Member State report / Art8-2024 / 2024 / D9 / Belgium / 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 | Belgium |
| Region/subregion | NE Atlantic: Greater North Sea |
| Report date | 2026-01-13 14:08:15 |
Belgian Part of the North Sea (ANS-BE-MS-1)
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
|
D9
|
D9
|
D9
|
D9
|
D9
|
D9
|
D9
|
D9
|
D9
|
D9
|
D9
|
D9
|
D9
|
D9
|
D9
|
D9
|
D9
|
D9
|
D9
|
D9
|
D9
|
D9
|
D9
|
D9
|
D9
|
D9
|
D9
|
D9
|
D9
|
D9
|
D9
|
D9
|
D9
|
D9
|
D9
|
D9
|
D9
|
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
|
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
|
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
|
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 |
Cadmium and its compounds |
Cesium-134 |
Cesium-134 |
Cesium-137 |
Cesium-137 |
Dioxins and dioxin-like compounds (7 PCDDs + 10 PCDFs + 12 PCB-DLs) |
Dioxins and dioxin-like compounds (7 PCDDs + 10 PCDFs + 12 PCB-DLs) |
Dioxins and dioxin-like compounds (7 PCDDs + 10 PCDFs + 12 PCB-DLs) |
Dioxins and dioxin-like compounds (7 PCDDs + 10 PCDFs + 12 PCB-DLs) |
Dioxins and dioxin-like compounds (7 PCDDs + 10 PCDFs + 12 PCB-DLs) |
Dioxins and dioxin-like compounds (7 PCDDs + 10 PCDFs + 12 PCB-DLs) |
Lead and its compounds |
Lead and its compounds |
Lead and its compounds |
Lead and its compounds |
Mercury and its compounds |
Mercury and its compounds |
Mercury and its compounds |
Mercury 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) |
Non-dioxin like PCB (sum of 6 PCB: 28, 52, 101, 138, 153 and 180) |
Non-dioxin like PCB (sum of 6 PCB: 28, 52, 101, 138, 153 and 180) |
Non-dioxin like PCB (sum of 6 PCB: 28, 52, 101, 138, 153 and 180) |
Non-dioxin like PCB (sum of 6 PCB: 28, 52, 101, 138, 153 and 180) |
Non-dioxin like PCB (sum of 6 PCB: 28, 52, 101, 138, 153 and 180) |
Non-dioxin like PCB (sum of 6 PCB: 28, 52, 101, 138, 153 and 180) |
PFOA |
PFOA |
PFOA |
PFOA |
PFOA |
PFOS |
PFOS |
PFOS |
PFOS |
PFOS |
Perfluorohexane sulfonate (PFHxS) |
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 benz (a) pyrene, benz (a) anthracene, benzo (b) fluoranthene and chrysene |
Sum of benz (a) pyrene, benz (a) anthracene, benzo (b) fluoranthene and chrysene |
Sum of benz (a) pyrene, benz (a) anthracene, benzo (b) fluoranthene and chrysene |
Sum of dioxins (WHO-PCDD/F-PCB-TEQ) |
Sum of dioxins (WHO-PCDD/F-PCB-TEQ) |
Sum of dioxins (WHO-PCDD/F-PCB-TEQ) |
Sum of dioxins (WHO-PCDD/F-PCB-TEQ) |
Sum of dioxins (WHO-PCDD/F-PCB-TEQ) |
Sum of dioxins (WHO-PCDD/F-PCB-TEQ) |
Sum of dioxins (WHO-PCDD/F-PCB-TEQ) |
Sum of dioxins (WHO-PCDD/F-PCB-TEQ) |
Sum of dioxins (WHO-PCDD/F-PCB-TEQ) |
Sum of dioxins (WHO-PCDD/F-PCB-TEQ) |
Sum of dioxins (WHO-PCDD/F-PCB-TEQ) |
Sum of dioxins (WHO-PCDD/F-PCB-TEQ) |
Sum of dioxins (WHO-PCDD/F-PCB-TEQ) |
Sum of dioxins (WHO-PCDD/F-PCB-TEQ) |
Sum of dioxins (WHO-PCDD/F-PCB-TEQ) |
Sum of dioxins (WHO-PCDD/F-PCB-TEQ) |
Sum of dioxins (WHO-PCDD/F-TEQ) |
Sum of dioxins (WHO-PCDD/F-TEQ) |
Sum of dioxins (WHO-PCDD/F-TEQ) |
Sum of dioxins (WHO-PCDD/F-TEQ) |
Sum of dioxins (WHO-PCDD/F-TEQ) |
Sum of dioxins (WHO-PCDD/F-TEQ) |
Sum of dioxins (WHO-PCDD/F-TEQ) |
Sum of dioxins (WHO-PCDD/F-TEQ) |
Sum of dioxins (WHO-PCDD/F-TEQ) |
Sum of dioxins (WHO-PCDD/F-TEQ) |
Element extent |
|||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Trend element |
Unknown |
Unknown |
Unknown |
Unknown |
Stable |
Stable |
Stable |
Stable |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Deteriorating |
Deteriorating |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Element 2 |
Pecten maximus
|
Batoidae
|
Decapodiformes
|
Lophius piscatorius
|
Crustacea
|
Pisces
|
Crustacea
|
Pisces
|
Batoidae
|
Decapodiformes
|
Lophius piscatorius
|
Pecten maximus
|
Scomber scombrus
|
Solea solea
|
Decapodiformes
|
Gadus morhua
|
Lophius piscatorius
|
Pecten maximus
|
Batoidae
|
Gadus morhua
|
Lophius piscatorius
|
Pecten maximus
|
Pleuronectes platessa
|
Solea solea
|
Batoidae
|
Crangon crangon
|
Decapodiformes
|
Lophius piscatorius
|
Pecten maximus
|
Pleuronectes platessa
|
Solea solea
|
Batoidae
|
Crangon crangon
|
Gadus morhua
|
Lophius piscatorius
|
Pleuronectes platessa
|
Batoidae
|
Crangon crangon
|
Gadus morhua
|
Lophius piscatorius
|
Pleuronectes platessa
|
Crangon crangon
|
Gadus morhua
|
Lophius piscatorius
|
Crangon crangon
|
Lophius piscatorius
|
Crangon crangon
|
Lophius piscatorius
|
Gadus morhua
|
Lophius piscatorius
|
Pecten maximus
|
Batoidae
|
Batoidae
|
Clupea harengus
|
Crangon crangon
|
Decapodiformes
|
Decapodiformes
|
Gadus morhua
|
Lophius piscatorius
|
Lophius piscatorius
|
Pecten maximus
|
Pecten maximus
|
Pleuronectes platessa
|
Scomber scombrus
|
Scomber scombrus
|
Solea solea
|
Solea solea
|
Batoidae
|
Clupea harengus
|
Crangon crangon
|
Decapodiformes
|
Gadus morhua
|
Lophius piscatorius
|
Pecten maximus
|
Pleuronectes platessa
|
Scomber scombrus
|
Solea solea
|
Element source |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
Criterion |
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
D9C1
|
Parameter |
CONC-B-Muscle
|
CONC-B-Muscle
|
CONC-B-Muscle
|
CONC-B-Muscle
|
Concentration in biota
|
Concentration in biota
|
Concentration in biota
|
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
|
CONC-B-Muscle
|
CONC-B-Muscle
|
CONC-B-Muscle
|
CONC-B-Muscle
|
Concentration in biota
|
Concentration in biota
|
Concentration in biota
|
Concentration in biota
|
Concentration in biota
|
Concentration in biota
|
Concentration in biota
|
Concentration in biota
|
Concentration in biota
|
Concentration in biota
|
Concentration in biota
|
Concentration in biota
|
Concentration in biota
|
Concentration in biota
|
Concentration in biota
|
Concentration in biota
|
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
|
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 |
|||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
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)
|
Euratom
|
Euratom
|
Euratom
|
Euratom
|
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)
|
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)
|
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 |
2.1 |
1.7 |
5.0 |
1.7 |
6.0 |
3.98 |
0.78 |
0.11 |
0.23 |
2.0 |
0.27 |
0.24 |
0.089 |
0.097 |
0.13 |
0.011 |
0.37 |
0.14 |
4.3 |
1.3 |
4.2 |
12.0 |
3.4 |
23.3 |
14.9 |
1.0 |
6.16 |
1.7 |
0.34 |
0.36 |
13.0 |
0.6 |
|||||||||||||||||||||||||||||||||||||||||||||
Value achieved lower |
0.9 |
