Member State report / Art8-2024 / 2024 / D9 / Sweden / NE Atlantic: Greater North Sea

Report type Member State report to Commission
MSFD Article Art8
Report due 2024-10-15
GES Descriptor D9 Contaminants in seafood
Member State Sweden
Region/subregion NE Atlantic: Greater North Sea
Report date 2025-10-30 08:59:20

ANS-SE-SR-Nordsjon

Regional assessment area
Component MRUs
GES component
D9
D9
D9
D9
D9
D9
D9
D9
D9
D9
D9
D9
D9
D9
D9
D9
D9
D9
D9
D9
Feature
Contaminants - in seafood
Contaminants - in seafood
Contaminants - in seafood
Contaminants - in seafood
Contaminants - in seafood
Contaminants - in seafood
Contaminants - in seafood
Contaminants - in seafood
Contaminants - in seafood
Contaminants - in seafood
Contaminants - in seafood
Contaminants - in seafood
Contaminants - in seafood
Contaminants - in seafood
Contaminants - in seafood
Contaminants - in seafood
Contaminants - in seafood
Contaminants - in seafood
Contaminants - in seafood
Contaminants - in seafood
Element
Benzo(a)pyrene
Cadmium and its compounds
Cadmium and its compounds
Dioxins and dioxin-like compounds (7 PCDDs + 10 PCDFs + 12 PCB-DLs)
Lead and its compounds
Lead and its compounds
Mercury and its compounds
Mercury and its compounds
Non-dioxin like PCB (sum of 6 PCB: 28, 52, 101, 138, 153 and 180)
PFOA
PFOA
PFOS
PFOS
Perfluorohexane sulfonate (PFHxS)
Perfluorohexane sulfonate (PFHxS)
Perfluorononanoate (PFNA)
Perfluorononanoate (PFNA)
Sum of PFOS, PFOA, PFNA and PFHxS
Sum of PFOS, PFOA, PFNA and PFHxS
Sum of dioxins (WHO-PCDD/F-PCB-TEQ)
Element extent
Trend element
Stable
Stable
Stable
Stable
Stable
Stable
Stable
Stable
Stable
Stable
Stable
Stable
Stable
Stable
Stable
Stable
Stable
Stable
Stable
Unknown
Element 2
Element source
EU
EU
EU
EU
EU
EU
EU
EU
EU
EU
EU
EU
EU
EU
EU
EU
EU
EU
EU
EU
Criterion
D9C1
D9C1
D9C1
D9C1
D9C1
D9C1
D9C1
D9C1
D9C1
D9C1
D9C1
D9C1
D9C1
D9C1
D9C1
D9C1
D9C1
D9C1
D9C1
D9C1
Parameter
Concentration in biota
CONC-B-Muscle
CONC-B-Muscle
CONC-B-Muscle
CONC-B-Muscle
CONC-B-Muscle
CONC-B-Muscle
CONC-B-Muscle
CONC-B-Muscle
CONC-B-Muscle
CONC-B-Muscle
CONC-B-Muscle
CONC-B-Muscle
CONC-B-Muscle
CONC-B-Muscle
CONC-B-Muscle
CONC-B-Muscle
CONC-B-Muscle
CONC-B-Muscle
CONC-B-Muscle
Threshold value upper
5.0
0.05
1.0
6.5
0.3
1.5
0.3
0.5
75.0
1.0
8.0
7.0
35.0
0.2
1.5
2.5
8.0
8.0
45.0
3.5
Threshold value lower
Threshold value operator
<
<
<
<
<
<
<
<
<
<
<
<
<
<
<
<
<
<
<
<
Threshold qualitative
Threshold value source
Regulation on contaminants in foodstuffs (EC 1881/2006)
Regulation on contaminants in foodstuffs (EC 1881/2006)
Regulation on contaminants in foodstuffs (EC 1881/2006)
Regulation on contaminants in foodstuffs (EC 1881/2006)
Regulation on contaminants in foodstuffs (EC 1881/2006)
Regulation on contaminants in foodstuffs (EC 1881/2006)
Regulation on contaminants in foodstuffs (EC 1881/2006)
Regulation on contaminants in foodstuffs (EC 1881/2006)
Regulation on contaminants in foodstuffs (EC 1881/2006)
Regulation on contaminants in foodstuffs (EC 1881/2006)
Regulation on contaminants in foodstuffs (EC 1881/2006)
Regulation on contaminants in foodstuffs (EC 1881/2006)
Regulation on contaminants in foodstuffs (EC 1881/2006)
Regulation on contaminants in foodstuffs (EC 1881/2006)
Regulation on contaminants in foodstuffs (EC 1881/2006)
Regulation on contaminants in foodstuffs (EC 1881/2006)
Regulation on contaminants in foodstuffs (EC 1881/2006)
Regulation on contaminants in foodstuffs (EC 1881/2006)
Regulation on contaminants in foodstuffs (EC 1881/2006)
Regulation on contaminants in foodstuffs (EC 1881/2006)
Value achieved upper
1.8
0.001
0.193
0.6
0.003
0.16
0.027
0.017
5.74
Value achieved lower
Value unit
microgram per kilogram of wet weight
milligram per kilogram of wet weight
milligram per kilogram of wet weight
pg TEQ/g ww
milligram per kilogram of wet weight
milligram per kilogram of wet weight
milligram per kilogram of wet weight
milligram per kilogram of wet weight
ng/g ww
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 wet weight
microgram per kilogram of wet weight
microgram per kilogram of wet weight
pg TEQ/g ww
Proportion threshold value
Proportion value achieved
