habitats	Benthic broad habitats	Benthic broad habitats	Benthic broad habitats	Benthic broad habitats	Benthic broad habitats	Benthic broad habitats	Benthic broad habitats
Element	Circalittoral coarse sediment	Circalittoral mixed sediment	Circalittoral mud	Circalittoral rock and biogenic reef	Circalittoral sand	Infralittoral coarse sediment	Infralittoral mixed sediment	Infralittoral mud	Infralittoral rock and biogenic reef	Infralittoral rock and biogenic reef	Infralittoral rock and biogenic reef	Infralittoral sand	Offshore circalittoral coarse sediment	Offshore circalittoral mixed sediment	Offshore circalittoral mud	Offshore circalittoral rock and biogenic	Offshore circalittoral sand	Offshore circalittoral sand	Upper bathyal sediment
Element code	HabBenCircalitCoarSed	HabBenCircalitMxdSed	HabBenCircalitMud	HabBenCircalitRock	HabBenCircalitSand	HabBenInfralitCoarSed	HabBenInfralitMxdSed	HabBenInfralitMud	HabBenInfralitRock	HabBenInfralitRock	HabBenInfralitRock	HabBenInfralitSand	HabBenOffshCoarSed	HabBenOffshMxdSed	HabBenOffshMud	HabBenOffshRock	HabBenOffshSand	HabBenOffshSand	HabBenBathyalUpSed
Element code source	Habitats (D1-D6) http://dd.eionet.europa.eu/vocabulary/msfd/broadHabitatTypes/view	Habitats (D1-D6) http://dd.eionet.europa.eu/vocabulary/msfd/broadHabitatTypes/view	Habitats (D1-D6) http://dd.eionet.europa.eu/vocabulary/msfd/broadHabitatTypes/view	Habitats (D1-D6) http://dd.eionet.europa.eu/vocabulary/msfd/broadHabitatTypes/view	Habitats (D1-D6) http://dd.eionet.europa.eu/vocabulary/msfd/broadHabitatTypes/view	Habitats (D1-D6) http://dd.eionet.europa.eu/vocabulary/msfd/broadHabitatTypes/view	Habitats (D1-D6) http://dd.eionet.europa.eu/vocabulary/msfd/broadHabitatTypes/view	Habitats (D1-D6) http://dd.eionet.europa.eu/vocabulary/msfd/broadHabitatTypes/view	Habitats (D1-D6) http://dd.eionet.europa.eu/vocabulary/msfd/broadHabitatTypes/view	Habitats (D1-D6) http://dd.eionet.europa.eu/vocabulary/msfd/broadHabitatTypes/view	Habitats (D1-D6) http://dd.eionet.europa.eu/vocabulary/msfd/broadHabitatTypes/view	Habitats (D1-D6) http://dd.eionet.europa.eu/vocabulary/msfd/broadHabitatTypes/view	Habitats (D1-D6) http://dd.eionet.europa.eu/vocabulary/msfd/broadHabitatTypes/view	Habitats (D1-D6) http://dd.eionet.europa.eu/vocabulary/msfd/broadHabitatTypes/view	Habitats (D1-D6) http://dd.eionet.europa.eu/vocabulary/msfd/broadHabitatTypes/view	Habitats (D1-D6) http://dd.eionet.europa.eu/vocabulary/msfd/broadHabitatTypes/view	Habitats (D1-D6) http://dd.eionet.europa.eu/vocabulary/msfd/broadHabitatTypes/view	Habitats (D1-D6) http://dd.eionet.europa.eu/vocabulary/msfd/broadHabitatTypes/view	Habitats (D1-D6) http://dd.eionet.europa.eu/vocabulary/msfd/broadHabitatTypes/view
Element 2
Element 2 code
Element 2 code source
Element source	OSPAR	OSPAR	EU	EU	EU	OSPAR	OSPAR	EU	EU	EU	EU	EU	OSPAR	OSPAR	EU	EU	EU	EU	OSPAR
Criterion	D6C3	D6C3	D6C5	D6C5	D6C5	D6C3	D6C3	D6C5	D6C3	D6C4	D6C5	D6C5	D6C3	D6C3	D6C5	D6C5	D6C3	D6C5	D6C3
Parameter	Extent	Extent	Extent	Extent	Extent	Extent	Extent	Extent	Extent		Extent	Extent	Extent	Extent	Extent	Extent	Extent	Extent	Extent
Parameter other
Threshold value upper
Threshold value lower
Threshold qualitative	disturbance category lower than 4	disturbance category lower than 4				disturbance category lower than 4	disturbance category lower than 4		disturbance category lower than 4				disturbance category lower than 4	disturbance category lower than 4			disturbance category lower than 4		disturbance category lower than 4