0.01 |
0.017 |
0.01 |
0.9 |
0.4 |
1.0 |
0.5 |
0.101 |
0.1 |
0.0209 |
0.19 |
1.3 |
0.0213 |
0.02 |
0.02 |
0.02 |
0.02 |
0.049 |
0.061 |
0.042 |
0.01 |
0.067 |
0.031 |
0.329 |
1.2 |
1.2 |
0.538 |
1.2 |
1.2 |
0.538 |
5.0 |
5.0 |
5.0 |
5.0 |
5.0 |
5.0 |
6.6 |
5.0 |
5.0 |
5.0 |
5.0 |
5.0 |
5.0 |
5.0 |
5.0 |
70.0 |
65.0 |
0.9 |
0.9 |
0.9 |
0.153 |
0.137 |
0.0893 |
0.28 |
4.86 |
0.0502 |
||||||||||||||||||||
Value unit |
microgram per kilogram of wet weight
|
milligram per kilogram of wet weight
|
milligram per kilogram of wet weight
|
milligram per kilogram of wet weight
|
Bq/kg
|
Bq/kg
|
Bq/kg
|
Bq/kg
|
pg TEQ/g ww
|
pg TEQ/g ww
|
pg TEQ/g ww
|
pg TEQ/g ww
|
pg TEQ/g ww
|
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
|
milligram per kilogram of wet weight
|
milligram per kilogram of wet weight
|
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
|
ng/g ww
|
ng/g ww
|
ng/g ww
|
ng/g ww
|
ng/g ww
|
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
|
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
|
pg TEQ/g ww
|
pg TEQ/g ww
|
pg TEQ/g ww
|
pg TEQ/g ww
|
pg TEQ/g ww
|
||||||||||||||||||||
Proportion threshold value |
|||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Proportion value achieved |
|||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Proportion threshold value unit |
|||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Trend parameter |
Stable |
Unknown |
Unknown |
Unknown |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Improving |
Unknown |
Unknown |
Unknown |
Improving |
Unknown |
Unknown |
Unknown |
Stable |
Deteriorating |
Unknown |
Unknown |
Deteriorating |
Improving |
Unknown |
Stable |
Improving |
Deteriorating |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Stable |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Parameter achieved |
Yes |
Yes |
Yes |
Yes |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Yes |
Yes |
Yes |
Yes |
No |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
No |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
No |
Unknown |
Unknown |
Yes |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Description parameter |
Value below detection limit
|
Value below detection limit
|
Value below detection limit
|
Value below detection limit. Radionuclides Cesium-134 and Cesium-137 have been monitored and show very low maximal values compared to the standard. Evaluation is however only needed special situations like a nuclear accident. |
Value below detection limit. Radionuclides Cesium-134 and Cesium-137 have been monitored and show very low maximal values compared to the standard. Evaluation is however only needed special situations like a nuclear accident. |
Value below detection limit. Radionuclides Cesium-134 and Cesium-137 have been monitored and show very low maximal values compared to the standard. Evaluation is however only needed special situations like a nuclear accident. |
Value below detection limit. Radionuclides Cesium-134 and Cesium-137 have been monitored and show very low maximal values compared to the standard. Evaluation is however only needed special situations like a nuclear accident. |
Value below detection limit
|
Value below detection limit
|
Value below detection limit
|
Value below detection limit
|
Value below detection limit
|
Value below detection limit (<5)
|
Value below detection limit (<5)
|
Value below detection limit (<5)
|
Value below detection limit (<5)
|
Value below detection limit (<5)
|
Value below detection limit (<5)
|
Value below detection limit (<5)
|
Value below detection limit (<5)
|
Value below detection limit
|
Value below detection limit (<5)
|
Value below detection limit (<5)
|
Value below detection limit (<5)
|
Value below detection limit (<5)
|
Value below detection limit (<5)
|
Value below detection limit (<70)
|
Value below detection limit (<65)
|
Value below detection limit
|
Value below detection limit
|
Value below detection limit
|
Status good: no quantitative data (CALUX screening)
|
Status good: no quantitative data (CALUX screening)
|
Status good: no quantitative data (CALUX screening)
|
Status good: no quantitative data (CALUX screening)
|
Status good: no quantitative data (CALUX screening)
|
Status good: no quantitative data (CALUX screening)
|
Status good: no quantitative data (CALUX screening)
|
Status good: no quantitative data (CALUX screening)
|
Status good: no quantitative data (CALUX screening)
|
Status good: no quantitative data (CALUX screening)
|
Status good: no quantitative data (CALUX screening)
|
Status good: no quantitative data (CALUX screening)
|
Status good: no quantitative data (CALUX screening)
|
Status good: no quantitative data (CALUX screening)
|
Status good: no quantitative data (CALUX screening)
|
Status good: no quantitative data (CALUX screening)
|
Status good: no quantitative data (CALUX screening)
|
Status good: no quantitative data (CALUX screening)
|
Status good: no quantitative data (CALUX screening)
|
Status good: no quantitative data (CALUX screening)
|
||||||||||||||||||||||||||
Related indicator |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Criteria status |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Not good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Not good |
Unknown |
Unknown |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Not good |
Not good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Description criteria |
One exceedance in plaice cfr. maximal levels as recently updated in 2023. |
One exceedance in shrimp cfr. maximal levels as recently updated in 2023. |
One exceedance in mackerel
|
One exceedance in mackerel
|
|||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Element status |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Not good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Not good |
Unknown |
Unknown |
Good |
Good |
Good |
Good |
Good |
Good |
Unknown |
Unknown |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Not good |
Not good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Description element |
exceedance in one specimen of new treshold in 2023. In the previous period, similar value encountered in one fish specimen. |
Higher maximum values observed compared to previous reporting period based on few data. |
Higher maximum values observed compared to previous reporting period based on few data. |
Only 75% of the samples are good.