Proportion threshold value unit
Trend parameter
Stable
Stable
Stable
Stable
Stable
Stable
Stable
Stable
Stable
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Parameter achieved
Yes
Yes
Yes
Yes
Yes
Yes
Yes
Yes
Yes
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Description parameter
Related indicator
Criteria status
Good
Good
Good
Good
Good
Good
Good
Good
Good
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Description criteria
Element status
Good
Good
Good
Good
Good
Good
Good
Good
Good
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Description element
Source assessment feature
  • National
  • National
  • National
  • National
  • National
  • National
  • National
  • National
  • National
  • National
  • National
  • National
  • National
  • National
  • National
  • National
  • National
  • National
  • National
  • National
Reporting method feature
Type D
Type D
Type D
Type D
Type D
Type D
Type D
Type D
Type D
Type D
Type D
Type D
Type D
Type D
Type D
Type D
Type D
Type D
Type D
Type D
Trend feature
Stable
Stable
Stable
Stable
Stable
Stable
Stable
Stable
Stable
Stable
Stable
Stable
Stable
Stable
Stable
Stable
Stable
Stable
Stable
Stable
Integration rule type parameter
OOAO
OOAO
OOAO
OOAO
OOAO
OOAO
OOAO
OOAO
OOAO
OOAO
OOAO
OOAO
OOAO
OOAO
OOAO
OOAO
OOAO
OOAO
OOAO
OOAO
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
100.00
100.00
100.00
100.00
100.00
GES extent achieved
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
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
Proportion of substances in good status
Proportion of substances in good status
Proportion of substances in good status
Proportion of substances in good status
Proportion of substances in good status
GES achieved
GES achieved by 2018
GES achieved by 2018
GES achieved by 2018
GES achieved by 2018
GES achieved by 2018
GES achieved by 2018
GES achieved by 2018
GES achieved by 2018
GES achieved by 2018
GES achieved by 2018
GES achieved by 2018
GES achieved by 2018
GES achieved by 2018
GES achieved by 2018
GES achieved by 2018
GES achieved by 2018
GES achieved by 2018
GES achieved by 2018
GES achieved by 2018
GES achieved by 2018
Description overall status
Assessments period
2016-2021
2016-2021
2016-2021
2016-2021
2016-2021
2016-2021
2016-2021
2016-2021
2016-2021
2016-2021
2016-2021
2016-2021
2016-2021
2016-2021
2016-2021
2016-2021
2016-2021
2016-2021
2016-2021
2016-2021
Related pressures
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
Related targets
  • ANSSE-B.1_Tillförsel_farliga_ämnen_halt
  • ANSSE-B.1_Tillförsel_farliga_ämnen_halt
  • ANSSE-B.1_Tillförsel_farliga_ämnen_halt
  • ANSSE-B.1_Tillförsel_farliga_ämnen_halt
  • ANSSE-B.1_Tillförsel_farliga_ämnen_halt
  • ANSSE-B.1_Tillförsel_farliga_ämnen_halt
  • ANSSE-B.1_Tillförsel_farliga_ämnen_halt
  • ANSSE-B.1_Tillförsel_farliga_ämnen_halt
  • ANSSE-B.1_Tillförsel_farliga_ämnen_halt
  • ANSSE-B.1_Tillförsel_farliga_ämnen_halt
  • ANSSE-B.1_Tillförsel_farliga_ämnen_halt
  • ANSSE-B.1_Tillförsel_farliga_ämnen_halt
  • ANSSE-B.1_Tillförsel_farliga_ämnen_halt
  • ANSSE-B.1_Tillförsel_farliga_ämnen_halt
  • ANSSE-B.1_Tillförsel_farliga_ämnen_halt
  • ANSSE-B.1_Tillförsel_farliga_ämnen_halt
  • ANSSE-B.1_Tillförsel_farliga_ämnen_halt
  • ANSSE-B.1_Tillförsel_farliga_ämnen_halt
  • ANSSE-B.1_Tillförsel_farliga_ämnen_halt
  • ANSSE-B.1_Tillförsel_farliga_ämnen_halt
Test TV
Yes
Yes
Yes
Yes
Yes
Yes
Yes
Yes
Yes
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
Test results
Correct
Correct
Correct
Correct
Correct
Correct
Correct
Correct
Correct
Correct
Correct
Correct
Correct
Correct
Correct
Correct
Correct
Correct
Correct
Correct

BAL-SE-RG-Ostersjon

Regional assessment area
Component MRUs
GES component
D9
D9
D9
D9
D9
D9
D9
D9
D9
D9
D9
D9
D9
D9
D9
D9
D9
D9
D9
D9
Feature
Contaminants - in seafood
Contaminants - in seafood
Contaminants - in seafood
Contaminants - in seafood
Contaminants - in seafood
Contaminants - in seafood
Contaminants - in seafood
Contaminants - in seafood
Contaminants - in seafood
Contaminants - in seafood
Contaminants - in seafood
Contaminants - in seafood