Threshold value source	National	National				National	National		National				National	National			National		National
Threshold value source other
Value achieved upper
Value achieved lower
Value unit	Other	Other				Other	Other		Other				Other	Other			Other		Other
Value unit other	percent	percent				percent	percent		percent				percent	percent			percent		percent
Proportion threshold value
Proportion value achieved	87.0	95.0				89.0	86.0		86.0				33.0	44.0			30.0		1.0
Proportion threshold value unit
Trend	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown		Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown
Parameter achieved	Not assessed	Not assessed	No	No	No	Not assessed	Not assessed	No	Not assessed		Not assessed	No	Not assessed	Not assessed	No	No	Not assessed	No	Not assessed
Description parameter	The national legislation sets down a different assessment level for indicator 6.3A, Extent of physical disturbance in benthic habitat types.	The national legislation sets down a different assessment level for indicator 6.3A, Extent of physical disturbance in benthic habitat types.	Good status was not reached for circalittoral sand and mud. 16 % of the assessment area reaches threshold values.	Following the precautionary principle good status cannot be considered reached, based on the 2013 reporting of quality parameters under Article 17 of the Habitats directive (92/43/EEG).	Good status was not reached for circalittoral sand and mud. 16 % of the assessment area reaches threshold values.	The national legislation sets down a different assessment level for indicator 6.3A, Extent of physical disturbance in benthic habitat types.	The national legislation sets down a different assessment level for indicator 6.3A, Extent of physical disturbance in benthic habitat types.	Following the precautionary principle good status cannot be considered reached, based on the 2013 reporting of quality parameters under Article 17 of the Habitats directive (92/43/EEG).	The national legislation sets down a different assessment level for indicator 6.3A, Extent of physical disturbance in benthic habitat types.		An assessment could not be made for infralittoral rock and biogenic reef because of data lacking for 33% of the assessment area, and threshold values reached for 66% of the area.	Following the precautionary principle good status cannot be considered reached, based on the 2013 reporting of quality parameters under Article 17 of the Habitats directive (92/43/EEG).	The national legislation sets down a different assessment level for indicator 6.3A, Extent of physical disturbance in benthic habitat types.	The national legislation sets down a different assessment level for indicator 6.3A, Extent of physical disturbance in benthic habitat types.	Good status was not reached for circalittoral sand and mud. In the open sea, 51,3 % of the assessment area reaches threshold values	Following the precautionary principle good status cannot be considered reached, based on the 2013 reporting of quality parameters under Article 17 of the Habitats directive (92/43/EEG).	The national legislation sets down a different assessment level for indicator 6.3A, Extent of physical disturbance in benthic habitat types.	Good status was not reached for circalittoral sand and mud. In the open sea, 51,3 % of the assessment area reaches threshold values	The national legislation sets down a different assessment level for indicator 6.3A, Extent of physical disturbance in benthic habitat types.
