Member State report / Art8 / 2018 / D9 / Belgium / NE Atlantic: Greater North Sea
| Report type | Member State report to Commission |
| MSFD Article | Art. 8 Initial assessment (and Art. 17 updates) |
| Report due | 2018-10-15 |
| GES Descriptor | D9 Contaminants in seafood |
| Member State | Belgium |
| Region/subregion | NE Atlantic: Greater North Sea |
| Reported by | RBINS - Scientific Service MUMM |
| Report date | 2020-01-14 |
| Report access | ART8_GES_BE_20200110.xml |
Greater North Sea, incl. the Kattegat and the English Channel (ANS)
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
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D9
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D9
|
D9
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D9
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D9
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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
|
Element |
Benzo(a)pyrene |
Cadmium |
Cadmium |
Cadmium |
Cadmium |
Cesium-134 |
Cesium-134 |
Cesium-137 |
Cesium-137 |
Dioxins and dioxin-like compounds (7 PCDDs and 10 PCDFs and 12 PCB-DLs) |
Dioxins and dioxin-like compounds (7 PCDDs and 10 PCDFs and 12 PCB-DLs) |
Dioxins and dioxin-like compounds (7 PCDDs and 10 PCDFs and 12 PCB-DLs) |
Dioxins and dioxin-like compounds (7 PCDDs and 10 PCDFs and 12 PCB-DLs) |
Dioxins and dioxin-like compounds (7 PCDDs and 10 PCDFs and 12 PCB-DLs) |
Dioxins and dioxin-like compounds (7 PCDDs and 10 PCDFs and 12 PCB-DLs) |
Dioxins and dioxin-like compounds (7 PCDDs and 10 PCDFs and 12 PCB-DLs) |
Dioxins and dioxin-like compounds (7 PCDDs and 10 PCDFs and 12 PCB-DLs) |
Lead |
Lead |
Lead |
Lead |
Mercury |
Mercury |
Mercury |
Mercury |
Polychlorinated biphenyls (7 PCB: 28,52,101,118,138,153,180) |
Polychlorinated biphenyls (7 PCB: 28,52,101,118,138,153,180) |
Polychlorinated biphenyls (7 PCB: 28,52,101,118,138,153,180) |
Polychlorinated biphenyls (7 PCB: 28,52,101,118,138,153,180) |
Polychlorinated biphenyls (7 PCB: 28,52,101,118,138,153,180) |
Polychlorinated biphenyls (7 PCB: 28,52,101,118,138,153,180) |
Polychlorinated biphenyls (7 PCB: 28,52,101,118,138,153,180) |
Polychlorinated biphenyls (7 PCB: 28,52,101,118,138,153,180) |
Total PAHs (Benzo(a)pyrene, Benzo(b)fluoranthene, Benzo(k)fluoranthene, Benzo(ghi)perylene, Indeno(1,2,3-cd)pyrene) |
Total dioxins and furans (PCDD and PCDF) |
Total dioxins and furans (PCDD and PCDF) |
Total dioxins and furans (PCDD and PCDF) |
Total dioxins and furans (PCDD and PCDF) |
Total dioxins and furans (PCDD and PCDF) |
Total dioxins and furans (PCDD and PCDF) |
Total dioxins and furans (PCDD and PCDF) |
Element code |
CAS_50-32-8 |
CAS_7440-43-9 |
CAS_7440-43-9 |
CAS_7440-43-9 |
CAS_7440-43-9 |
CS134 |
CS134 |
CS002370 |
CS002370 |
EEA_33-58-9 |
EEA_33-58-9 |
EEA_33-58-9 |
EEA_33-58-9 |
EEA_33-58-9 |
EEA_33-58-9 |
EEA_33-58-9 |
EEA_33-58-9 |
CAS_7439-92-1 |
CAS_7439-92-1 |
CAS_7439-92-1 |
CAS_7439-92-1 |
CAS_7439-97-6 |
CAS_7439-97-6 |
CAS_7439-97-6 |
CAS_7439-97-6 |
EEA_33-38-5 |
EEA_33-38-5 |
EEA_33-38-5 |
EEA_33-38-5 |
EEA_33-38-5 |
EEA_33-38-5 |
EEA_33-38-5 |
EEA_33-38-5 |
EEA_33-56-7 |
EEA_33-40-9 |
EEA_33-40-9 |
EEA_33-40-9 |
EEA_33-40-9 |
EEA_33-40-9 |
EEA_33-40-9 |
EEA_33-40-9 |
Element code source |
Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view
|
Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view
|
Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view
|
Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view
|
Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view
|
Contaminants (D8-D9) http://vocab.ices.dk/?ref=37
|
Contaminants (D8-D9) http://vocab.ices.dk/?ref=37
|
Contaminants (D8-D9) http://seadatanet.maris2.nl/v_bodc_vocab_v2/vocab_relations.asp?lib=P02
|
Contaminants (D8-D9) http://seadatanet.maris2.nl/v_bodc_vocab_v2/vocab_relations.asp?lib=P02
|
Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view
|
Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view
|
Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view
|
Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view
|
Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view
|
Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view
|
Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view
|
Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view
|
Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view
|
Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view
|
Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view
|
Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view
|
Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view
|
Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view
|
Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view
|
Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view
|
Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view
|
Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view
|
Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view
|
Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view
|
Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view
|
Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view
|
Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view
|
Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view
|
Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view
|
Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view
|
Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view
|
Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view
|
Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view
|
Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view
|
Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view
|
Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view
|
Element 2 |
Crangon crangon
|
Crangon crangon
|
Osteichthyes
|
Pecten jacobeus
|
Pleuronectes platessa
|
Crustacea
|
Pisces
|
Crustacea
|
Pisces
|
Crangon crangon
|
Decapodiformes
|
Osteichthyes
|
Pecten jacobeus
|
Pleuronectes platessa
|
Raja aquila
|
Selachimorpha
|
Solea solea
|
Crangon crangon
|
Osteichthyes
|
Pecten jacobeus
|
Pleuronectes platessa
|
Crangon crangon
|
Osteichthyes
|
Pecten jacobeus
|
Pleuronectes platessa
|
Crangon crangon
|
Decapodiformes
|
Osteichthyes
|
Pecten jacobeus
|
Pleuronectes platessa
|
Raja aquila
|
Selachimorpha
|
Solea solea
|
Pecten jacobeus
|
Decapodiformes
|
Osteichthyes
|
Pecten jacobeus
|
Pleuronectes platessa
|
Raja aquila
|
Selachimorpha
|
Solea solea
|
Element 2 code |
107552
|
107552
|
152352
|
394429
|
127143
|
1066
|
11676
|
1066
|
11676
|
107552
|
325342
|
152352
|
394429
|
127143
|
298854
|
368408
|
127160
|
107552
|
152352
|
394429
|
127143
|
107552
|
152352
|
394429
|
127143
|
107552
|
325342
|
152352
|
394429
|
127143
|
298854
|
368408
|
127160
|
394429
|
325342
|
152352
|
394429
|
127143
|
298854
|
368408
|
127160
|
Element 2 code source |
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Element source |
EU |
EU |
EU |
EU |
EU |
EU |
EU |
EU |
EU |
EU |
EU |
EU |
EU |
EU |
EU |
EU |
EU |
EU |
EU |
EU |
EU |
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
|
D9C1
|
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-MU
|
CONC-B-MU
|
Concentration in biota
|
CONC-B-MU
|
CONC-B-MU
|
CONC-B-MU
|
CONC-B-MU
|
CONC-B-MU
|
CONC-B-MU
|
CONC-B-MU
|
CONC-B-MU
|
Concentration in biota
|
CONC-B-MU
|
CONC-B-MU
|
CONC-B-MU
|
CONC-B-MU
|
CONC-B-MU
|
CONC-B-MU
|
Concentration in biota
|
CONC-B-MU
|
CONC-B-MU
|
CONC-B-MU
|
Concentration in biota
|
CONC-B-MU
|
CONC-B-MU
|
CONC-B-MU
|
CONC-B-MU
|
Concentration in biota
|
CONC-B-MU
|
CONC-B-MU
|
CONC-B-MU
|
CONC-B-MU
|
Concentration in biota
|
CONC-B-MU
|
CONC-B-MU
|
Concentration in biota
|
CONC-B-MU
|
CONC-B-MU
|
CONC-B-MU
|
CONC-B-MU
|
Parameter other |
|||||||||||||||||||||||||||||||||||||||||
Threshold value upper |
5.0 |
0.5 |
0.05 |
1.0 |
0.05 |
600.0 |
600.0 |
600.0 |
600.0 |
6.5 |
6.5 |
6.5 |
6.5 |
6.5 |
6.5 |
6.5 |
6.5 |
0.5 |
0.3 |
1.5 |
0.3 |
0.5 |
0.5 |
0.5 |
0.5 |
75.0 |
75.0 |
75.0 |
75.0 |
75.0 |
75.0 |
75.0 |
75.0 |
0.5 |
3.5 |
3.5 |
3.5 |
3.5 |
3.5 |
3.5 |
3.5 |
Threshold value lower |
|||||||||||||||||||||||||||||||||||||||||
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)
|
Other (specify)
|
Other (specify)
|
Other (specify)
|
Other (specify)
|
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)
|
Threshold value source other |
EC 773/2008
|
EC 773/2008
|
EC 773/2008
|
EC 773/2008
|
|||||||||||||||||||||||||||||||||||||
Value achieved upper |
0.9 |
0.014 |
0.01 |
0.36 |
0.01 |
5.0 |
5.0 |
5.0 |
6.0 |
0.0067 |
0.02 |
0.088 |
0.02 |
0.101 |
0.36 |
0.011 |
0.21 |
1.4 |
1.6 |
4.9 |
1.2 |
4.11 |
1.4 |
1.2 |
0.46 |
0.9 |
0.61 |
||||||||||||||
Value achieved lower |
0.23 |
