Member State report / Art8 / 2018 / D8 / 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 D8 Contaminants
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

Belgian Part of the North Sea (ANS-BE-MS-1)

GES component
D8
D8
D8
D8
D8
D8
Feature
Marine species
Marine species
Marine species
Marine species
Acute pollution events
Acute pollution events
Element
Gastropoda
Limanda limanda
Limanda limanda
Uria aalge
Element code
101
127139
127139
137133
Element 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/
Element 2
Element 2 code
Element 2 code source
Element source
National
National
National
National
Criterion
D8C2
D8C2
D8C2
D8C2
D8C3
D8C4
Parameter
Other
Other
Other
Incidence
Duration
Other
Parameter other
Imposex-gebaseerd op meting van TBT in biota
Activity of 7-ethoxyresorufine O-deethylase (EROD) in liver
Fish Disease Index (FDI)
Adverse effects
Threshold value upper
147.0
20.0
Threshold value lower
Threshold qualitative
Downward trend
Downward trend
Threshold value source
OSPAR Convention
Other (specify)
Threshold value source other
National
Value achieved upper
57.59
0.42
100.0
27.0
Value achieved lower
0.37
3.0
Value unit
Other
Other
percentage
Other
Value unit other
pmol/min/mg protein
FDI
D/y
Proportion threshold value
Proportion value achieved
3000.0
Proportion threshold value unit
% of samples achieving threshold value
% of samples achieving threshold value
extent in km2 of pressure
Trend
Improving
Unknown
Unknown
Improving
Unknown
Unknown
Parameter achieved
Yes
Yes
Unknown
No
Not assessed
Unknown
Description parameter
Due to the low abundance of gastropods, in particular the purple snail, imposex could not be established in the Belgian part of the North Sea and the follow-up is based on concentrations of TBT in mussels. At concentrations lower than the EAC no clear negative effects are expected.
No EAC available, BAC value 178 for female and 147 for male fish.
EAC for FDI (Fish Disease Index) are in development, based on the presence or absence of 9 disorders (skin diseases and parasites). Low FDI-values indicate healthy fish. The difference in FDI-values for coast (0.37 ± 0.82) and offshore (0.42 ± 0.98) is low.
Based on observations, GES is reached in 2 of 6 years, but due to the low number of beached individuals (only 1 in winter 2016-2017), results are of low confidence. If only results on more than 25 individuals are kept (cfr. OSPAR protocol), one result remains: 3%. Based on GLM, GES is reached starting from 2014.
Monitoring of harmful effects: PAHs in sediments and biota and macro ecological characteristics of the seabed, impact on seabirds
Related indicator
Criteria status
Good
Unknown
Unknown
Not good
Unknown
Good
Description criteria
No clear negative effects are expected due to the occurrence of imposex in marine snails based on TBT concentrations in mussels.
The results of the monitoring following the Flinterstar incident showed no impact of oil pollution on marine sediments, organisms or soil fauna. The impact on seabirds was probably limited to just over 300 slightly polluted individuals (mostly gulls).
Element status
Good
Unknown
Unknown
Not good
Description element
Integration rule type parameter
OOAO
OOAO
OOAO
OOAO
OOAO
OOAO
Integration rule description parameter
Various variables
Various variables
Various variables
Various variables
Various variables
Various variables
Integration rule type criteria
Not relevant
Not relevant
Not relevant
Not relevant
Not relevant
Not relevant
Integration rule description criteria
GES extent threshold
GES extent achieved
GES extent unit
Not relevant
Not relevant
Not relevant
Not relevant
Not relevant
Not relevant
GES achieved
Not relevant
Not relevant
Not relevant
Not relevant
Not relevant
Not relevant
Description overall status
Long-term monitoring (1961-2017) shows that the oil pollution degree in guillemots shows a sharply falling trend. In the early years of the monitoring, almost all guillemots found were contaminated with oil, in recent years less than 50% of the animals found were contaminated. Due to the small number of stranded guillemots, the OSPAR protocol can no longer be strictly followed. The higher values obtained in recent years are based on relatively few individuals. However, the environmental quality standard has not yet been achieved. - The fish disease indicator (FDI) gives a good reflection of general stress within the ecosystem under increasing pressure, but assessment criteria are still being developed. Most of the observed anomalies are related to parasitic infections, and the skin disorders are the most remarkable in terms of skin disorders. Skin disorders and parasitic infections were more commonly observed during the last years. Since no trend analysis can yet be done, we cannot make a statement about an improvement or deterioration in the health of the common dab population. - The EROD activity level in dab of the BPNS is lower than the background value established by OSPAR. It is therefore very unlikely that these fish are exposed to contaminant concentrations that pose a toxicological threat. - Due to the low abundance of gastropods, in particular the purple snail, imposex could not be established in the Belgian part of the North Sea and the follow-up is based on concentrations in mussels. Decreasing concentrations were observed after the ban on tributyltin in antifouling paints, which results in concentrations lower than the norm for tributyltin in biota. As a result, one can expect that these concentrations do not give rise to a too high level of imposex in the Belgian part of the North Sea.