|
Only 75% of the samples are good.
|
||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
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 |
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 |
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 |
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 |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Integration rule type parameter |
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
Integration rule description parameter |
Assessment in various species
|
Assessment in various species
|
Assessment in various species
|
Assessment in various species
|
Assessment in various species
|
Assessment in various species
|
Assessment in various species
|
Assessment in various species
|
Assessment in various species
|
Assessment in various species
|
Assessment in various species
|
Assessment in various species
|
Assessment in various species
|
Assessment in various species
|
Assessment in various species
|
Assessment in various species
|
Assessment in various species
|
Assessment in various species
|
Assessment in various species
|
Assessment in various species
|
Assessment in various species
|
Assessment in various species
|
Assessment in various species
|
Assessment in various species
|
Assessment in various species
|
Assessment in various species
|
Assessment in various species
|
Assessment in various species
|
Assessment in various species
|
Assessment in various species
|
Assessment in various species
|
Assessment in various species
|
Assessment in various species
|
Assessment in various species
|
Assessment in various species
|
Assessment in various species
|
Assessment in various species
|
Assessment in various species
|
Assessment in various species
|
Assessment in various species
|
Assessment in various species
|
Assessment in various species
|
Assessment in various species
|
Assessment in various species
|
Assessment in various species
|
Assessment in various species
|
Assessment in various species
|
Assessment in various species
|
Assessment in various species
|
Assessment in various species
|
Assessment in various species
|
Assessment in various species
|
Assessment in various species
|
Assessment in various species
|
Assessment in various species
|
Assessment in various species
|
Assessment in various species
|
Assessment in various species
|
Assessment in various species
|
Assessment in various species
|
Assessment in various species
|
Assessment in various species
|
Assessment in various species
|
Assessment in various species
|
Assessment in various species
|
Assessment in various species
|
Assessment in various species
|
Assessment in various species
|
Assessment in various species
|
Assessment in various species
|
Assessment in various species
|
Assessment in various species
|
Assessment in various species
|
Assessment in various species
|
Assessment in various species
|
Assessment in various species
|
Assessment in various species
|
Integration rule type criteria |
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
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 |
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 |
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 |
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 |
96.70 |
96.70 |
96.70 |
96.70 |
96.70 |
96.70 |
96.70 |
96.70 |
96.70 |
96.70 |
96.70 |
96.70 |
96.70 |
96.70 |
96.70 |
96.70 |
96.70 |
96.70 |
96.70 |
96.70 |
96.70 |
96.70 |
96.70 |
96.70 |
96.70 |
96.70 |
96.70 |
96.70 |
96.70 |
96.70 |
96.70 |
96.70 |
96.70 |
96.70 |
96.70 |
96.70 |
96.70 |
96.70 |
96.70 |
96.70 |
96.70 |
96.70 |
96.70 |
96.70 |
96.70 |
96.70 |
96.70 |
96.70 |
96.70 |
96.70 |
96.70 |
96.70 |
96.70 |
96.70 |
96.70 |
96.70 |
96.70 |
96.70 |
96.70 |
96.70 |
96.70 |
96.70 |
96.70 |
96.70 |
96.70 |
96.70 |
96.70 |
96.70 |
96.70 |
96.70 |
96.70 |
96.70 |
96.70 |
96.70 |
96.70 |
96.70 |
96.70 |
GES extent unit |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
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 |
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 |
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, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
Description overall status |
Of all fish and seafood from Belgian fish mines and originating from the Southern North Sea and Channel, one specimen showed too high values for dioxins and dioxin-like PCB’s which was not observed previously. Mercury shows one exceedance of the new and lower maximum level (established in 2023). For PFAS, methods did not allow to measure up to the required level (one exceedance for PFOS in shrimps was observed based on 2023 maximum levels). Due to new thresholds in 2023, status not necessarily deteriorating. |
Of all fish and seafood from Belgian fish mines and originating from the Southern North Sea and Channel, one specimen showed too high values for dioxins and dioxin-like PCB’s which was not observed previously. Mercury shows one exceedance of the new and lower maximum level (established in 2023). For PFAS, methods did not allow to measure up to the required level (one exceedance for PFOS in shrimps was observed based on 2023 maximum levels). Due to new thresholds in 2023, status not necessarily deteriorating. |
Of all fish and seafood from Belgian fish mines and originating from the Southern North Sea and Channel, one specimen showed too high values for dioxins and dioxin-like PCB’s which was not observed previously. Mercury shows one exceedance of the new and lower maximum level (established in 2023). For PFAS, methods did not allow to measure up to the required level (one exceedance for PFOS in shrimps was observed based on 2023 maximum levels). Due to new thresholds in 2023, status not necessarily deteriorating. |
Of all fish and seafood from Belgian fish mines and originating from the Southern North Sea and Channel, one specimen showed too high values for dioxins and dioxin-like PCB’s which was not observed previously. Mercury shows one exceedance of the new and lower maximum level (established in 2023). For PFAS, methods did not allow to measure up to the required level (one exceedance for PFOS in shrimps was observed based on 2023 maximum levels). Due to new thresholds in 2023, status not necessarily deteriorating. |
Of all fish and seafood from Belgian fish mines and originating from the Southern North Sea and Channel, one specimen showed too high values for dioxins and dioxin-like PCB’s which was not observed previously. Mercury shows one exceedance of the new and lower maximum level (established in 2023). For PFAS, methods did not allow to measure up to the required level (one exceedance for PFOS in shrimps was observed based on 2023 maximum levels). Due to new thresholds in 2023, status not necessarily deteriorating. |
Of all fish and seafood from Belgian fish mines and originating from the Southern North Sea and Channel, one specimen showed too high values for dioxins and dioxin-like PCB’s which was not observed previously. Mercury shows one exceedance of the new and lower maximum level (established in 2023). For PFAS, methods did not allow to measure up to the required level (one exceedance for PFOS in shrimps was observed based on 2023 maximum levels). Due to new thresholds in 2023, status not necessarily deteriorating. |