0.9 |
0.6 |
1.0 |
0.7 |
0.027 |
0.1 |
0.01 |
0.061 |
1.2 |
1.2 |
1.2 |
0.21 |
0.46 |
0.61 |
||||||||||||||||||||||||||
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
|
milligram per kilogram of wet weight
|
Becquerels per kilogram of wet weight
|
Becquerels per kilogram of wet weight
|
Becquerels per kilogram of wet weight
|
Becquerels per kilogram of wet weight
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
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
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
microgram per kilogram of wet weight
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Value unit other |
pg TEQ/G ww
|
pg TEQ/G ww
|
pg TEQ/G ww
|
pg TEQ/G ww
|
pg TEQ/G ww
|
pg TEQ/G ww
|
pg TEQ/G ww
|
pg TEQ/G ww
|
ng/g ww
|
ng/g ww
|
ng/g ww
|
ng/g ww
|
ng/g ww
|
ng/g ww
|
ng/g ww
|
ng/g ww
|
pg TEQ/G ww
|
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 |
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 |
Parameter achieved |
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 |
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
|
Values below detection limit
|
Values below detection limit
|
Values below detection limit
|
Values 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)
|
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)
|
|||||||||||||||||
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 |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Description criteria |
|||||||||||||||||||||||||||||||||||||||||
Element status |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Description element |
|||||||||||||||||||||||||||||||||||||||||
Integration rule type parameter |
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
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
|
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
|
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 |
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 |
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 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 |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
Description overall status |
All fish, mollusc and crustacean samples from the Belgian southern North Sea and the Channel appear, after analysis, to be suitable for human consumption. The substances analyzed are metals (cadmium, mercury and lead), dioxins and dioxin-like PCBs, PCBs, PAHs, Cesium 134 and Cesium 137. These results are in accordance with the results prior to the 2011-2016 period.
|
All fish, mollusc and crustacean samples from the Belgian southern North Sea and the Channel appear, after analysis, to be suitable for human consumption. The substances analyzed are metals (cadmium, mercury and lead), dioxins and dioxin-like PCBs, PCBs, PAHs, Cesium 134 and Cesium 137. These results are in accordance with the results prior to the 2011-2016 period.
|
All fish, mollusc and crustacean samples from the Belgian southern North Sea and the Channel appear, after analysis, to be suitable for human consumption. The substances analyzed are metals (cadmium, mercury and lead), dioxins and dioxin-like PCBs, PCBs, PAHs, Cesium 134 and Cesium 137. These results are in accordance with the results prior to the 2011-2016 period.
|
All fish, mollusc and crustacean samples from the Belgian southern North Sea and the Channel appear, after analysis, to be suitable for human consumption. The substances analyzed are metals (cadmium, mercury and lead), dioxins and dioxin-like PCBs, PCBs, PAHs, Cesium 134 and Cesium 137. These results are in accordance with the results prior to the 2011-2016 period.
|
All fish, mollusc and crustacean samples from the Belgian southern North Sea and the Channel appear, after analysis, to be suitable for human consumption. The substances analyzed are metals (cadmium, mercury and lead), dioxins and dioxin-like PCBs, PCBs, PAHs, Cesium 134 and Cesium 137. These results are in accordance with the results prior to the 2011-2016 period.
|
All fish, mollusc and crustacean samples from the Belgian southern North Sea and the Channel appear, after analysis, to be suitable for human consumption. The substances analyzed are metals (cadmium, mercury and lead), dioxins and dioxin-like PCBs, PCBs, PAHs, Cesium 134 and Cesium 137. These results are in accordance with the results prior to the 2011-2016 period.