Related indicator	6.3A Utsträckning av fysisk störning i bentiska livsmiljöer/ 6.3A Extent of physical disturbance in benthic habitat types	6.3A Utsträckning av fysisk störning i bentiska livsmiljöer/ 6.3A Extent of physical disturbance in benthic habitat types				6.3A Utsträckning av fysisk störning i bentiska livsmiljöer/ 6.3A Extent of physical disturbance in benthic habitat types	6.3A Utsträckning av fysisk störning i bentiska livsmiljöer/ 6.3A Extent of physical disturbance in benthic habitat types		6.3A Utsträckning av fysisk störning i bentiska livsmiljöer/ 6.3A Extent of physical disturbance in benthic habitat types				6.3A Utsträckning av fysisk störning i bentiska livsmiljöer/ 6.3A Extent of physical disturbance in benthic habitat types	6.3A Utsträckning av fysisk störning i bentiska livsmiljöer/ 6.3A Extent of physical disturbance in benthic habitat types			6.3A Utsträckning av fysisk störning i bentiska livsmiljöer/ 6.3A Extent of physical disturbance in benthic habitat types		6.3A Utsträckning av fysisk störning i bentiska livsmiljöer/ 6.3A Extent of physical disturbance in benthic habitat types
Criteria status	Not assessed	Not assessed	Not good	Not good	Not good	Not assessed	Not assessed	Not good	Not assessed	Not assessed	Not assessed	Not good	Not assessed	Not assessed	Not good	Not good	Not assessed	Not good	Not assessed
Description criteria			Good status was not reached for circalittoral sand and mud. 16 % of the assessment area reaches threshold values.	Following the precautionary principle good status cannot be considered reached, based on the 2013 reporting of quality parameters under Article 17 of the Habitats directive (92/43/EEG).	Good status was not reached for circalittoral sand and mud. 16 % of the assessment area reaches threshold values.			Following the precautionary principle good status cannot be considered reached, based on the 2013 reporting of quality parameters under Article 17 of the Habitats directive (92/43/EEG).		Sweden do not have indicators under this criterion yet. The reason is lack of enough and adequate information and knowledge on the benthic habitats. Another reason is that threshold values shall be established at union level. We will include these thresholds when they are established. We are active in groups discussing this in CIS-MSFD, as well as in OSPAR and HELCOM.	An assessment could not be made for infralittoral rock and biogenic reef because of data lacking for 33% of the assessment area, and threshold values reached for 66% of the area.	Following the precautionary principle good status cannot be considered reached, based on the 2013 reporting of quality parameters under Article 17 of the Habitats directive (92/43/EEG).			Good status was not reached for circalittoral sand and mud. In the open sea, 51,3 % of the assessment area reaches threshold values	Following the precautionary principle good status cannot be considered reached, based on the 2013 reporting of quality parameters under Article 17 of the Habitats directive (92/43/EEG).		Good status was not reached for circalittoral sand and mud. In the open sea, 51,3 % of the assessment area reaches threshold values
Element status	Not assessed	Not assessed	Not good	Not good	Not good	Not assessed	Not assessed	Not good	Not assessed	Not assessed	Not assessed	Not good	Not assessed	Not assessed	Not good	Not good	Not good	Not good	Not assessed
Description element
Integration rule type parameter	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 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
GES extent achieved
GES extent unit
GES achieved	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed
Description overall status	The Swedish assessment for benthic habitats in 2018 is incomplete, and is assessed for 9 elements for criterion D6C5 and 16 elements for D6C3. The assessment for D6C3 is not done quantitatively on parameter level due to lack of integration methods. For D5C6 coastal areas were assessed building on the assessment done according to the Water Framework Directive but aggregated to coastal water type regarding soft-bottom macrofauna and macrophytes. Habitats in the open sea were assessed based on indicators and assessments available within the regional sea conventions. In cases where no assessments were available, a risk assessment was made based on Article 17 of the Habitats directive (92/43/EEG).	The Swedish assessment for benthic habitats in 2018 is incomplete, and is assessed for 9 elements for criterion D6C5 and 16 elements for D6C3. The assessment for D6C3 is not done quantitatively on parameter level due to lack of integration methods. For D5C6 coastal areas were assessed building on the assessment done according to the Water Framework Directive but aggregated to coastal water type regarding soft-bottom macrofauna and macrophytes. Habitats in the open sea were assessed based on indicators and assessments available within the regional sea conventions. In cases where no assessments were available, a risk assessment was made based on Article 17 of the Habitats directive (92/43/EEG).	The Swedish assessment for benthic habitats in 2018 is incomplete, and is assessed for 9 elements for criterion D6C5 and 16 elements for D6C3. The assessment for D6C3 is not done quantitatively on parameter level due to lack of integration methods. For D5C6 coastal areas were assessed building on the assessment done according to the Water Framework Directive but aggregated to coastal water type regarding soft-bottom macrofauna and macrophytes. Habitats in the open sea were assessed based on indicators and assessments available within the regional sea conventions. In cases where no assessments were available, a risk assessment was made based on Article 17 of the Habitats directive (92/43/EEG).	