Of all fish and seafood from Belgian fish mines and originating from the Southern North Sea and Channel, one specimen showed too high values for dioxins and dioxin-like PCB’s which was not observed previously. Mercury shows one exceedance of the new and lower maximum level (established in 2023). For PFAS, methods did not allow to measure up to the required level (one exceedance for PFOS in shrimps was observed based on 2023 maximum levels). Due to new thresholds in 2023, status not necessarily deteriorating. |
Of all fish and seafood from Belgian fish mines and originating from the Southern North Sea and Channel, one specimen showed too high values for dioxins and dioxin-like PCB’s which was not observed previously. Mercury shows one exceedance of the new and lower maximum level (established in 2023). For PFAS, methods did not allow to measure up to the required level (one exceedance for PFOS in shrimps was observed based on 2023 maximum levels). Due to new thresholds in 2023, status not necessarily deteriorating. |
Of all fish and seafood from Belgian fish mines and originating from the Southern North Sea and Channel, one specimen showed too high values for dioxins and dioxin-like PCB’s which was not observed previously. Mercury shows one exceedance of the new and lower maximum level (established in 2023). For PFAS, methods did not allow to measure up to the required level (one exceedance for PFOS in shrimps was observed based on 2023 maximum levels). Due to new thresholds in 2023, status not necessarily deteriorating. |
Of all fish and seafood from Belgian fish mines and originating from the Southern North Sea and Channel, one specimen showed too high values for dioxins and dioxin-like PCB’s which was not observed previously. Mercury shows one exceedance of the new and lower maximum level (established in 2023). For PFAS, methods did not allow to measure up to the required level (one exceedance for PFOS in shrimps was observed based on 2023 maximum levels). Due to new thresholds in 2023, status not necessarily deteriorating. |
Of all fish and seafood from Belgian fish mines and originating from the Southern North Sea and Channel, one specimen showed too high values for dioxins and dioxin-like PCB’s which was not observed previously. Mercury shows one exceedance of the new and lower maximum level (established in 2023). For PFAS, methods did not allow to measure up to the required level (one exceedance for PFOS in shrimps was observed based on 2023 maximum levels). Due to new thresholds in 2023, status not necessarily deteriorating. |
Of all fish and seafood from Belgian fish mines and originating from the Southern North Sea and Channel, one specimen showed too high values for dioxins and dioxin-like PCB’s which was not observed previously. Mercury shows one exceedance of the new and lower maximum level (established in 2023). For PFAS, methods did not allow to measure up to the required level (one exceedance for PFOS in shrimps was observed based on 2023 maximum levels). Due to new thresholds in 2023, status not necessarily deteriorating. |
Of all fish and seafood from Belgian fish mines and originating from the Southern North Sea and Channel, one specimen showed too high values for dioxins and dioxin-like PCB’s which was not observed previously. Mercury shows one exceedance of the new and lower maximum level (established in 2023). For PFAS, methods did not allow to measure up to the required level (one exceedance for PFOS in shrimps was observed based on 2023 maximum levels). Due to new thresholds in 2023, status not necessarily deteriorating. |
Of all fish and seafood from Belgian fish mines and originating from the Southern North Sea and Channel, one specimen showed too high values for dioxins and dioxin-like PCB’s which was not observed previously. Mercury shows one exceedance of the new and lower maximum level (established in 2023). For PFAS, methods did not allow to measure up to the required level (one exceedance for PFOS in shrimps was observed based on 2023 maximum levels). Due to new thresholds in 2023, status not necessarily deteriorating. |
Of all fish and seafood from Belgian fish mines and originating from the Southern North Sea and Channel, one specimen showed too high values for dioxins and dioxin-like PCB’s which was not observed previously. Mercury shows one exceedance of the new and lower maximum level (established in 2023). For PFAS, methods did not allow to measure up to the required level (one exceedance for PFOS in shrimps was observed based on 2023 maximum levels). Due to new thresholds in 2023, status not necessarily deteriorating. |
Of all fish and seafood from Belgian fish mines and originating from the Southern North Sea and Channel, one specimen showed too high values for dioxins and dioxin-like PCB’s which was not observed previously. Mercury shows one exceedance of the new and lower maximum level (established in 2023). For PFAS, methods did not allow to measure up to the required level (one exceedance for PFOS in shrimps was observed based on 2023 maximum levels). Due to new thresholds in 2023, status not necessarily deteriorating. |
Of all fish and seafood from Belgian fish mines and originating from the Southern North Sea and Channel, one specimen showed too high values for dioxins and dioxin-like PCB’s which was not observed previously. Mercury shows one exceedance of the new and lower maximum level (established in 2023). For PFAS, methods did not allow to measure up to the required level (one exceedance for PFOS in shrimps was observed based on 2023 maximum levels). Due to new thresholds in 2023, status not necessarily deteriorating. |
Of all fish and seafood from Belgian fish mines and originating from the Southern North Sea and Channel, one specimen showed too high values for dioxins and dioxin-like PCB’s which was not observed previously. Mercury shows one exceedance of the new and lower maximum level (established in 2023). For PFAS, methods did not allow to measure up to the required level (one exceedance for PFOS in shrimps was observed based on 2023 maximum levels). Due to new thresholds in 2023, status not necessarily deteriorating. |
Of all fish and seafood from Belgian fish mines and originating from the Southern North Sea and Channel, one specimen showed too high values for dioxins and dioxin-like PCB’s which was not observed previously. Mercury shows one exceedance of the new and lower maximum level (established in 2023). For PFAS, methods did not allow to measure up to the required level (one exceedance for PFOS in shrimps was observed based on 2023 maximum levels). Due to new thresholds in 2023, status not necessarily deteriorating. |
Of all fish and seafood from Belgian fish mines and originating from the Southern North Sea and Channel, one specimen showed too high values for dioxins and dioxin-like PCB’s which was not observed previously. Mercury shows one exceedance of the new and lower maximum level (established in 2023). For PFAS, methods did not allow to measure up to the required level (one exceedance for PFOS in shrimps was observed based on 2023 maximum levels). Due to new thresholds in 2023, status not necessarily deteriorating. |
Of all fish and seafood from Belgian fish mines and originating from the Southern North Sea and Channel, one specimen showed too high values for dioxins and dioxin-like PCB’s which was not observed previously. Mercury shows one exceedance of the new and lower maximum level (established in 2023). For PFAS, methods did not allow to measure up to the required level (one exceedance for PFOS in shrimps was observed based on 2023 maximum levels). Due to new thresholds in 2023, status not necessarily deteriorating. |