|
All fish, mollusc and crustacean samples from the Belgian southern North Sea and the Channel appear, after analysis, to be suitable for human consumption. The substances analyzed are metals (cadmium, mercury and lead), dioxins and dioxin-like PCBs, PCBs, PAHs, Cesium 134 and Cesium 137. These results are in accordance with the results prior to the 2011-2016 period.
|
All fish, mollusc and crustacean samples from the Belgian southern North Sea and the Channel appear, after analysis, to be suitable for human consumption. The substances analyzed are metals (cadmium, mercury and lead), dioxins and dioxin-like PCBs, PCBs, PAHs, Cesium 134 and Cesium 137. These results are in accordance with the results prior to the 2011-2016 period.
|
All fish, mollusc and crustacean samples from the Belgian southern North Sea and the Channel appear, after analysis, to be suitable for human consumption. The substances analyzed are metals (cadmium, mercury and lead), dioxins and dioxin-like PCBs, PCBs, PAHs, Cesium 134 and Cesium 137. These results are in accordance with the results prior to the 2011-2016 period.
|
All fish, mollusc and crustacean samples from the Belgian southern North Sea and the Channel appear, after analysis, to be suitable for human consumption. The substances analyzed are metals (cadmium, mercury and lead), dioxins and dioxin-like PCBs, PCBs, PAHs, Cesium 134 and Cesium 137. These results are in accordance with the results prior to the 2011-2016 period.
|
All fish, mollusc and crustacean samples from the Belgian southern North Sea and the Channel appear, after analysis, to be suitable for human consumption. The substances analyzed are metals (cadmium, mercury and lead), dioxins and dioxin-like PCBs, PCBs, PAHs, Cesium 134 and Cesium 137. These results are in accordance with the results prior to the 2011-2016 period.
|
All fish, mollusc and crustacean samples from the Belgian southern North Sea and the Channel appear, after analysis, to be suitable for human consumption. The substances analyzed are metals (cadmium, mercury and lead), dioxins and dioxin-like PCBs, PCBs, PAHs, Cesium 134 and Cesium 137. These results are in accordance with the results prior to the 2011-2016 period.
|
All fish, mollusc and crustacean samples from the Belgian southern North Sea and the Channel appear, after analysis, to be suitable for human consumption. The substances analyzed are metals (cadmium, mercury and lead), dioxins and dioxin-like PCBs, PCBs, PAHs, Cesium 134 and Cesium 137. These results are in accordance with the results prior to the 2011-2016 period.
|
All fish, mollusc and crustacean samples from the Belgian southern North Sea and the Channel appear, after analysis, to be suitable for human consumption. The substances analyzed are metals (cadmium, mercury and lead), dioxins and dioxin-like PCBs, PCBs, PAHs, Cesium 134 and Cesium 137. These results are in accordance with the results prior to the 2011-2016 period.
|
All fish, mollusc and crustacean samples from the Belgian southern North Sea and the Channel appear, after analysis, to be suitable for human consumption. The substances analyzed are metals (cadmium, mercury and lead), dioxins and dioxin-like PCBs, PCBs, PAHs, Cesium 134 and Cesium 137. These results are in accordance with the results prior to the 2011-2016 period.
|
All fish, mollusc and crustacean samples from the Belgian southern North Sea and the Channel appear, after analysis, to be suitable for human consumption. The substances analyzed are metals (cadmium, mercury and lead), dioxins and dioxin-like PCBs, PCBs, PAHs, Cesium 134 and Cesium 137. These results are in accordance with the results prior to the 2011-2016 period.
|
All fish, mollusc and crustacean samples from the Belgian southern North Sea and the Channel appear, after analysis, to be suitable for human consumption. The substances analyzed are metals (cadmium, mercury and lead), dioxins and dioxin-like PCBs, PCBs, PAHs, Cesium 134 and Cesium 137. These results are in accordance with the results prior to the 2011-2016 period.
|
All fish, mollusc and crustacean samples from the Belgian southern North Sea and the Channel appear, after analysis, to be suitable for human consumption. The substances analyzed are metals (cadmium, mercury and lead), dioxins and dioxin-like PCBs, PCBs, PAHs, Cesium 134 and Cesium 137. These results are in accordance with the results prior to the 2011-2016 period.