The Swedish assessment for benthic habitats in 2018 is incomplete, and is assessed for 9 elements for criterion D6C5 and 16 elements for D6C3. The assessment for D6C3 is not done quantitatively on parameter level due to lack of integration methods. For D5C6 coastal areas were assessed building on the assessment done according to the Water Framework Directive but aggregated to coastal water type regarding soft-bottom macrofauna and macrophytes. Habitats in the open sea were assessed based on indicators and assessments available within the regional sea conventions. In cases where no assessments were available, a risk assessment was made based on Article 17 of the Habitats directive (92/43/EEG).	The Swedish assessment for benthic habitats in 2018 is incomplete, and is assessed for 9 elements for criterion D6C5 and 16 elements for D6C3. The assessment for D6C3 is not done quantitatively on parameter level due to lack of integration methods. For D5C6 coastal areas were assessed building on the assessment done according to the Water Framework Directive but aggregated to coastal water type regarding soft-bottom macrofauna and macrophytes. Habitats in the open sea were assessed based on indicators and assessments available within the regional sea conventions. In cases where no assessments were available, a risk assessment was made based on Article 17 of the Habitats directive (92/43/EEG).	The Swedish assessment for benthic habitats in 2018 is incomplete, and is assessed for 9 elements for criterion D6C5 and 16 elements for D6C3. The assessment for D6C3 is not done quantitatively on parameter level due to lack of integration methods. For D5C6 coastal areas were assessed building on the assessment done according to the Water Framework Directive but aggregated to coastal water type regarding soft-bottom macrofauna and macrophytes. Habitats in the open sea were assessed based on indicators and assessments available within the regional sea conventions. In cases where no assessments were available, a risk assessment was made based on Article 17 of the Habitats directive (92/43/EEG).	The Swedish assessment for benthic habitats in 2018 is incomplete, and is assessed for 9 elements for criterion D6C5 and 16 elements for D6C3. The assessment for D6C3 is not done quantitatively on parameter level due to lack of integration methods. For D5C6 coastal areas were assessed building on the assessment done according to the Water Framework Directive but aggregated to coastal water type regarding soft-bottom macrofauna and macrophytes. Habitats in the open sea were assessed based on indicators and assessments available within the regional sea conventions. In cases where no assessments were available, a risk assessment was made based on Article 17 of the Habitats directive (92/43/EEG).	The Swedish assessment for benthic habitats in 2018 is incomplete, and is assessed for 9 elements for criterion D6C5 and 16 elements for D6C3. The assessment for D6C3 is not done quantitatively on parameter level due to lack of integration methods. For D5C6 coastal areas were assessed building on the assessment done according to the Water Framework Directive but aggregated to coastal water type regarding soft-bottom macrofauna and macrophytes. Habitats in the open sea were assessed based on indicators and assessments available within the regional sea conventions. In cases where no assessments were available, a risk assessment was made based on Article 17 of the Habitats directive (92/43/EEG).	The Swedish assessment for benthic habitats in 2018 is incomplete, and is assessed for 9 elements for criterion D6C5 and 16 elements for D6C3. The assessment for D6C3 is not done quantitatively on parameter level due to lack of integration methods. For D5C6 coastal areas were assessed building on the assessment done according to the Water Framework Directive but aggregated to coastal water type regarding soft-bottom macrofauna and macrophytes. Habitats in the open sea were assessed based on indicators and assessments available within the regional sea conventions. In cases where no assessments were available, a risk assessment was made based on Article 17 of the Habitats directive (92/43/EEG).	The Swedish assessment for benthic habitats in 2018 is incomplete, and is assessed for 9 elements for criterion D6C5 and 16 elements for D6C3. The assessment for D6C3 is not done quantitatively on parameter level due to lack of integration methods. For D5C6 coastal areas were assessed building on the assessment done according to the Water Framework Directive but aggregated to coastal water type regarding soft-bottom macrofauna and macrophytes. Habitats in the open sea were assessed based on indicators and assessments available within the regional sea conventions. In cases where no assessments were available, a risk assessment was made based on Article 17 of the Habitats directive (92/43/EEG).	The Swedish assessment for benthic habitats in 2018 is incomplete, and is assessed for 9 elements for criterion D6C5 and 16 elements for D6C3. The assessment for D6C3 is not done quantitatively on parameter level due to lack of integration methods. For D5C6 coastal areas were assessed building on the assessment done according to the Water Framework Directive but aggregated to coastal water type regarding soft-bottom macrofauna and macrophytes. Habitats in the open sea were assessed based on indicators and assessments available within the regional sea conventions. In cases where no assessments were available, a risk assessment was made based on Article 17 of the Habitats directive (92/43/EEG).	