Long-term monitoring (1961-2017) shows that the oil pollution degree in guillemots shows a sharply falling trend. In the early years of the monitoring, almost all guillemots found were contaminated with oil, in recent years less than 50% of the animals found were contaminated. Due to the small number of stranded guillemots, the OSPAR protocol can no longer be strictly followed. The higher values obtained in recent years are based on relatively few individuals. However, the environmental quality standard has not yet been achieved. - The fish disease indicator (FDI) gives a good reflection of general stress within the ecosystem under increasing pressure, but assessment criteria are still being developed. Most of the observed anomalies are related to parasitic infections, and the skin disorders are the most remarkable in terms of skin disorders. Skin disorders and parasitic infections were more commonly observed during the last years. Since no trend analysis can yet be done, we cannot make a statement about an improvement or deterioration in the health of the common dab population. - The EROD activity level in dab of the BPNS is lower than the background value established by OSPAR. It is therefore very unlikely that these fish are exposed to contaminant concentrations that pose a toxicological threat. - Due to the low abundance of gastropods, in particular the purple snail, imposex could not be established in the Belgian part of the North Sea and the follow-up is based on concentrations in mussels. Decreasing concentrations were observed after the ban on tributyltin in antifouling paints, which results in concentrations lower than the norm for tributyltin in biota. As a result, one can expect that these concentrations do not give rise to a too high level of imposex in the Belgian part of the North Sea.
Long-term monitoring (1961-2017) shows that the oil pollution degree in guillemots shows a sharply falling trend. In the early years of the monitoring, almost all guillemots found were contaminated with oil, in recent years less than 50% of the animals found were contaminated. Due to the small number of stranded guillemots, the OSPAR protocol can no longer be strictly followed. The higher values obtained in recent years are based on relatively few individuals. However, the environmental quality standard has not yet been achieved. - The fish disease indicator (FDI) gives a good reflection of general stress within the ecosystem under increasing pressure, but assessment criteria are still being developed. Most of the observed anomalies are related to parasitic infections, and the skin disorders are the most remarkable in terms of skin disorders. Skin disorders and parasitic infections were more commonly observed during the last years. Since no trend analysis can yet be done, we cannot make a statement about an improvement or deterioration in the health of the common dab population. - The EROD activity level in dab of the BPNS is lower than the background value established by OSPAR. It is therefore very unlikely that these fish are exposed to contaminant concentrations that pose a toxicological threat. - Due to the low abundance of gastropods, in particular the purple snail, imposex could not be established in the Belgian part of the North Sea and the follow-up is based on concentrations in mussels. Decreasing concentrations were observed after the ban on tributyltin in antifouling paints, which results in concentrations lower than the norm for tributyltin in biota. As a result, one can expect that these concentrations do not give rise to a too high level of imposex in the Belgian part of the North Sea.