Contaminants - in seafood
Contaminants - in seafood
Contaminants - in seafood
Contaminants - in seafood
Contaminants - in seafood
Contaminants - in seafood
Contaminants - in seafood
Contaminants - in seafood
Element
Benzo(a)pyrene
Cadmium and its compounds
Cadmium and its compounds
Dioxins and dioxin-like compounds (7 PCDDs + 10 PCDFs + 12 PCB-DLs)
Lead and its compounds
Lead and its compounds
Mercury and its compounds
Mercury and its compounds
Non-dioxin like PCB (sum of 6 PCB: 28, 52, 101, 138, 153 and 180)
PFOA
PFOA
PFOS
PFOS
Perfluorohexane sulfonate (PFHxS)
Perfluorohexane sulfonate (PFHxS)
Perfluorononanoate (PFNA)
Perfluorononanoate (PFNA)
Sum of PFOS, PFOA, PFNA and PFHxS
Sum of PFOS, PFOA, PFNA and PFHxS
Sum of dioxins (WHO-PCDD/F-PCB-TEQ)
Element extent
Trend element
Stable
Stable
Stable
Stable
Stable
Stable
Stable
Stable
Stable
Stable
Stable
Stable
Stable
Stable
Stable
Stable
Stable
Stable
Stable
Stable
Element 2
Element source
EU
EU
EU
EU
EU
EU
EU
EU
EU
EU
EU
EU
EU
EU
EU
EU
EU
EU
EU
EU
Criterion
D9C1
D9C1
D9C1
D9C1
D9C1
D9C1
D9C1
D9C1
D9C1
D9C1
D9C1
D9C1
D9C1
D9C1
D9C1
D9C1
D9C1
D9C1
D9C1
D9C1
Parameter
Concentration in biota
CONC-B-Muscle
CONC-B-Muscle
CONC-B-Muscle
CONC-B-Muscle
CONC-B-Muscle
CONC-B-Muscle
CONC-B-Muscle
CONC-B-Muscle
CONC-B-Muscle
CONC-B-Muscle
CONC-B-Muscle
CONC-B-Muscle
CONC-B-Muscle
CONC-B-Muscle
CONC-B-Muscle
CONC-B-Muscle
CONC-B-Muscle
CONC-B-Muscle
CONC-B-Muscle
Threshold value upper
5.0
0.05
1.0
6.5
0.3
1.5
0.3
0.5
75.0
1.0
8.0
7.0
35.0
0.2
1.5
2.5
8.0
8.0
45.0
3.5
Threshold value lower
Threshold value operator
<
<
<
<
<
<
<
<
<
<
<
<
<
<
<
<
<
<
<
<
Threshold qualitative
Threshold value source
Regulation on contaminants in foodstuffs (EC 1881/2006)
Regulation on contaminants in foodstuffs (EC 1881/2006)
Regulation on contaminants in foodstuffs (EC 1881/2006)
Regulation on contaminants in foodstuffs (EC 1881/2006)
Regulation on contaminants in foodstuffs (EC 1881/2006)
Regulation on contaminants in foodstuffs (EC 1881/2006)
Regulation on contaminants in foodstuffs (EC 1881/2006)
Regulation on contaminants in foodstuffs (EC 1881/2006)
Regulation on contaminants in foodstuffs (EC 1881/2006)
Regulation on contaminants in foodstuffs (EC 1881/2006)
Regulation on contaminants in foodstuffs (EC 1881/2006)
Regulation on contaminants in foodstuffs (EC 1881/2006)
Regulation on contaminants in foodstuffs (EC 1881/2006)
Regulation on contaminants in foodstuffs (EC 1881/2006)
Regulation on contaminants in foodstuffs (EC 1881/2006)
Regulation on contaminants in foodstuffs (EC 1881/2006)
Regulation on contaminants in foodstuffs (EC 1881/2006)
Regulation on contaminants in foodstuffs (EC 1881/2006)
Regulation on contaminants in foodstuffs (EC 1881/2006)
Regulation on contaminants in foodstuffs (EC 1881/2006)
Value achieved upper
0.18
0.002
0.28
0.004
0.15
0.06
0.009
Value achieved lower
Value unit
microgram per kilogram of wet weight
milligram per kilogram of wet weight
milligram per kilogram of wet weight
pg TEQ/g ww
milligram per kilogram of wet weight
milligram per kilogram of wet weight
milligram per kilogram of wet weight
milligram per kilogram of wet weight
ng/g ww
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 wet weight
microgram per kilogram of wet weight
microgram per kilogram of wet weight
pg TEQ/g ww
Proportion threshold value
Proportion value achieved
Proportion threshold value unit
Trend parameter
Stable
Stable
Stable
Stable
Stable
Stable
Stable
Stable
Stable
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Stable
Parameter achieved
Yes
Yes
Yes
No
Yes
Yes
Yes
Yes
Yes
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
No
Description parameter
According to the Swedish National Food Agency, maximum levels for dioxins and/or dioxinlike PCBs in foodstuffs are often exceeded in catches of wild caught salmon (Salmo salar), trout (Salmo trutta) and wild caught herring larger than 17 cm (Clupea harengus) in the Baltic Sea and Gulf of Bothnia. This conclusion is drawn based on results from sampling of a number of different species, time points, and monitoring stations, why a specific value can not be presented here.