The Swedish assessment for benthic habitats in 2018 is incomplete, and is assessed for 9 elements for criterion D6C5 and 16 elements for D6C3. The assessment for D6C3 is not done quantitatively on parameter level due to lack of integration methods. For D5C6 coastal areas were assessed building on the assessment done according to the Water Framework Directive but aggregated to coastal water type regarding soft-bottom macrofauna and macrophytes. Habitats in the open sea were assessed based on indicators and assessments available within the regional sea conventions. In cases where no assessments were available, a risk assessment was made based on Article 17 of the Habitats directive (92/43/EEG).	The Swedish assessment for benthic habitats in 2018 is incomplete, and is assessed for 9 elements for criterion D6C5 and 16 elements for D6C3. The assessment for D6C3 is not done quantitatively on parameter level due to lack of integration methods. For D5C6 coastal areas were assessed building on the assessment done according to the Water Framework Directive but aggregated to coastal water type regarding soft-bottom macrofauna and macrophytes. Habitats in the open sea were assessed based on indicators and assessments available within the regional sea conventions. In cases where no assessments were available, a risk assessment was made based on Article 17 of the Habitats directive (92/43/EEG).	The Swedish assessment for benthic habitats in 2018 is incomplete, and is assessed for 9 elements for criterion D6C5 and 16 elements for D6C3. The assessment for D6C3 is not done quantitatively on parameter level due to lack of integration methods. For D5C6 coastal areas were assessed building on the assessment done according to the Water Framework Directive but aggregated to coastal water type regarding soft-bottom macrofauna and macrophytes. Habitats in the open sea were assessed based on indicators and assessments available within the regional sea conventions. In cases where no assessments were available, a risk assessment was made based on Article 17 of the Habitats directive (92/43/EEG).	The Swedish assessment for benthic habitats in 2018 is incomplete, and is assessed for 9 elements for criterion D6C5 and 16 elements for D6C3. The assessment for D6C3 is not done quantitatively on parameter level due to lack of integration methods. For D5C6 coastal areas were assessed building on the assessment done according to the Water Framework Directive but aggregated to coastal water type regarding soft-bottom macrofauna and macrophytes. Habitats in the open sea were assessed based on indicators and assessments available within the regional sea conventions. In cases where no assessments were available, a risk assessment was made based on Article 17 of the Habitats directive (92/43/EEG).	The Swedish assessment for benthic habitats in 2018 is incomplete, and is assessed for 9 elements for criterion D6C5 and 16 elements for D6C3. The assessment for D6C3 is not done quantitatively on parameter level due to lack of integration methods. For D5C6 coastal areas were assessed building on the assessment done according to the Water Framework Directive but aggregated to coastal water type regarding soft-bottom macrofauna and macrophytes. Habitats in the open sea were assessed based on indicators and assessments available within the regional sea conventions. In cases where no assessments were available, a risk assessment was made based on Article 17 of the Habitats directive (92/43/EEG).	The Swedish assessment for benthic habitats in 2018 is incomplete, and is assessed for 9 elements for criterion D6C5 and 16 elements for D6C3. The assessment for D6C3 is not done quantitatively on parameter level due to lack of integration methods. For D5C6 coastal areas were assessed building on the assessment done according to the Water Framework Directive but aggregated to coastal water type regarding soft-bottom macrofauna and macrophytes. Habitats in the open sea were assessed based on indicators and assessments available within the regional sea conventions. In cases where no assessments were available, a risk assessment was made based on Article 17 of the Habitats directive (92/43/EEG).	The Swedish assessment for benthic habitats in 2018 is incomplete, and is assessed for 9 elements for criterion D6C5 and 16 elements for D6C3. The assessment for D6C3 is not done quantitatively on parameter level due to lack of integration methods. For D5C6 coastal areas were assessed building on the assessment done according to the Water Framework Directive but aggregated to coastal water type regarding soft-bottom macrofauna and macrophytes. Habitats in the open sea were assessed based on indicators and assessments available within the regional sea conventions. In cases where no assessments were available, a risk assessment was made based on Article 17 of the Habitats directive (92/43/EEG).	The Swedish assessment for benthic habitats in 2018 is incomplete, and is assessed for 9 elements for criterion D6C5 and 16 elements for D6C3. The assessment for D6C3 is not done quantitatively on parameter level due to lack of integration methods. For D5C6 coastal areas were assessed building on the assessment done according to the Water Framework Directive but aggregated to coastal water type regarding soft-bottom macrofauna and macrophytes. Habitats in the open sea were assessed based on indicators and assessments available within the regional sea conventions. In cases where no assessments were available, a risk assessment was made based on Article 17 of the Habitats directive (92/43/EEG).