Long-term monitoring (1961-2017) shows that the oil pollution degree in guillemots shows a sharply falling trend. In the early years of the monitoring, almost all guillemots found were contaminated with oil, in recent years less than 50% of the animals found were contaminated. Due to the small number of stranded guillemots, the OSPAR protocol can no longer be strictly followed. The higher values obtained in recent years are based on relatively few individuals. However, the environmental quality standard has not yet been achieved. - The fish disease indicator (FDI) gives a good reflection of general stress within the ecosystem under increasing pressure, but assessment criteria are still being developed. Most of the observed anomalies are related to parasitic infections, and the skin disorders are the most remarkable in terms of skin disorders. Skin disorders and parasitic infections were more commonly observed during the last years. Since no trend analysis can yet be done, we cannot make a statement about an improvement or deterioration in the health of the common dab population. - The EROD activity level in dab of the BPNS is lower than the background value established by OSPAR. It is therefore very unlikely that these fish are exposed to contaminant concentrations that pose a toxicological threat. - Due to the low abundance of gastropods, in particular the purple snail, imposex could not be established in the Belgian part of the North Sea and the follow-up is based on concentrations in mussels. Decreasing concentrations were observed after the ban on tributyltin in antifouling paints, which results in concentrations lower than the norm for tributyltin in biota. As a result, one can expect that these concentrations do not give rise to a too high level of imposex in the Belgian part of the North Sea.
In 2011-2016, Belgium was hit by a significant acute oil pollution caused by the Flinterstar incident (2015). During the 27-day crisis phase, 190 m3 of oil was released into the marine environment, 55 m3 of which was cleared. The impacted zone of roughly 3000 km2 covered the northern French, Belgian and southern Dutch territorial sea and a part of the Belgian EEZ. The results of the monitoring following the Flinterstar incident showed no impact of oil pollution on marine sediments, organisms or soil fauna. The impact on seabirds remained limited. For illegal oil spills, the declining trend from the past continues, these spills have become very rare (min 2 - max 12 slicks per year during this period). A similar trend cannot be observed for illegal discharges of other harmful liquids, but checking for illegality is not always possible for this type of stain during operations.
In 2011-2016, Belgium was hit by a significant acute oil pollution caused by the Flinterstar incident (2015). During the 27-day crisis phase, 190 m3 of oil was released into the marine environment, 55 m3 of which was cleared. The impacted zone of roughly 3000 km2 covered the northern French, Belgian and southern Dutch territorial sea and a part of the Belgian EEZ. The results of the monitoring following the Flinterstar incident showed no impact of oil pollution on marine sediments, organisms or soil fauna. The impact on seabirds remained limited. For illegal oil spills, the declining trend from the past continues, these spills have become very rare (min 2 - max 12 slicks per year during this period). A similar trend cannot be observed for illegal discharges of other harmful liquids, but checking for illegality is not always possible for this type of stain during operations.
Assessments period
2011-2016
2011-2016
2011-2016
2011-2016
2011-2016
2011-2016
Related pressures
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
Related targets
  • D8.T4
  • D8.T5
  • Target 38
  • Target 40
  • D8.T4
  • D8.T5
  • Target 38