|
All fish, mollusc and crustacean samples from the Belgian southern North Sea and the Channel appear, after analysis, to be suitable for human consumption. The substances analyzed are metals (cadmium, mercury and lead), dioxins and dioxin-like PCBs, PCBs, PAHs, Cesium 134 and Cesium 137. These results are in accordance with the results prior to the 2011-2016 period.
|
All fish, mollusc and crustacean samples from the Belgian southern North Sea and the Channel appear, after analysis, to be suitable for human consumption. The substances analyzed are metals (cadmium, mercury and lead), dioxins and dioxin-like PCBs, PCBs, PAHs, Cesium 134 and Cesium 137. These results are in accordance with the results prior to the 2011-2016 period.
|
All fish, mollusc and crustacean samples from the Belgian southern North Sea and the Channel appear, after analysis, to be suitable for human consumption. The substances analyzed are metals (cadmium, mercury and lead), dioxins and dioxin-like PCBs, PCBs, PAHs, Cesium 134 and Cesium 137. These results are in accordance with the results prior to the 2011-2016 period.
|
All fish, mollusc and crustacean samples from the Belgian southern North Sea and the Channel appear, after analysis, to be suitable for human consumption. The substances analyzed are metals (cadmium, mercury and lead), dioxins and dioxin-like PCBs, PCBs, PAHs, Cesium 134 and Cesium 137. These results are in accordance with the results prior to the 2011-2016 period.
|
All fish, mollusc and crustacean samples from the Belgian southern North Sea and the Channel appear, after analysis, to be suitable for human consumption. The substances analyzed are metals (cadmium, mercury and lead), dioxins and dioxin-like PCBs, PCBs, PAHs, Cesium 134 and Cesium 137. These results are in accordance with the results prior to the 2011-2016 period.
|
All fish, mollusc and crustacean samples from the Belgian southern North Sea and the Channel appear, after analysis, to be suitable for human consumption. The substances analyzed are metals (cadmium, mercury and lead), dioxins and dioxin-like PCBs, PCBs, PAHs, Cesium 134 and Cesium 137. These results are in accordance with the results prior to the 2011-2016 period.
|
All fish, mollusc and crustacean samples from the Belgian southern North Sea and the Channel appear, after analysis, to be suitable for human consumption. The substances analyzed are metals (cadmium, mercury and lead), dioxins and dioxin-like PCBs, PCBs, PAHs, Cesium 134 and Cesium 137. These results are in accordance with the results prior to the 2011-2016 period.
|
All fish, mollusc and crustacean samples from the Belgian southern North Sea and the Channel appear, after analysis, to be suitable for human consumption. The substances analyzed are metals (cadmium, mercury and lead), dioxins and dioxin-like PCBs, PCBs, PAHs, Cesium 134 and Cesium 137. These results are in accordance with the results prior to the 2011-2016 period.
|
All fish, mollusc and crustacean samples from the Belgian southern North Sea and the Channel appear, after analysis, to be suitable for human consumption. The substances analyzed are metals (cadmium, mercury and lead), dioxins and dioxin-like PCBs, PCBs, PAHs, Cesium 134 and Cesium 137. These results are in accordance with the results prior to the 2011-2016 period.
|
All fish, mollusc and crustacean samples from the Belgian southern North Sea and the Channel appear, after analysis, to be suitable for human consumption. The substances analyzed are metals (cadmium, mercury and lead), dioxins and dioxin-like PCBs, PCBs, PAHs, Cesium 134 and Cesium 137. These results are in accordance with the results prior to the 2011-2016 period.
|
All fish, mollusc and crustacean samples from the Belgian southern North Sea and the Channel appear, after analysis, to be suitable for human consumption. The substances analyzed are metals (cadmium, mercury and lead), dioxins and dioxin-like PCBs, PCBs, PAHs, Cesium 134 and Cesium 137. These results are in accordance with the results prior to the 2011-2016 period.
|
All fish, mollusc and crustacean samples from the Belgian southern North Sea and the Channel appear, after analysis, to be suitable for human consumption. The substances analyzed are metals (cadmium, mercury and lead), dioxins and dioxin-like PCBs, PCBs, PAHs, Cesium 134 and Cesium 137. These results are in accordance with the results prior to the 2011-2016 period.
|
All fish, mollusc and crustacean samples from the Belgian southern North Sea and the Channel appear, after analysis, to be suitable for human consumption. The substances analyzed are metals (cadmium, mercury and lead), dioxins and dioxin-like PCBs, PCBs, PAHs, Cesium 134 and Cesium 137. These results are in accordance with the results prior to the 2011-2016 period.