According to the Swedish National Food Agency, maximum levels for dioxins and/or dioxinlike PCBs in foodstuffs are often exceeded in catches of wild caught salmon (Salmo salar), trout (Salmo trutta) and wild caught herring larger than 17 cm (Clupea harengus) in the Baltic Sea and Gulf of Bothnia. This conclusion is drawn based on results from sampling of a number of different species, time points, and monitoring stations, why a specific value can not be presented here.
According to the Swedish National Food Agency, maximum levels for dioxins and/or dioxinlike PCBs in foodstuffs are often exceeded in catches of wild caught salmon (Salmo salar), trout (Salmo trutta) and wild caught herring larger than 17 cm (Clupea harengus) in the Baltic Sea and Gulf of Bothnia. This conclusion is drawn based on results from sampling of a number of different species, time points, and monitoring stations, why a specific value can not be presented here.
Related indicator
Criteria status
Good
Good
Good
Not good
Good
Good
Good
Good
Good
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Not good
Description criteria
Element status
Good
Good
Good
Not good
Good
Good
Good
Good
Good
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Not good
Description element
Source assessment feature
  • National
  • National
  • National
  • National
  • National
  • National
  • National
  • National
  • National
  • National
  • National
  • National
  • National
  • National
  • National
  • National
  • National
  • National
  • National
  • National
Reporting method feature
Type D
Type D
Type D
Type D
Type D
Type D
Type D
Type D
Type D
Type D
Type D
Type D
Type D
Type D
Type D
Type D
Type D
Type D
Type D
Type D
Trend feature
Stable
Stable
Stable
Stable
Stable
Stable
Stable
Stable
Stable
Stable
Stable
Stable
Stable
Stable
Stable
Stable
Stable
Stable
Stable
Stable
Integration rule type parameter
OOAO
OOAO
OOAO
OOAO
OOAO
OOAO
OOAO
OOAO
OOAO
OOAO
OOAO
OOAO
OOAO
OOAO
OOAO
OOAO
OOAO
OOAO
OOAO
OOAO
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
100.00
100.00
100.00
100.00
100.00
GES extent achieved
71.00
71.00
71.00
71.00
71.00
71.00
71.00
71.00
71.00
71.00
71.00
71.00
71.00
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
Proportion of substances in good status
Proportion of substances in good status
Proportion of substances in good status
Proportion of substances in good status
GES achieved
GES later than 2024, Art14ExceptionReported
GES later than 2024, Art14ExceptionReported
GES later than 2024, Art14ExceptionReported
GES later than 2024, Art14ExceptionReported
GES later than 2024, Art14ExceptionReported
GES later than 2024, Art14ExceptionReported
GES later than 2024, Art14ExceptionReported
GES later than 2024, Art14ExceptionReported
GES later than 2024, Art14ExceptionReported
GES later than 2024, Art14ExceptionReported
GES later than 2024, Art14ExceptionReported
GES later than 2024, Art14ExceptionReported
GES later than 2024, Art14ExceptionReported
GES later than 2024, Art14ExceptionReported
GES later than 2024, Art14ExceptionReported
GES later than 2024, Art14ExceptionReported
GES later than 2024, Art14ExceptionReported
GES later than 2024, Art14ExceptionReported
GES later than 2024, Art14ExceptionReported
GES later than 2024, Art14ExceptionReported
Description overall status
When good environmental status can be reached for is difficult to estimate, as this depends on the load of dioxins and dioxin-like PCBs to the marine environment. Over the period 2006–2018, however, dioxins and dioxin-like PCBs in herring from the Baltic Sea decreased by 4–8% annually Sweden also has an exception in the Baltic Sea from (EC) 2023/91547 on levels of dioxins/dioxin like PCB in fish. När god miljöstatus kan nås är svårt att uppskatta då möjligheten påverkas av storleken på nytillförsel av dioxiner och dioxinlika PCB:er till havsmiljön. Över perioden 2006–2018 minskade dock dioxiner och dioxinlika PCB i sill och strömming från Östersjön med 4–8 % årligen. Sverige har också på grund av höga halter av dioxiner fet fisk i Östersjön ett undantag från saluföringsförbud av vissa fiskarter enligt EU- förordning 2023/91547.