  • Target 40
  • D8.T4
  • D8.T5
  • Target 38
  • Target 40
  • D8.T4
  • D8.T5
  • Target 38
  • Target 40
  • D8.T6
  • D8.T7
  • D8.T8
  • Target 41
  • Target 42
  • D8.T6
  • D8.T7
  • D8.T8
  • Target 41
  • Target 42

Belgische offshore wateren (vanaf 12 zeemijl)/eaux belges offshore (au-del? de 12 milles nautiques) (ANS-BE-OFFSHORE)

GES component
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
Feature
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - UPBT substances
Contaminants - UPBT substances
Contaminants - UPBT substances
Contaminants - UPBT substances
Contaminants - UPBT substances
Contaminants - UPBT substances
Contaminants - UPBT substances
Contaminants - UPBT substances
Contaminants - UPBT substances
Contaminants - UPBT substances
Contaminants - UPBT substances
Contaminants - UPBT substances
Contaminants - UPBT substances
Contaminants - UPBT substances
Element
2,2,3,4,4,5,5-heptachlorobiphenyl
2,2,3,4,4,5,5-heptachlorobiphenyl
2,2,3,4,4,5-hexachlorobiphenyl
2,2,3,4,4,5-hexachlorobiphenyl
2,2,4,4,5,5-hexachlorobiphenyl
2,2,4,4,5,5-hexachlorobiphenyl
2,2,4,5,5-pentachlorobiphenyl
2,2,4,5,5-pentachlorobiphenyl
2,2,5,5-tetrachlorobiphenyl
2,2,5,5-tetrachlorobiphenyl
2,4,4-trichlorobiphenyl
2,4,4-trichlorobiphenyl
Anthracene
Arsenic
Benzo(a)anthracene
Cadmium
Cadmium
Chromium
Chrysene
Copper
Fluoranthene
Hexachlorobenzene
Hexachlorobutadiene
Lead
Lead
Nickel
Phenanthrene
Pyrene
Zinc
2,2,4,4,5,5-hexabromodiphenyl ether
2,2,4,4,5,6-hexabromodiphenyl ether
2,2,4,4,5-pentabromodiphenyl ether
2,2,4,4,6-pentabromodiphenyl ether
2,2,4,4-tetrabromodiphenyl ether
2,3,4,4,5-pentachlorobiphenyl
2,3,4,4,5-pentachlorobiphenyl
2,4,4-tribromodiphenyl ether
Benzo(a)pyrene
Benzo(ghi)perylene
Indeno(1,2,3-cd)pyrene
Mercury
Mercury
Tributyltin compounds
Element code
CAS_35065-29-3
CAS_35065-29-3
CAS_35065-28-2
CAS_35065-28-2
CAS_35065-27-1
CAS_35065-27-1
CAS_37680-73-2
CAS_37680-73-2
CAS_35693-99-3
CAS_35693-99-3
CAS_7012-37-5
CAS_7012-37-5
CAS_120-12-7
CAS_7440-38-2
CAS_56-55-3
CAS_7440-43-9
CAS_7440-43-9
CAS_7440-47-3
CAS_218-01-9
CAS_7440-50-8
CAS_206-44-0
CAS_118-74-1
CAS_87-68-3
CAS_7439-92-1
CAS_7439-92-1
CAS_7440-02-0
CAS_85-01-8
CAS_129-00-0
CAS_7440-66-6
CAS_68631-49-2
CAS_207122-15-4
CAS_60348-60-9
CAS_189084-64-8
CAS_5436-43-1
CAS_31508-00-6
CAS_31508-00-6
CAS_41318-75-6
CAS_50-32-8
CAS_191-24-2
CAS_193-39-5
CAS_7439-97-6
CAS_7439-97-6
TBTIN
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
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
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
ICES
Element 2
Element 2 code
Element 2 code source
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
EU
EU
Criterion
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
Parameter
CONC-S-63
Other
CONC-S-63
Other
CONC-S-63
Other
CONC-S-63
Other
CONC-S-63
Other
CONC-S-63
Other
CONC-S-63
CONC-S-63
CONC-S-63
CONC-S-63
Other
CONC-S-63
CONC-S-63
CONC-S-63
CONC-S-63
Other
Other
CONC-S-63
Other
CONC-S-63
CONC-S-63
CONC-S-63
CONC-S-63
CONC-S-63
CONC-S-63
CONC-S-63
CONC-S-63
CONC-S-63
CONC-S-63
Other
CONC-S-63
CONC-S-63
CONC-S-63
CONC-S-63
CONC-S-63
Other
CONC-S-63
Parameter other
Concentration in liver of Platichthys flesus
Concentration in liver of Platichthys flesus
Concentration in liver of Platichthys flesus
Concentration in liver of Platichthys flesus
Concentration in liver of Platichthys flesus
Concentration in liver of Platichthys flesus
Concentration in Platichthys flesus
Concentration in muscles of Platichthys flesus
Concentration in muscles of Platichthys flesus
Concentration in Platichthys flesus
Concentration in liver of Platichthys flesus
Concentration in Platichthys flesus
Threshold value upper
12.0
60.97
7.9
41.21
40.0
206.05
3.0
15.73
2.7
14.04
1.7
8.71
85.0
261.0
1.2
1000.0
81.0
384.0
34.0
600.0
10.0
55.0
47.0
1500.0
240.0
665.0
150.0
0.6
3.25
430.0
85.0
240.0