|
All fish, mollusc and crustacean samples from the Belgian southern North Sea and the Channel appear, after analysis, to be suitable for human consumption. The substances analyzed are metals (cadmium, mercury and lead), dioxins and dioxin-like PCBs, PCBs, PAHs, Cesium 134 and Cesium 137. These results are in accordance with the results prior to the 2011-2016 period.
|
All fish, mollusc and crustacean samples from the Belgian southern North Sea and the Channel appear, after analysis, to be suitable for human consumption. The substances analyzed are metals (cadmium, mercury and lead), dioxins and dioxin-like PCBs, PCBs, PAHs, Cesium 134 and Cesium 137. These results are in accordance with the results prior to the 2011-2016 period.
|
All fish, mollusc and crustacean samples from the Belgian southern North Sea and the Channel appear, after analysis, to be suitable for human consumption. The substances analyzed are metals (cadmium, mercury and lead), dioxins and dioxin-like PCBs, PCBs, PAHs, Cesium 134 and Cesium 137. These results are in accordance with the results prior to the 2011-2016 period.
|
All fish, mollusc and crustacean samples from the Belgian southern North Sea and the Channel appear, after analysis, to be suitable for human consumption. The substances analyzed are metals (cadmium, mercury and lead), dioxins and dioxin-like PCBs, PCBs, PAHs, Cesium 134 and Cesium 137. These results are in accordance with the results prior to the 2011-2016 period.
|
All fish, mollusc and crustacean samples from the Belgian southern North Sea and the Channel appear, after analysis, to be suitable for human consumption. The substances analyzed are metals (cadmium, mercury and lead), dioxins and dioxin-like PCBs, PCBs, PAHs, Cesium 134 and Cesium 137. These results are in accordance with the results prior to the 2011-2016 period.
|
All fish, mollusc and crustacean samples from the Belgian southern North Sea and the Channel appear, after analysis, to be suitable for human consumption. The substances analyzed are metals (cadmium, mercury and lead), dioxins and dioxin-like PCBs, PCBs, PAHs, Cesium 134 and Cesium 137. These results are in accordance with the results prior to the 2011-2016 period.
|
All fish, mollusc and crustacean samples from the Belgian southern North Sea and the Channel appear, after analysis, to be suitable for human consumption. The substances analyzed are metals (cadmium, mercury and lead), dioxins and dioxin-like PCBs, PCBs, PAHs, Cesium 134 and Cesium 137. These results are in accordance with the results prior to the 2011-2016 period.
|
All fish, mollusc and crustacean samples from the Belgian southern North Sea and the Channel appear, after analysis, to be suitable for human consumption. The substances analyzed are metals (cadmium, mercury and lead), dioxins and dioxin-like PCBs, PCBs, PAHs, Cesium 134 and Cesium 137. These results are in accordance with the results prior to the 2011-2016 period.
|
All fish, mollusc and crustacean samples from the Belgian southern North Sea and the Channel appear, after analysis, to be suitable for human consumption. The substances analyzed are metals (cadmium, mercury and lead), dioxins and dioxin-like PCBs, PCBs, PAHs, Cesium 134 and Cesium 137. These results are in accordance with the results prior to the 2011-2016 period.
|
All fish, mollusc and crustacean samples from the Belgian southern North Sea and the Channel appear, after analysis, to be suitable for human consumption. The substances analyzed are metals (cadmium, mercury and lead), dioxins and dioxin-like PCBs, PCBs, PAHs, Cesium 134 and Cesium 137. These results are in accordance with the results prior to the 2011-2016 period.
|
Assessments period |
2011-2016 |
2011-2016 |
2011-2016 |
2011-2016 |
2011-2016 |
2011-2016 |
2011-2016 |
2011-2016 |
2011-2016 |
2011-2016 |
2011-2016 |
2011-2016 |
2011-2016 |
2011-2016 |
2011-2016 |
2011-2016 |
2011-2016 |
2011-2016 |
2011-2016 |
2011-2016 |
2011-2016 |
2011-2016 |
2011-2016 |
2011-2016 |
2011-2016 |
2011-2016 |
2011-2016 |
2011-2016 |
2011-2016 |
2011-2016 |
2011-2016 |
2011-2016 |
2011-2016 |
2011-2016 |
2011-2016 |
2011-2016 |
2011-2016 |
2011-2016 |
2011-2016 |
2011-2016 |
2011-2016 |
Related pressures |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Related targets |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
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