When good environmental status can be reached for is difficult to estimate, as this depends on the load of dioxins and dioxin-like PCBs to the marine environment. Over the period 2006–2018, however, dioxins and dioxin-like PCBs in herring from the Baltic Sea decreased by 4–8% annually Sweden also has an exception in the Baltic Sea from (EC) 2023/91547 on levels of dioxins/dioxin like PCB in fish. När god miljöstatus kan nås är svårt att uppskatta då möjligheten påverkas av storleken på nytillförsel av dioxiner och dioxinlika PCB:er till havsmiljön. Över perioden 2006–2018 minskade dock dioxiner och dioxinlika PCB i sill och strömming från Östersjön med 4–8 % årligen. Sverige har också på grund av höga halter av dioxiner fet fisk i Östersjön ett undantag från saluföringsförbud av vissa fiskarter enligt EU- förordning 2023/91547.
When good environmental status can be reached for is difficult to estimate, as this depends on the load of dioxins and dioxin-like PCBs to the marine environment. Over the period 2006–2018, however, dioxins and dioxin-like PCBs in herring from the Baltic Sea decreased by 4–8% annually Sweden also has an exception in the Baltic Sea from (EC) 2023/91547 on levels of dioxins/dioxin like PCB in fish. När god miljöstatus kan nås är svårt att uppskatta då möjligheten påverkas av storleken på nytillförsel av dioxiner och dioxinlika PCB:er till havsmiljön. Över perioden 2006–2018 minskade dock dioxiner och dioxinlika PCB i sill och strömming från Östersjön med 4–8 % årligen. Sverige har också på grund av höga halter av dioxiner fet fisk i Östersjön ett undantag från saluföringsförbud av vissa fiskarter enligt EU- förordning 2023/91547.
When good environmental status can be reached for is difficult to estimate, as this depends on the load of dioxins and dioxin-like PCBs to the marine environment. Over the period 2006–2018, however, dioxins and dioxin-like PCBs in herring from the Baltic Sea decreased by 4–8% annually Sweden also has an exception in the Baltic Sea from (EC) 2023/91547 on levels of dioxins/dioxin like PCB in fish. När god miljöstatus kan nås är svårt att uppskatta då möjligheten påverkas av storleken på nytillförsel av dioxiner och dioxinlika PCB:er till havsmiljön. Över perioden 2006–2018 minskade dock dioxiner och dioxinlika PCB i sill och strömming från Östersjön med 4–8 % årligen. Sverige har också på grund av höga halter av dioxiner fet fisk i Östersjön ett undantag från saluföringsförbud av vissa fiskarter enligt EU- förordning 2023/91547.
When good environmental status can be reached for is difficult to estimate, as this depends on the load of dioxins and dioxin-like PCBs to the marine environment. Over the period 2006–2018, however, dioxins and dioxin-like PCBs in herring from the Baltic Sea decreased by 4–8% annually Sweden also has an exception in the Baltic Sea from (EC) 2023/91547 on levels of dioxins/dioxin like PCB in fish. När god miljöstatus kan nås är svårt att uppskatta då möjligheten påverkas av storleken på nytillförsel av dioxiner och dioxinlika PCB:er till havsmiljön. Över perioden 2006–2018 minskade dock dioxiner och dioxinlika PCB i sill och strömming från Östersjön med 4–8 % årligen. Sverige har också på grund av höga halter av dioxiner fet fisk i Östersjön ett undantag från saluföringsförbud av vissa fiskarter enligt EU- förordning 2023/91547.
When good environmental status can be reached for is difficult to estimate, as this depends on the load of dioxins and dioxin-like PCBs to the marine environment. Over the period 2006–2018, however, dioxins and dioxin-like PCBs in herring from the Baltic Sea decreased by 4–8% annually Sweden also has an exception in the Baltic Sea from (EC) 2023/91547 on levels of dioxins/dioxin like PCB in fish. När god miljöstatus kan nås är svårt att uppskatta då möjligheten påverkas av storleken på nytillförsel av dioxiner och dioxinlika PCB:er till havsmiljön. Över perioden 2006–2018 minskade dock dioxiner och dioxinlika PCB i sill och strömming från Östersjön med 4–8 % årligen. Sverige har också på grund av höga halter av dioxiner fet fisk i Östersjön ett undantag från saluföringsförbud av vissa fiskarter enligt EU- förordning 2023/91547.