0.15
20.0
Threshold value lower
Threshold qualitative
Downward trend
Downward trend
Downward trend
Downward trend
Downward trend
Downward trend
Downward trend
Downward trend
Downward trend
Threshold value source
OSPAR Convention
OSPAR Convention
OSPAR Convention
OSPAR Convention
OSPAR Convention
OSPAR Convention
OSPAR Convention
OSPAR Convention
OSPAR Convention
OSPAR Convention
OSPAR Convention
OSPAR Convention
OSPAR Convention
OSPAR Convention
OSPAR Convention
OSPAR Convention
OSPAR Convention
OSPAR Convention
OSPAR Convention
OSPAR Convention
OSPAR Convention
OSPAR Convention
OSPAR Convention
OSPAR Convention
OSPAR Convention
OSPAR Convention
OSPAR Convention
OSPAR Convention
OSPAR Convention
OSPAR Convention
OSPAR Convention
OSPAR Convention
OSPAR Convention
OSPAR Convention
Threshold value source other
Value achieved upper
0.42
16.75
1.17
29.38
1.24
33.8
0.54
9.73
0.2
7.78
0.29
1.3
21.3
132.9
43.3
0.5
127.25
312.9
63.4
102.6
106.7
0.06
0.2
1159.8
29.24
166.4
217.9
130.3
483.8
0.17
0.17
13.83
0.17
0.98
0.95
8.48
0.17
46.8
56.5
54.6
0.26
73.7
5.21
Value achieved lower
8.8
18.1
27.5
0.24
190.8
38.7
51.0
54.5
149.3
86.0
58.6
53.0
139.4
27.6
38.9
39.3
0.14
0.57
Value unit
microgram per kilogram of dry weight
microgram per kilogram of wet weight
microgram per kilogram of dry weight
microgram per kilogram of wet weight
microgram per kilogram of dry weight
microgram per kilogram of wet weight
microgram per kilogram of dry weight
microgram per kilogram of wet weight
microgram per kilogram of dry weight
microgram per kilogram of wet weight
microgram per kilogram of dry weight
microgram per kilogram of wet weight
microgram per kilogram of dry weight
microgram per kilogram of dry weight
microgram per kilogram of dry weight
microgram per kilogram of dry weight
microgram per kilogram of wet weight
microgram per kilogram of dry weight
microgram per kilogram of dry weight
microgram per kilogram of dry weight
microgram per kilogram of dry weight
microgram per kilogram of wet weight
microgram per kilogram of wet weight
microgram per kilogram of dry weight
microgram per kilogram of wet weight
microgram per kilogram of dry weight
microgram per kilogram of dry weight
microgram per kilogram of dry weight
microgram per kilogram of dry weight
microgram per kilogram of dry weight
microgram per kilogram of dry weight
microgram per kilogram of dry weight
microgram per kilogram of dry weight
microgram per kilogram of dry weight
microgram per kilogram of dry weight
microgram per kilogram of wet weight
microgram per kilogram of dry weight
microgram per kilogram of dry weight
microgram per kilogram of dry weight
microgram per kilogram of dry weight
microgram per kilogram of dry weight
microgram per kilogram of wet weight
microgram per kilogram of dry weight
Value unit other
Proportion threshold value
Proportion value achieved
Proportion threshold value unit
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
Trend
Unknown
Improving
Unknown
Improving
Unknown
Improving
Unknown
Improving
Unknown
Improving
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Stable
Unknown
Unknown
Unknown
Unknown
Improving
Unknown
Unknown
Stable
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Improving
Unknown
Unknown
Unknown
Unknown
Unknown
Stable
Unknown
Parameter achieved
Yes
Yes
Yes
Yes
Yes
Yes
Yes
Yes
Yes
Yes
Yes
Yes
Yes
Unknown
Yes
Yes
Yes
No
Yes
No
Yes
Yes
Yes
No
Yes
Unknown
Yes
Yes
No
Unknown
Unknown
Unknown
Unknown
Unknown
No
No
Unknown
Yes
Yes
Yes
No
No
Unknown
Description parameter
W07, -63um fraction after wet screening, concentrations normalized 2.5% TOC, in accordance with OSPAR methodology (95% confidence interval on modeled concentration)
Sampling of bone over an area representative of the Belgian part of the North Sea. Value of OSPAR assessment (95% confidence interval on modeled concentration for 2016).