Of all fish and seafood from Belgian fish mines and originating from the Southern North Sea and Channel, one specimen showed too high values for dioxins and dioxin-like PCB’s which was not observed previously. Mercury shows one exceedance of the new and lower maximum level (established in 2023). For PFAS, methods did not allow to measure up to the required level (one exceedance for PFOS in shrimps was observed based on 2023 maximum levels). Due to new thresholds in 2023, status not necessarily deteriorating. |
Of all fish and seafood from Belgian fish mines and originating from the Southern North Sea and Channel, one specimen showed too high values for dioxins and dioxin-like PCB’s which was not observed previously. Mercury shows one exceedance of the new and lower maximum level (established in 2023). For PFAS, methods did not allow to measure up to the required level (one exceedance for PFOS in shrimps was observed based on 2023 maximum levels). Due to new thresholds in 2023, status not necessarily deteriorating. |
Of all fish and seafood from Belgian fish mines and originating from the Southern North Sea and Channel, one specimen showed too high values for dioxins and dioxin-like PCB’s which was not observed previously. Mercury shows one exceedance of the new and lower maximum level (established in 2023). For PFAS, methods did not allow to measure up to the required level (one exceedance for PFOS in shrimps was observed based on 2023 maximum levels). Due to new thresholds in 2023, status not necessarily deteriorating. |
Of all fish and seafood from Belgian fish mines and originating from the Southern North Sea and Channel, one specimen showed too high values for dioxins and dioxin-like PCB’s which was not observed previously. Mercury shows one exceedance of the new and lower maximum level (established in 2023). For PFAS, methods did not allow to measure up to the required level (one exceedance for PFOS in shrimps was observed based on 2023 maximum levels). Due to new thresholds in 2023, status not necessarily deteriorating. |
Of all fish and seafood from Belgian fish mines and originating from the Southern North Sea and Channel, one specimen showed too high values for dioxins and dioxin-like PCB’s which was not observed previously. Mercury shows one exceedance of the new and lower maximum level (established in 2023). For PFAS, methods did not allow to measure up to the required level (one exceedance for PFOS in shrimps was observed based on 2023 maximum levels). Due to new thresholds in 2023, status not necessarily deteriorating. |
Of all fish and seafood from Belgian fish mines and originating from the Southern North Sea and Channel, one specimen showed too high values for dioxins and dioxin-like PCB’s which was not observed previously. Mercury shows one exceedance of the new and lower maximum level (established in 2023). For PFAS, methods did not allow to measure up to the required level (one exceedance for PFOS in shrimps was observed based on 2023 maximum levels). Due to new thresholds in 2023, status not necessarily deteriorating. |
Of all fish and seafood from Belgian fish mines and originating from the Southern North Sea and Channel, one specimen showed too high values for dioxins and dioxin-like PCB’s which was not observed previously. Mercury shows one exceedance of the new and lower maximum level (established in 2023). For PFAS, methods did not allow to measure up to the required level (one exceedance for PFOS in shrimps was observed based on 2023 maximum levels). Due to new thresholds in 2023, status not necessarily deteriorating. |
Of all fish and seafood from Belgian fish mines and originating from the Southern North Sea and Channel, one specimen showed too high values for dioxins and dioxin-like PCB’s which was not observed previously. Mercury shows one exceedance of the new and lower maximum level (established in 2023). For PFAS, methods did not allow to measure up to the required level (one exceedance for PFOS in shrimps was observed based on 2023 maximum levels). Due to new thresholds in 2023, status not necessarily deteriorating. |
Of all fish and seafood from Belgian fish mines and originating from the Southern North Sea and Channel, one specimen showed too high values for dioxins and dioxin-like PCB’s which was not observed previously. Mercury shows one exceedance of the new and lower maximum level (established in 2023). For PFAS, methods did not allow to measure up to the required level (one exceedance for PFOS in shrimps was observed based on 2023 maximum levels). Due to new thresholds in 2023, status not necessarily deteriorating. |
Of all fish and seafood from Belgian fish mines and originating from the Southern North Sea and Channel, one specimen showed too high values for dioxins and dioxin-like PCB’s which was not observed previously. Mercury shows one exceedance of the new and lower maximum level (established in 2023). For PFAS, methods did not allow to measure up to the required level (one exceedance for PFOS in shrimps was observed based on 2023 maximum levels). Due to new thresholds in 2023, status not necessarily deteriorating. |
Of all fish and seafood from Belgian fish mines and originating from the Southern North Sea and Channel, one specimen showed too high values for dioxins and dioxin-like PCB’s which was not observed previously. Mercury shows one exceedance of the new and lower maximum level (established in 2023). For PFAS, methods did not allow to measure up to the required level (one exceedance for PFOS in shrimps was observed based on 2023 maximum levels). Due to new thresholds in 2023, status not necessarily deteriorating. |
Of all fish and seafood from Belgian fish mines and originating from the Southern North Sea and Channel, one specimen showed too high values for dioxins and dioxin-like PCB’s which was not observed previously. Mercury shows one exceedance of the new and lower maximum level (established in 2023). For PFAS, methods did not allow to measure up to the required level (one exceedance for PFOS in shrimps was observed based on 2023 maximum levels). Due to new thresholds in 2023, status not necessarily deteriorating. |
Of all fish and seafood from Belgian fish mines and originating from the Southern North Sea and Channel, one specimen showed too high values for dioxins and dioxin-like PCB’s which was not observed previously. Mercury shows one exceedance of the new and lower maximum level (established in 2023). For PFAS, methods did not allow to measure up to the required level (one exceedance for PFOS in shrimps was observed based on 2023 maximum levels). Due to new thresholds in 2023, status not necessarily deteriorating. |
Of all fish and seafood from Belgian fish mines and originating from the Southern North Sea and Channel, one specimen showed too high values for dioxins and dioxin-like PCB’s which was not observed previously. Mercury shows one exceedance of the new and lower maximum level (established in 2023). For PFAS, methods did not allow to measure up to the required level (one exceedance for PFOS in shrimps was observed based on 2023 maximum levels). Due to new thresholds in 2023, status not necessarily deteriorating. |