When good environmental status can be reached for is difficult to estimate, as this depends on the load of dioxins and dioxin-like PCBs to the marine environment. Over the period 2006–2018, however, dioxins and dioxin-like PCBs in herring from the Baltic Sea decreased by 4–8% annually Sweden also has an exception in the Baltic Sea from (EC) 2023/91547 on levels of dioxins/dioxin like PCB in fish. När god miljöstatus kan nås är svårt att uppskatta då möjligheten påverkas av storleken på nytillförsel av dioxiner och dioxinlika PCB:er till havsmiljön. Över perioden 2006–2018 minskade dock dioxiner och dioxinlika PCB i sill och strömming från Östersjön med 4–8 % årligen. Sverige har också på grund av höga halter av dioxiner fet fisk i Östersjön ett undantag från saluföringsförbud av vissa fiskarter enligt EU- förordning 2023/91547.
When good environmental status can be reached for is difficult to estimate, as this depends on the load of dioxins and dioxin-like PCBs to the marine environment. Over the period 2006–2018, however, dioxins and dioxin-like PCBs in herring from the Baltic Sea decreased by 4–8% annually Sweden also has an exception in the Baltic Sea from (EC) 2023/91547 on levels of dioxins/dioxin like PCB in fish. När god miljöstatus kan nås är svårt att uppskatta då möjligheten påverkas av storleken på nytillförsel av dioxiner och dioxinlika PCB:er till havsmiljön. Över perioden 2006–2018 minskade dock dioxiner och dioxinlika PCB i sill och strömming från Östersjön med 4–8 % årligen. Sverige har också på grund av höga halter av dioxiner fet fisk i Östersjön ett undantag från saluföringsförbud av vissa fiskarter enligt EU- förordning 2023/91547.
When good environmental status can be reached for is difficult to estimate, as this depends on the load of dioxins and dioxin-like PCBs to the marine environment. Over the period 2006–2018, however, dioxins and dioxin-like PCBs in herring from the Baltic Sea decreased by 4–8% annually Sweden also has an exception in the Baltic Sea from (EC) 2023/91547 on levels of dioxins/dioxin like PCB in fish. När god miljöstatus kan nås är svårt att uppskatta då möjligheten påverkas av storleken på nytillförsel av dioxiner och dioxinlika PCB:er till havsmiljön. Över perioden 2006–2018 minskade dock dioxiner och dioxinlika PCB i sill och strömming från Östersjön med 4–8 % årligen. Sverige har också på grund av höga halter av dioxiner fet fisk i Östersjön ett undantag från saluföringsförbud av vissa fiskarter enligt EU- förordning 2023/91547.
When good environmental status can be reached for is difficult to estimate, as this depends on the load of dioxins and dioxin-like PCBs to the marine environment. Over the period 2006–2018, however, dioxins and dioxin-like PCBs in herring from the Baltic Sea decreased by 4–8% annually Sweden also has an exception in the Baltic Sea from (EC) 2023/91547 on levels of dioxins/dioxin like PCB in fish. När god miljöstatus kan nås är svårt att uppskatta då möjligheten påverkas av storleken på nytillförsel av dioxiner och dioxinlika PCB:er till havsmiljön. Över perioden 2006–2018 minskade dock dioxiner och dioxinlika PCB i sill och strömming från Östersjön med 4–8 % årligen. Sverige har också på grund av höga halter av dioxiner fet fisk i Östersjön ett undantag från saluföringsförbud av vissa fiskarter enligt EU- förordning 2023/91547.
When good environmental status can be reached for is difficult to estimate, as this depends on the load of dioxins and dioxin-like PCBs to the marine environment. Over the period 2006–2018, however, dioxins and dioxin-like PCBs in herring from the Baltic Sea decreased by 4–8% annually Sweden also has an exception in the Baltic Sea from (EC) 2023/91547 on levels of dioxins/dioxin like PCB in fish. När god miljöstatus kan nås är svårt att uppskatta då möjligheten påverkas av storleken på nytillförsel av dioxiner och dioxinlika PCB:er till havsmiljön. Över perioden 2006–2018 minskade dock dioxiner och dioxinlika PCB i sill och strömming från Östersjön med 4–8 % årligen. Sverige har också på grund av höga halter av dioxiner fet fisk i Östersjön ett undantag från saluföringsförbud av vissa fiskarter enligt EU- förordning 2023/91547.