W07, concentrations normalized 2.5% TOC, in accordance with OSPAR methodology (95% confidence interval on modeled concentration).
Sampling of bone over an area representative of the Belgian part of the North Sea. Value of OSPAR assessment (95% confidence interval on modeled concentration for 2016).
W07, concentrations normalized 2.5% TOC, in accordance with OSPAR methodology (95% confidence interval on modeled concentration).
Sampling of bone over an area representative of the Belgian part of the North Sea. Value of OSPAR assessment (95% confidence interval on modeled concentration for 2016).
W07, concentrations normalized 2.5% TOC, in accordance with OSPAR methodology (95% confidence interval on modeled concentration).
Sampling of bone over an area representative of the Belgian part of the North Sea. Value of OSPAR assessment (95% confidence interval on modeled concentration for 2016).
W07, concentrations normalized 2.5% TOC, in accordance with OSPAR methodology (95% confidence interval on modeled concentration).
Sampling of bone over an area representative of the Belgian part of the North Sea. Value of OSPAR assessment (95% confidence interval on modeled concentration for 2016).
W07, concentrations normalized 2.5% TOC, in accordance with OSPAR methodology (95% confidence interval on modeled concentration).
Sampling of bone over an area representative of the Belgian part of the North Sea. Value of OSPAR assessment (95% confidence interval on modeled concentration for 2016).
W07-10, concentrations normalized 2.5% TOC, in accordance with OSPAR methodology (95% confidence interval on modeled concentration)
In accordance with OSPAR methodology. No ERL.
W07-10, concentrations normalized 2.5% TOC, in accordance with OSPAR methodology (95% confidence interval on modeled concentration)
According to OSPAR methodology.
OSPAR (2017). No significant trend.
According to OSPAR methodology.
W07-10, concentrations normalized 2.5% TOC, in accordance with OSPAR methodology (95% confidence interval on modeled concentration)
According to OSPAR methodology.
W07-10, concentrations normalized 2.5% TOC, in accordance with OSPAR methodology (95% confidence interval on modeled concentration)
OSPAR assessments, 3 sampling locations (Nieuwpoort, Oostende, Knokke), values below detection limit
OSPAR assessments, 3 sampling locations (Nieuwpoort, Oostende, Knokke), values below detection limit
According to OSPAR methodology.
OSPAR (2017). No significant trend.
In accordance with OSPAR methodology. No ERL.
W07-10, concentrations normalized 2.5% TOC, in accordance with OSPAR methodology (95% confidence interval on modeled concentration)
W07-10, concentrations normalized 2.5% TOC, in accordance with OSPAR methodology (95% confidence interval on modeled concentration)
According to OSPAR methodology.
maximum value for the period 2013-2015, values often lower then detection limit, W07-10, no EAC
maximum value for the period 2013-2015, values often lower then detection limit, W07-10, no EAC
maximum value for the period 2013-2015, values often lower then detection limit, W07-10, no EAC
maximum value for the period 2013-2015, values often lower then detection limit, W07-10, no EAC
maximum value for the period 2013-2015, values often lower then detection limit, W07-10, no EAC
W07, concentrations normalized 2.5% TOC, in accordance with OSPAR methodology (95% confidence interval on modeled concentration).
Sampling of bone over an area representative of the Belgian part of the North Sea. Value of OSPAR assessment (95% confidence interval on modeled concentration for 2016).
maximum value for the period 2013-2015, values often lower then detection limit, W07-10, no EAC
W07-10, concentrations normalized 2.5% TOC, in accordance with OSPAR methodology (95% confidence interval on modeled concentration)
W07-10, concentrations normalized 2.5% TOC, in accordance with OSPAR methodology (95% confidence interval on modeled concentration)
W07-10, concentrations normalized 2.5% TOC, in accordance with OSPAR methodology (95% confidence interval on modeled concentration)
According to OSPAR methodology.
Average value. No significant trend (OSPAR, 2017).
