Member State report / Art8-2024 / 2024 / D9 / Sweden / Baltic 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 | Baltic Sea |
| Report date | 2025-10-30 08:59:20 |
ANS-SE-SR-Nordsjon
Regional assessment area |
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|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
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 |
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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 |
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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 |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
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 |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Related targets |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
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. |
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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 |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
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
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Integration rule description parameter |
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Integration rule type criteria |
Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Integration rule description criteria |
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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 |
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Related targets |
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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 |