Of all fish and seafood from Belgian fish mines and originating from the Southern North Sea and Channel, one specimen showed too high values for dioxins and dioxin-like PCB’s which was not observed previously. Mercury shows one exceedance of the new and lower maximum level (established in 2023). For PFAS, methods did not allow to measure up to the required level (one exceedance for PFOS in shrimps was observed based on 2023 maximum levels). Due to new thresholds in 2023, status not necessarily deteriorating. |
Of all fish and seafood from Belgian fish mines and originating from the Southern North Sea and Channel, one specimen showed too high values for dioxins and dioxin-like PCB’s which was not observed previously. Mercury shows one exceedance of the new and lower maximum level (established in 2023). For PFAS, methods did not allow to measure up to the required level (one exceedance for PFOS in shrimps was observed based on 2023 maximum levels). Due to new thresholds in 2023, status not necessarily deteriorating. |
Of all fish and seafood from Belgian fish mines and originating from the Southern North Sea and Channel, one specimen showed too high values for dioxins and dioxin-like PCB’s which was not observed previously. Mercury shows one exceedance of the new and lower maximum level (established in 2023). For PFAS, methods did not allow to measure up to the required level (one exceedance for PFOS in shrimps was observed based on 2023 maximum levels). Due to new thresholds in 2023, status not necessarily deteriorating. |
Of all fish and seafood from Belgian fish mines and originating from the Southern North Sea and Channel, one specimen showed too high values for dioxins and dioxin-like PCB’s which was not observed previously. Mercury shows one exceedance of the new and lower maximum level (established in 2023). For PFAS, methods did not allow to measure up to the required level (one exceedance for PFOS in shrimps was observed based on 2023 maximum levels). Due to new thresholds in 2023, status not necessarily deteriorating. |
Of all fish and seafood from Belgian fish mines and originating from the Southern North Sea and Channel, one specimen showed too high values for dioxins and dioxin-like PCB’s which was not observed previously. Mercury shows one exceedance of the new and lower maximum level (established in 2023). For PFAS, methods did not allow to measure up to the required level (one exceedance for PFOS in shrimps was observed based on 2023 maximum levels). Due to new thresholds in 2023, status not necessarily deteriorating. |
Of all fish and seafood from Belgian fish mines and originating from the Southern North Sea and Channel, one specimen showed too high values for dioxins and dioxin-like PCB’s which was not observed previously. Mercury shows one exceedance of the new and lower maximum level (established in 2023). For PFAS, methods did not allow to measure up to the required level (one exceedance for PFOS in shrimps was observed based on 2023 maximum levels). Due to new thresholds in 2023, status not necessarily deteriorating. |
Of all fish and seafood from Belgian fish mines and originating from the Southern North Sea and Channel, one specimen showed too high values for dioxins and dioxin-like PCB’s which was not observed previously. Mercury shows one exceedance of the new and lower maximum level (established in 2023). For PFAS, methods did not allow to measure up to the required level (one exceedance for PFOS in shrimps was observed based on 2023 maximum levels). Due to new thresholds in 2023, status not necessarily deteriorating. |
Of all fish and seafood from Belgian fish mines and originating from the Southern North Sea and Channel, one specimen showed too high values for dioxins and dioxin-like PCB’s which was not observed previously. Mercury shows one exceedance of the new and lower maximum level (established in 2023). For PFAS, methods did not allow to measure up to the required level (one exceedance for PFOS in shrimps was observed based on 2023 maximum levels). Due to new thresholds in 2023, status not necessarily deteriorating. |
Of all fish and seafood from Belgian fish mines and originating from the Southern North Sea and Channel, one specimen showed too high values for dioxins and dioxin-like PCB’s which was not observed previously. Mercury shows one exceedance of the new and lower maximum level (established in 2023). For PFAS, methods did not allow to measure up to the required level (one exceedance for PFOS in shrimps was observed based on 2023 maximum levels). Due to new thresholds in 2023, status not necessarily deteriorating. |
Of all fish and seafood from Belgian fish mines and originating from the Southern North Sea and Channel, one specimen showed too high values for dioxins and dioxin-like PCB’s which was not observed previously. Mercury shows one exceedance of the new and lower maximum level (established in 2023). For PFAS, methods did not allow to measure up to the required level (one exceedance for PFOS in shrimps was observed based on 2023 maximum levels). Due to new thresholds in 2023, status not necessarily deteriorating. |
Of all fish and seafood from Belgian fish mines and originating from the Southern North Sea and Channel, one specimen showed too high values for dioxins and dioxin-like PCB’s which was not observed previously. Mercury shows one exceedance of the new and lower maximum level (established in 2023). For PFAS, methods did not allow to measure up to the required level (one exceedance for PFOS in shrimps was observed based on 2023 maximum levels). Due to new thresholds in 2023, status not necessarily deteriorating. |
Of all fish and seafood from Belgian fish mines and originating from the Southern North Sea and Channel, one specimen showed too high values for dioxins and dioxin-like PCB’s which was not observed previously. Mercury shows one exceedance of the new and lower maximum level (established in 2023). For PFAS, methods did not allow to measure up to the required level (one exceedance for PFOS in shrimps was observed based on 2023 maximum levels). Due to new thresholds in 2023, status not necessarily deteriorating. |
Of all fish and seafood from Belgian fish mines and originating from the Southern North Sea and Channel, one specimen showed too high values for dioxins and dioxin-like PCB’s which was not observed previously. Mercury shows one exceedance of the new and lower maximum level (established in 2023). For PFAS, methods did not allow to measure up to the required level (one exceedance for PFOS in shrimps was observed based on 2023 maximum levels). Due to new thresholds in 2023, status not necessarily deteriorating. |
Of all fish and seafood from Belgian fish mines and originating from the Southern North Sea and Channel, one specimen showed too high values for dioxins and dioxin-like PCB’s which was not observed previously. Mercury shows one exceedance of the new and lower maximum level (established in 2023). For PFAS, methods did not allow to measure up to the required level (one exceedance for PFOS in shrimps was observed based on 2023 maximum levels). Due to new thresholds in 2023, status not necessarily deteriorating. |
Of all fish and seafood from Belgian fish mines and originating from the Southern North Sea and Channel, one specimen showed too high values for dioxins and dioxin-like PCB’s which was not observed previously. Mercury shows one exceedance of the new and lower maximum level (established in 2023). For PFAS, methods did not allow to measure up to the required level (one exceedance for PFOS in shrimps was observed based on 2023 maximum levels). Due to new thresholds in 2023, status not necessarily deteriorating. |