When good environmental status can be reached for is difficult to estimate, as this depends on the load of dioxins and dioxin-like PCBs to the marine environment. Over the period 2006–2018, however, dioxins and dioxin-like PCBs in herring from the Baltic Sea decreased by 4–8% annually Sweden also has an exception in the Baltic Sea from (EC) 2023/91547 on levels of dioxins/dioxin like PCB in fish. När god miljöstatus kan nås är svårt att uppskatta då möjligheten påverkas av storleken på nytillförsel av dioxiner och dioxinlika PCB:er till havsmiljön. Över perioden 2006–2018 minskade dock dioxiner och dioxinlika PCB i sill och strömming från Östersjön med 4–8 % årligen. Sverige har också på grund av höga halter av dioxiner fet fisk i Östersjön ett undantag från saluföringsförbud av vissa fiskarter enligt EU- förordning 2023/91547.
When good environmental status can be reached for is difficult to estimate, as this depends on the load of dioxins and dioxin-like PCBs to the marine environment. Over the period 2006–2018, however, dioxins and dioxin-like PCBs in herring from the Baltic Sea decreased by 4–8% annually Sweden also has an exception in the Baltic Sea from (EC) 2023/91547 on levels of dioxins/dioxin like PCB in fish. När god miljöstatus kan nås är svårt att uppskatta då möjligheten påverkas av storleken på nytillförsel av dioxiner och dioxinlika PCB:er till havsmiljön. Över perioden 2006–2018 minskade dock dioxiner och dioxinlika PCB i sill och strömming från Östersjön med 4–8 % årligen. Sverige har också på grund av höga halter av dioxiner fet fisk i Östersjön ett undantag från saluföringsförbud av vissa fiskarter enligt EU- förordning 2023/91547.
When good environmental status can be reached for is difficult to estimate, as this depends on the load of dioxins and dioxin-like PCBs to the marine environment. Over the period 2006–2018, however, dioxins and dioxin-like PCBs in herring from the Baltic Sea decreased by 4–8% annually Sweden also has an exception in the Baltic Sea from (EC) 2023/91547 on levels of dioxins/dioxin like PCB in fish. När god miljöstatus kan nås är svårt att uppskatta då möjligheten påverkas av storleken på nytillförsel av dioxiner och dioxinlika PCB:er till havsmiljön. Över perioden 2006–2018 minskade dock dioxiner och dioxinlika PCB i sill och strömming från Östersjön med 4–8 % årligen. Sverige har också på grund av höga halter av dioxiner fet fisk i Östersjön ett undantag från saluföringsförbud av vissa fiskarter enligt EU- förordning 2023/91547.
When good environmental status can be reached for is difficult to estimate, as this depends on the load of dioxins and dioxin-like PCBs to the marine environment. Over the period 2006–2018, however, dioxins and dioxin-like PCBs in herring from the Baltic Sea decreased by 4–8% annually Sweden also has an exception in the Baltic Sea from (EC) 2023/91547 on levels of dioxins/dioxin like PCB in fish. När god miljöstatus kan nås är svårt att uppskatta då möjligheten påverkas av storleken på nytillförsel av dioxiner och dioxinlika PCB:er till havsmiljön. Över perioden 2006–2018 minskade dock dioxiner och dioxinlika PCB i sill och strömming från Östersjön med 4–8 % årligen. Sverige har också på grund av höga halter av dioxiner fet fisk i Östersjön ett undantag från saluföringsförbud av vissa fiskarter enligt EU- förordning 2023/91547.
When good environmental status can be reached for is difficult to estimate, as this depends on the load of dioxins and dioxin-like PCBs to the marine environment. Over the period 2006–2018, however, dioxins and dioxin-like PCBs in herring from the Baltic Sea decreased by 4–8% annually Sweden also has an exception in the Baltic Sea from (EC) 2023/91547 on levels of dioxins/dioxin like PCB in fish. När god miljöstatus kan nås är svårt att uppskatta då möjligheten påverkas av storleken på nytillförsel av dioxiner och dioxinlika PCB:er till havsmiljön. Över perioden 2006–2018 minskade dock dioxiner och dioxinlika PCB i sill och strömming från Östersjön med 4–8 % årligen. Sverige har också på grund av höga halter av dioxiner fet fisk i Östersjön ett undantag från saluföringsförbud av vissa fiskarter enligt EU- förordning 2023/91547.
When good environmental status can be reached for is difficult to estimate, as this depends on the load of dioxins and dioxin-like PCBs to the marine environment. Over the period 2006–2018, however, dioxins and dioxin-like PCBs in herring from the Baltic Sea decreased by 4–8% annually Sweden also has an exception in the Baltic Sea from (EC) 2023/91547 on levels of dioxins/dioxin like PCB in fish. När god miljöstatus kan nås är svårt att uppskatta då möjligheten påverkas av storleken på nytillförsel av dioxiner och dioxinlika PCB:er till havsmiljön. Över perioden 2006–2018 minskade dock dioxiner och dioxinlika PCB i sill och strömming från Östersjön med 4–8 % årligen. Sverige har också på grund av höga halter av dioxiner fet fisk i Östersjön ett undantag från saluföringsförbud av vissa fiskarter enligt EU- förordning 2023/91547.