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	Input of nutrients - diffuse sources, point sources, atmospheric deposition Input of organic matter - diffuse sources and point sources	Input of nutrients - diffuse sources, point sources, atmospheric deposition Input of organic matter - diffuse sources and point sources	Input of nutrients - diffuse sources, point sources, atmospheric deposition Input of organic matter - diffuse sources and point sources	Input of nutrients - diffuse sources, point sources, atmospheric deposition Input of organic matter - diffuse sources and point sources	Input of nutrients - diffuse sources, point sources, atmospheric deposition Input of organic matter - diffuse sources and point sources	Input of nutrients - diffuse sources, point sources, atmospheric deposition Input of organic matter - diffuse sources and point sources	Input of nutrients - diffuse sources, point sources, atmospheric deposition Input of organic matter - diffuse sources and point sources	Input of nutrients - diffuse sources, point sources, atmospheric deposition Input of organic matter - diffuse sources and point sources	Input of nutrients - diffuse sources, point sources, atmospheric deposition Input of organic matter - diffuse sources and point sources	Input of nutrients - diffuse sources, point sources, atmospheric deposition Input of organic matter - diffuse sources and point sources	Input of nutrients - diffuse sources, point sources, atmospheric deposition Input of organic matter - diffuse sources and point sources	Input of nutrients - diffuse sources, point sources, atmospheric deposition Input of organic matter - diffuse sources and point sources	Input of nutrients - diffuse sources, point sources, atmospheric deposition Input of organic matter - diffuse sources and point sources	Input of nutrients - diffuse sources, point sources, atmospheric deposition Input of organic matter - diffuse sources and point sources	Input of nutrients - diffuse sources, point sources, atmospheric deposition Input of organic matter - diffuse sources and point sources	Input of nutrients - diffuse sources, point sources, atmospheric deposition Input of organic matter - diffuse sources and point sources	Input of nutrients - diffuse sources, point sources, atmospheric deposition Input of organic matter - diffuse sources and point sources	Input of nutrients - diffuse sources, point sources, atmospheric deposition Input of organic matter - diffuse sources and point sources	Input of nutrients - diffuse sources, point sources, atmospheric deposition Input of organic matter - diffuse sources and point sources
Related targets	ANSSE-A.1_Tillförsel_näringsämnen ANSSE-B.1_Tillförsel_farliga_ämnen_halt ANSSE-B.2_Tillförsel_farliga_ämnen_effekt ANSSE-C.1_Introduktion_främmande arter ANSSE-C.3_Population_fisk_ålder_storlek_bestånd ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek ANSSE-D.1_Havsbottenareal_struktur_funktion ANSSE-D.2_Biogena_substrat_areal ANSSE-D.3_Hydrografiska_förhåll_storskal_verksam ANSSE-E.1_Skräp	ANSSE-A.1_Tillförsel_näringsämnen ANSSE-B.1_Tillförsel_farliga_ämnen_halt ANSSE-B.2_Tillförsel_farliga_ämnen_effekt ANSSE-C.1_Introduktion_främmande arter ANSSE-C.3_Population_fisk_ålder_storlek_bestånd ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek ANSSE-D.1_Havsbottenareal_struktur_funktion ANSSE-D.2_Biogena_substrat_areal ANSSE-D.3_Hydrografiska_förhåll_storskal_verksam