Of all fish and seafood from Belgian fish mines and originating from the Southern North Sea and Channel, one specimen showed too high values for dioxins and dioxin-like PCB’s which was not observed previously. Mercury shows one exceedance of the new and lower maximum level (established in 2023). For PFAS, methods did not allow to measure up to the required level (one exceedance for PFOS in shrimps was observed based on 2023 maximum levels). Due to new thresholds in 2023, status not necessarily deteriorating. |
Of all fish and seafood from Belgian fish mines and originating from the Southern North Sea and Channel, one specimen showed too high values for dioxins and dioxin-like PCB’s which was not observed previously. Mercury shows one exceedance of the new and lower maximum level (established in 2023). For PFAS, methods did not allow to measure up to the required level (one exceedance for PFOS in shrimps was observed based on 2023 maximum levels). Due to new thresholds in 2023, status not necessarily deteriorating. |
Of all fish and seafood from Belgian fish mines and originating from the Southern North Sea and Channel, one specimen showed too high values for dioxins and dioxin-like PCB’s which was not observed previously. Mercury shows one exceedance of the new and lower maximum level (established in 2023). For PFAS, methods did not allow to measure up to the required level (one exceedance for PFOS in shrimps was observed based on 2023 maximum levels). Due to new thresholds in 2023, status not necessarily deteriorating. |
Of all fish and seafood from Belgian fish mines and originating from the Southern North Sea and Channel, one specimen showed too high values for dioxins and dioxin-like PCB’s which was not observed previously. Mercury shows one exceedance of the new and lower maximum level (established in 2023). For PFAS, methods did not allow to measure up to the required level (one exceedance for PFOS in shrimps was observed based on 2023 maximum levels). Due to new thresholds in 2023, status not necessarily deteriorating. |
Of all fish and seafood from Belgian fish mines and originating from the Southern North Sea and Channel, one specimen showed too high values for dioxins and dioxin-like PCB’s which was not observed previously. Mercury shows one exceedance of the new and lower maximum level (established in 2023). For PFAS, methods did not allow to measure up to the required level (one exceedance for PFOS in shrimps was observed based on 2023 maximum levels). Due to new thresholds in 2023, status not necessarily deteriorating. |
Of all fish and seafood from Belgian fish mines and originating from the Southern North Sea and Channel, one specimen showed too high values for dioxins and dioxin-like PCB’s which was not observed previously. Mercury shows one exceedance of the new and lower maximum level (established in 2023). For PFAS, methods did not allow to measure up to the required level (one exceedance for PFOS in shrimps was observed based on 2023 maximum levels). Due to new thresholds in 2023, status not necessarily deteriorating. |
Of all fish and seafood from Belgian fish mines and originating from the Southern North Sea and Channel, one specimen showed too high values for dioxins and dioxin-like PCB’s which was not observed previously. Mercury shows one exceedance of the new and lower maximum level (established in 2023). For PFAS, methods did not allow to measure up to the required level (one exceedance for PFOS in shrimps was observed based on 2023 maximum levels). Due to new thresholds in 2023, status not necessarily deteriorating. |
Of all fish and seafood from Belgian fish mines and originating from the Southern North Sea and Channel, one specimen showed too high values for dioxins and dioxin-like PCB’s which was not observed previously. Mercury shows one exceedance of the new and lower maximum level (established in 2023). For PFAS, methods did not allow to measure up to the required level (one exceedance for PFOS in shrimps was observed based on 2023 maximum levels). Due to new thresholds in 2023, status not necessarily deteriorating. |
Of all fish and seafood from Belgian fish mines and originating from the Southern North Sea and Channel, one specimen showed too high values for dioxins and dioxin-like PCB’s which was not observed previously. Mercury shows one exceedance of the new and lower maximum level (established in 2023). For PFAS, methods did not allow to measure up to the required level (one exceedance for PFOS in shrimps was observed based on 2023 maximum levels). Due to new thresholds in 2023, status not necessarily deteriorating. |
Of all fish and seafood from Belgian fish mines and originating from the Southern North Sea and Channel, one specimen showed too high values for dioxins and dioxin-like PCB’s which was not observed previously. Mercury shows one exceedance of the new and lower maximum level (established in 2023). For PFAS, methods did not allow to measure up to the required level (one exceedance for PFOS in shrimps was observed based on 2023 maximum levels). Due to new thresholds in 2023, status not necessarily deteriorating. |
Of all fish and seafood from Belgian fish mines and originating from the Southern North Sea and Channel, one specimen showed too high values for dioxins and dioxin-like PCB’s which was not observed previously. Mercury shows one exceedance of the new and lower maximum level (established in 2023). For PFAS, methods did not allow to measure up to the required level (one exceedance for PFOS in shrimps was observed based on 2023 maximum levels). Due to new thresholds in 2023, status not necessarily deteriorating. |
Of all fish and seafood from Belgian fish mines and originating from the Southern North Sea and Channel, one specimen showed too high values for dioxins and dioxin-like PCB’s which was not observed previously. Mercury shows one exceedance of the new and lower maximum level (established in 2023). For PFAS, methods did not allow to measure up to the required level (one exceedance for PFOS in shrimps was observed based on 2023 maximum levels). Due to new thresholds in 2023, status not necessarily deteriorating. |
Of all fish and seafood from Belgian fish mines and originating from the Southern North Sea and Channel, one specimen showed too high values for dioxins and dioxin-like PCB’s which was not observed previously. Mercury shows one exceedance of the new and lower maximum level (established in 2023). For PFAS, methods did not allow to measure up to the required level (one exceedance for PFOS in shrimps was observed based on 2023 maximum levels). Due to new thresholds in 2023, status not necessarily deteriorating. |
Of all fish and seafood from Belgian fish mines and originating from the Southern North Sea and Channel, one specimen showed too high values for dioxins and dioxin-like PCB’s which was not observed previously. Mercury shows one exceedance of the new and lower maximum level (established in 2023). For PFAS, methods did not allow to measure up to the required level (one exceedance for PFOS in shrimps was observed based on 2023 maximum levels). Due to new thresholds in 2023, status not necessarily deteriorating. |