When good environmental status can be reached for is difficult to estimate, as this depends on the load of dioxins and dioxin-like PCBs to the marine environment. Over the period 2006–2018, however, dioxins and dioxin-like PCBs in herring from the Baltic Sea decreased by 4–8% annually Sweden also has an exception in the Baltic Sea from (EC) 2023/91547 on levels of dioxins/dioxin like PCB in fish. När god miljöstatus kan nås är svårt att uppskatta då möjligheten påverkas av storleken på nytillförsel av dioxiner och dioxinlika PCB:er till havsmiljön. Över perioden 2006–2018 minskade dock dioxiner och dioxinlika PCB i sill och strömming från Östersjön med 4–8 % årligen. Sverige har också på grund av höga halter av dioxiner fet fisk i Östersjön ett undantag från saluföringsförbud av vissa fiskarter enligt EU- förordning 2023/91547.
When good environmental status can be reached for is difficult to estimate, as this depends on the load of dioxins and dioxin-like PCBs to the marine environment. Over the period 2006–2018, however, dioxins and dioxin-like PCBs in herring from the Baltic Sea decreased by 4–8% annually Sweden also has an exception in the Baltic Sea from (EC) 2023/91547 on levels of dioxins/dioxin like PCB in fish. När god miljöstatus kan nås är svårt att uppskatta då möjligheten påverkas av storleken på nytillförsel av dioxiner och dioxinlika PCB:er till havsmiljön. Över perioden 2006–2018 minskade dock dioxiner och dioxinlika PCB i sill och strömming från Östersjön med 4–8 % årligen. Sverige har också på grund av höga halter av dioxiner fet fisk i Östersjön ett undantag från saluföringsförbud av vissa fiskarter enligt EU- förordning 2023/91547.
When good environmental status can be reached for is difficult to estimate, as this depends on the load of dioxins and dioxin-like PCBs to the marine environment. Over the period 2006–2018, however, dioxins and dioxin-like PCBs in herring from the Baltic Sea decreased by 4–8% annually Sweden also has an exception in the Baltic Sea from (EC) 2023/91547 on levels of dioxins/dioxin like PCB in fish. När god miljöstatus kan nås är svårt att uppskatta då möjligheten påverkas av storleken på nytillförsel av dioxiner och dioxinlika PCB:er till havsmiljön. Över perioden 2006–2018 minskade dock dioxiner och dioxinlika PCB i sill och strömming från Östersjön med 4–8 % årligen. Sverige har också på grund av höga halter av dioxiner fet fisk i Östersjön ett undantag från saluföringsförbud av vissa fiskarter enligt EU- förordning 2023/91547.
Assessments period
2016-2021
2016-2021
2016-2021
2016-2021
2016-2021
2016-2021
2016-2021
2016-2021
2016-2021
2016-2021
2016-2021
2016-2021
2016-2021
2016-2021
2016-2021
2016-2021
2016-2021
2016-2021
2016-2021
2016-2021
Related pressures
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
Related targets
  • BALSE-B.1_Tillförsel_farliga_ämnen_halt
  • BALSE-B.1_Tillförsel_farliga_ämnen_halt
  • BALSE-B.1_Tillförsel_farliga_ämnen_halt
  • BALSE-B.1_Tillförsel_farliga_ämnen_halt
  • BALSE-B.1_Tillförsel_farliga_ämnen_halt
  • BALSE-B.1_Tillförsel_farliga_ämnen_halt
  • BALSE-B.1_Tillförsel_farliga_ämnen_halt
  • BALSE-B.1_Tillförsel_farliga_ämnen_halt
  • BALSE-B.1_Tillförsel_farliga_ämnen_halt
  • BALSE-B.1_Tillförsel_farliga_ämnen_halt
  • BALSE-B.1_Tillförsel_farliga_ämnen_halt
  • BALSE-B.1_Tillförsel_farliga_ämnen_halt
  • BALSE-B.1_Tillförsel_farliga_ämnen_halt
  • BALSE-B.1_Tillförsel_farliga_ämnen_halt
  • BALSE-B.1_Tillförsel_farliga_ämnen_halt
  • BALSE-B.1_Tillförsel_farliga_ämnen_halt
  • BALSE-B.1_Tillförsel_farliga_ämnen_halt
  • BALSE-B.1_Tillförsel_farliga_ämnen_halt
  • BALSE-B.1_Tillförsel_farliga_ämnen_halt
  • BALSE-B.1_Tillförsel_farliga_ämnen_halt
Test TV
Yes
Yes
Yes
NA
Yes
Yes
Yes
Yes
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
Test results
Correct
Correct
Correct
False
Correct
Correct
Correct
Correct
False
Correct
Correct
Correct
Correct
Correct
Correct
Correct
Correct
Correct
Correct
False