ANSSE-E.1_Skräp	ANSSE-A.1_Tillförsel_näringsämnen ANSSE-B.1_Tillförsel_farliga_ämnen_halt ANSSE-B.2_Tillförsel_farliga_ämnen_effekt ANSSE-C.1_Introduktion_främmande arter ANSSE-C.3_Population_fisk_ålder_storlek_bestånd ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek ANSSE-D.1_Havsbottenareal_struktur_funktion ANSSE-D.2_Biogena_substrat_areal ANSSE-D.3_Hydrografiska_förhåll_storskal_verksam ANSSE-E.1_Skräp	ANSSE-A.1_Tillförsel_näringsämnen ANSSE-B.1_Tillförsel_farliga_ämnen_halt ANSSE-B.2_Tillförsel_farliga_ämnen_effekt ANSSE-C.1_Introduktion_främmande arter ANSSE-C.3_Population_fisk_ålder_storlek_bestånd ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek ANSSE-D.1_Havsbottenareal_struktur_funktion ANSSE-D.2_Biogena_substrat_areal ANSSE-D.3_Hydrografiska_förhåll_storskal_verksam ANSSE-E.1_Skräp	ANSSE-A.1_Tillförsel_näringsämnen ANSSE-B.1_Tillförsel_farliga_ämnen_halt ANSSE-B.2_Tillförsel_farliga_ämnen_effekt ANSSE-C.1_Introduktion_främmande arter ANSSE-C.3_Population_fisk_ålder_storlek_bestånd ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek ANSSE-D.1_Havsbottenareal_struktur_funktion ANSSE-D.2_Biogena_substrat_areal ANSSE-D.3_Hydrografiska_förhåll_storskal_verksam ANSSE-E.1_Skräp	ANSSE-A.1_Tillförsel_näringsämnen ANSSE-B.1_Tillförsel_farliga_ämnen_halt ANSSE-B.2_Tillförsel_farliga_ämnen_effekt ANSSE-C.1_Introduktion_främmande arter ANSSE-C.3_Population_fisk_ålder_storlek_bestånd ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek ANSSE-D.1_Havsbottenareal_struktur_funktion ANSSE-D.2_Biogena_substrat_areal ANSSE-D.3_Hydrografiska_förhåll_storskal_verksam ANSSE-E.1_Skräp	ANSSE-A.1_Tillförsel_näringsämnen ANSSE-B.1_Tillförsel_farliga_ämnen_halt ANSSE-B.2_Tillförsel_farliga_ämnen_effekt ANSSE-C.1_Introduktion_främmande arter ANSSE-C.3_Population_fisk_ålder_storlek_bestånd ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek ANSSE-D.1_Havsbottenareal_struktur_funktion ANSSE-D.2_Biogena_substrat_areal ANSSE-D.3_Hydrografiska_förhåll_storskal_verksam ANSSE-E.1_Skräp	ANSSE-A.1_Tillförsel_näringsämnen ANSSE-B.1_Tillförsel_farliga_ämnen_halt ANSSE-B.2_Tillförsel_farliga_ämnen_effekt ANSSE-C.1_Introduktion_främmande arter ANSSE-C.3_Population_fisk_ålder_storlek_bestånd ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek ANSSE-D.1_Havsbottenareal_struktur_funktion ANSSE-D.2_Biogena_substrat_areal ANSSE-D.3_Hydrografiska_förhåll_storskal_verksam ANSSE-E.1_Skräp	ANSSE-A.1_Tillförsel_näringsämnen ANSSE-B.1_Tillförsel_farliga_ämnen_halt ANSSE-B.2_Tillförsel_farliga_ämnen_effekt ANSSE-C.1_Introduktion_främmande arter ANSSE-C.3_Population_fisk_ålder_storlek_bestånd ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek ANSSE-D.1_Havsbottenareal_struktur_funktion ANSSE-D.2_Biogena_substrat_areal ANSSE-D.3_Hydrografiska_förhåll_storskal_verksam ANSSE-E.1_Skräp	ANSSE-A.1_Tillförsel_näringsämnen ANSSE-B.1_Tillförsel_farliga_ämnen_halt ANSSE-B.2_Tillförsel_farliga_ämnen_effekt ANSSE-C.1_Introduktion_främmande arter ANSSE-C.3_Population_fisk_ålder_storlek_bestånd ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek ANSSE-D.1_Havsbottenareal_struktur_funktion ANSSE-D.2_Biogena_substrat_areal ANSSE-D.3_Hydrografiska_förhåll_storskal_verksam ANSSE-E.1_Skräp	ANSSE-A.1_Tillförsel_näringsämnen ANSSE-B.1_Tillförsel_farliga_ämnen_halt ANSSE-B.2_Tillförsel_farliga_ämnen_effekt ANSSE-C.1_Introduktion_främmande arter