Of all fish and seafood from Belgian fish mines and originating from the Southern North Sea and Channel, one specimen showed too high values for dioxins and dioxin-like PCB’s which was not observed previously. Mercury shows one exceedance of the new and lower maximum level (established in 2023). For PFAS, methods did not allow to measure up to the required level (one exceedance for PFOS in shrimps was observed based on 2023 maximum levels). Due to new thresholds in 2023, status not necessarily deteriorating. |
Of all fish and seafood from Belgian fish mines and originating from the Southern North Sea and Channel, one specimen showed too high values for dioxins and dioxin-like PCB’s which was not observed previously. Mercury shows one exceedance of the new and lower maximum level (established in 2023). For PFAS, methods did not allow to measure up to the required level (one exceedance for PFOS in shrimps was observed based on 2023 maximum levels). Due to new thresholds in 2023, status not necessarily deteriorating. |
Of all fish and seafood from Belgian fish mines and originating from the Southern North Sea and Channel, one specimen showed too high values for dioxins and dioxin-like PCB’s which was not observed previously. Mercury shows one exceedance of the new and lower maximum level (established in 2023). For PFAS, methods did not allow to measure up to the required level (one exceedance for PFOS in shrimps was observed based on 2023 maximum levels). Due to new thresholds in 2023, status not necessarily deteriorating. |
Of all fish and seafood from Belgian fish mines and originating from the Southern North Sea and Channel, one specimen showed too high values for dioxins and dioxin-like PCB’s which was not observed previously. Mercury shows one exceedance of the new and lower maximum level (established in 2023). For PFAS, methods did not allow to measure up to the required level (one exceedance for PFOS in shrimps was observed based on 2023 maximum levels). Due to new thresholds in 2023, status not necessarily deteriorating. |
Of all fish and seafood from Belgian fish mines and originating from the Southern North Sea and Channel, one specimen showed too high values for dioxins and dioxin-like PCB’s which was not observed previously. Mercury shows one exceedance of the new and lower maximum level (established in 2023). For PFAS, methods did not allow to measure up to the required level (one exceedance for PFOS in shrimps was observed based on 2023 maximum levels). Due to new thresholds in 2023, status not necessarily deteriorating. |
Of all fish and seafood from Belgian fish mines and originating from the Southern North Sea and Channel, one specimen showed too high values for dioxins and dioxin-like PCB’s which was not observed previously. Mercury shows one exceedance of the new and lower maximum level (established in 2023). For PFAS, methods did not allow to measure up to the required level (one exceedance for PFOS in shrimps was observed based on 2023 maximum levels). Due to new thresholds in 2023, status not necessarily deteriorating. |
Of all fish and seafood from Belgian fish mines and originating from the Southern North Sea and Channel, one specimen showed too high values for dioxins and dioxin-like PCB’s which was not observed previously. Mercury shows one exceedance of the new and lower maximum level (established in 2023). For PFAS, methods did not allow to measure up to the required level (one exceedance for PFOS in shrimps was observed based on 2023 maximum levels). Due to new thresholds in 2023, status not necessarily deteriorating. |
Of all fish and seafood from Belgian fish mines and originating from the Southern North Sea and Channel, one specimen showed too high values for dioxins and dioxin-like PCB’s which was not observed previously. Mercury shows one exceedance of the new and lower maximum level (established in 2023). For PFAS, methods did not allow to measure up to the required level (one exceedance for PFOS in shrimps was observed based on 2023 maximum levels). Due to new thresholds in 2023, status not necessarily deteriorating. |
Of all fish and seafood from Belgian fish mines and originating from the Southern North Sea and Channel, one specimen showed too high values for dioxins and dioxin-like PCB’s which was not observed previously. Mercury shows one exceedance of the new and lower maximum level (established in 2023). For PFAS, methods did not allow to measure up to the required level (one exceedance for PFOS in shrimps was observed based on 2023 maximum levels). Due to new thresholds in 2023, status not necessarily deteriorating. |
Of all fish and seafood from Belgian fish mines and originating from the Southern North Sea and Channel, one specimen showed too high values for dioxins and dioxin-like PCB’s which was not observed previously. Mercury shows one exceedance of the new and lower maximum level (established in 2023). For PFAS, methods did not allow to measure up to the required level (one exceedance for PFOS in shrimps was observed based on 2023 maximum levels). Due to new thresholds in 2023, status not necessarily deteriorating. |
Of all fish and seafood from Belgian fish mines and originating from the Southern North Sea and Channel, one specimen showed too high values for dioxins and dioxin-like PCB’s which was not observed previously. Mercury shows one exceedance of the new and lower maximum level (established in 2023). For PFAS, methods did not allow to measure up to the required level (one exceedance for PFOS in shrimps was observed based on 2023 maximum levels). Due to new thresholds in 2023, status not necessarily deteriorating. |
Of all fish and seafood from Belgian fish mines and originating from the Southern North Sea and Channel, one specimen showed too high values for dioxins and dioxin-like PCB’s which was not observed previously. Mercury shows one exceedance of the new and lower maximum level (established in 2023). For PFAS, methods did not allow to measure up to the required level (one exceedance for PFOS in shrimps was observed based on 2023 maximum levels). Due to new thresholds in 2023, status not necessarily deteriorating. |
Of all fish and seafood from Belgian fish mines and originating from the Southern North Sea and Channel, one specimen showed too high values for dioxins and dioxin-like PCB’s which was not observed previously. Mercury shows one exceedance of the new and lower maximum level (established in 2023). For PFAS, methods did not allow to measure up to the required level (one exceedance for PFOS in shrimps was observed based on 2023 maximum levels). Due to new thresholds in 2023, status not necessarily deteriorating. |
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 |
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 |
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 |
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 |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
Test results |
False |
False |
False |
False |
Correct |
Correct |
Correct |
Correct |
False |
False |
False |
False |
False |
False |
False |
False |
False |
False |
False |
False |
False |
False |
False |
False |
False |
False |
False |
False |
False |
False |
False |
Correct |
Correct |
Correct |
Correct |
Correct |
Correct |
False |
Correct |
Correct |
False |
Correct |
Correct |
Correct |
Correct |
Correct |
Correct |
Correct |
False |
False |
False |
False |
False |
False |
False |
False |
False |
False |
False |
False |
False |
False |
False |
False |
False |
False |
False |
False |
False |
False |
False |
False |
False |
False |
False |
False |
False |