ANSSE-C.3_Population_fisk_ålder_storlek_bestånd ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek ANSSE-D.1_Havsbottenareal_struktur_funktion ANSSE-D.2_Biogena_substrat_areal ANSSE-D.3_Hydrografiska_förhåll_storskal_verksam ANSSE-E.1_Skräp	ANSSE-A.1_Tillförsel_näringsämnen ANSSE-B.1_Tillförsel_farliga_ämnen_halt ANSSE-B.2_Tillförsel_farliga_ämnen_effekt ANSSE-C.1_Introduktion_främmande arter ANSSE-C.3_Population_fisk_ålder_storlek_bestånd ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek ANSSE-D.1_Havsbottenareal_struktur_funktion ANSSE-D.2_Biogena_substrat_areal ANSSE-D.3_Hydrografiska_förhåll_storskal_verksam ANSSE-E.1_Skräp	ANSSE-A.1_Tillförsel_näringsämnen ANSSE-B.1_Tillförsel_farliga_ämnen_halt ANSSE-B.2_Tillförsel_farliga_ämnen_effekt ANSSE-C.1_Introduktion_främmande arter ANSSE-C.3_Population_fisk_ålder_storlek_bestånd ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek ANSSE-D.1_Havsbottenareal_struktur_funktion ANSSE-D.2_Biogena_substrat_areal ANSSE-D.3_Hydrografiska_förhåll_storskal_verksam ANSSE-E.1_Skräp	ANSSE-A.1_Tillförsel_näringsämnen ANSSE-B.1_Tillförsel_farliga_ämnen_halt ANSSE-B.2_Tillförsel_farliga_ämnen_effekt ANSSE-C.1_Introduktion_främmande arter ANSSE-C.3_Population_fisk_ålder_storlek_bestånd ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek ANSSE-D.1_Havsbottenareal_struktur_funktion ANSSE-D.2_Biogena_substrat_areal ANSSE-D.3_Hydrografiska_förhåll_storskal_verksam ANSSE-E.1_Skräp	ANSSE-A.1_Tillförsel_näringsämnen ANSSE-B.1_Tillförsel_farliga_ämnen_halt ANSSE-B.2_Tillförsel_farliga_ämnen_effekt ANSSE-C.1_Introduktion_främmande arter ANSSE-C.3_Population_fisk_ålder_storlek_bestånd ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek ANSSE-D.1_Havsbottenareal_struktur_funktion ANSSE-D.2_Biogena_substrat_areal ANSSE-D.3_Hydrografiska_förhåll_storskal_verksam ANSSE-E.1_Skräp	ANSSE-A.1_Tillförsel_näringsämnen ANSSE-B.1_Tillförsel_farliga_ämnen_halt ANSSE-B.2_Tillförsel_farliga_ämnen_effekt ANSSE-C.1_Introduktion_främmande arter ANSSE-C.3_Population_fisk_ålder_storlek_bestånd ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek ANSSE-D.1_Havsbottenareal_struktur_funktion ANSSE-D.2_Biogena_substrat_areal ANSSE-D.3_Hydrografiska_förhåll_storskal_verksam ANSSE-E.1_Skräp	ANSSE-A.1_Tillförsel_näringsämnen ANSSE-B.1_Tillförsel_farliga_ämnen_halt ANSSE-B.2_Tillförsel_farliga_ämnen_effekt ANSSE-C.1_Introduktion_främmande arter ANSSE-C.3_Population_fisk_ålder_storlek_bestånd ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek ANSSE-D.1_Havsbottenareal_struktur_funktion ANSSE-D.2_Biogena_substrat_areal ANSSE-D.3_Hydrografiska_förhåll_storskal_verksam ANSSE-E.1_Skräp	ANSSE-A.1_Tillförsel_näringsämnen ANSSE-B.1_Tillförsel_farliga_ämnen_halt ANSSE-B.2_Tillförsel_farliga_ämnen_effekt ANSSE-C.1_Introduktion_främmande arter ANSSE-C.3_Population_fisk_ålder_storlek_bestånd ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek ANSSE-D.1_Havsbottenareal_struktur_funktion ANSSE-D.2_Biogena_substrat_areal ANSSE-D.3_Hydrografiska_förhåll_storskal_verksam ANSSE-E.1_Skräp	ANSSE-A.1_Tillförsel_näringsämnen ANSSE-B.1_Tillförsel_farliga_ämnen_halt ANSSE-B.2_Tillförsel_farliga_ämnen_effekt ANSSE-C.1_Introduktion_främmande arter ANSSE-C.3_Population_fisk_ålder_storlek_bestånd ANSSE-C.4_Samhälle_fisk_förkomst_art_storlek ANSSE-D.1_Havsbottenareal_struktur_funktion ANSSE-D.2_Biogena_substrat_areal ANSSE-D.3_Hydrografiska_förhåll_storskal_verksam ANSSE-E.1_Skräp