Most values are lower than the determination limit, so that the trend could not be assessed. W07-10, normalized 2.5% TOC.
Related indicator
Criteria status
Good
Good
Good
Good
Good
Good
Good
Good
Good
Good
Good
Good
Good
Unknown
Good
Good
Good
Not good
Good
Not good
Good
Good
Good
Not good
Not good
Unknown
Good
Good
Not good
Unknown
Unknown
Unknown
Unknown
Unknown
Not good
Not good
Unknown
Good
Good
Good
Not good
Not good
Unknown
Description criteria
Element status
Good
Good
Good
Good
Good
Good
Good
Good
Good
Good
Good
Good
Good
Good
Good
Good
Good
Not good
Good
Not good
Good
Good
Good
Not good
Not good
Unknown
Good
Good
Not good
Unknown
Unknown
Unknown
Unknown
Unknown
Not good
Not good
Unknown
Good
Good
Good
Not good
Not good
Unknown
Description element
Most values are below detection limit of 0.06µg/kg
Most values are below detection limit of 0.06µg/kg
Most values are below detection limit of 0.06µg/kg
Most values are below detection limit of 0.06µg/kg
Most values are below detection limit of 0.06µg/kg
Most values are below detection limit of 0.06µg/kg
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
Integration rule description parameter
Assessment in sediment and biota
Assessment in sediment and biota
Assessment in sediment and biota
Assessment in sediment and biota
Assessment in sediment and biota
Assessment in sediment and biota
Assessment in sediment and biota
Assessment in sediment and biota
Assessment in sediment and biota
Assessment in sediment and biota
Assessment in sediment and biota
Assessment in sediment and biota
Assessment in sediment and biota
Assessment in sediment and biota
Assessment in sediment and biota
Assessment in sediment and biota
Assessment in sediment and biota
Assessment in sediment and biota
Assessment in sediment and biota
Assessment in sediment and biota
Assessment in sediment and biota
Assessment in sediment and biota
Assessment in sediment and biota
Assessment in sediment and biota
Assessment in sediment and biota
Assessment in sediment and biota
Assessment in sediment and biota
Assessment in sediment and biota
Assessment in sediment and biota
Assessment in sediment and biota
Assessment in sediment and biota
Assessment in sediment and biota
Assessment in sediment and biota
Assessment in sediment and biota
Assessment in sediment and biota
Assessment in sediment and biota
Assessment in sediment and biota
Assessment in sediment and biota
Assessment in sediment and biota
Assessment in sediment and biota
Assessment in sediment and biota
Assessment in sediment and biota
Assessment in sediment and biota
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
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
GES extent achieved
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
GES achieved
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
Description overall status
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
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
2011-2016
2011-2016
Related pressures
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
Related targets
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38

BELGISCHE KUSTZONE (BEFED_CW)

GES component
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
Feature
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - UPBT substances
Contaminants - UPBT substances
Contaminants - UPBT substances
Contaminants - UPBT substances
Contaminants - UPBT substances
Contaminants - UPBT substances
Contaminants - UPBT substances
Contaminants - UPBT substances
Contaminants - UPBT substances
Contaminants - UPBT substances
Contaminants - UPBT substances
Contaminants - UPBT substances
Contaminants - UPBT substances
Contaminants - UPBT substances
Contaminants - UPBT substances
Contaminants - UPBT substances
Contaminants - UPBT substances
Contaminants - UPBT substances
Contaminants - UPBT substances
Contaminants - UPBT substances
Contaminants - UPBT substances
Contaminants - UPBT substances
Contaminants - UPBT substances
Contaminants - UPBT substances
Contaminants - UPBT substances
Contaminants - UPBT substances
Contaminants - UPBT substances
Contaminants - UPBT substances
Contaminants - UPBT substances
Contaminants - UPBT substances
Element
2,2,3,4,4,5,5-heptachlorobiphenyl
2,2,3,4,4,5,5-heptachlorobiphenyl
2,2,3,4,4,5,5-heptachlorobiphenyl
2,2,3,4,4,5-hexachlorobiphenyl
2,2,3,4,4,5-hexachlorobiphenyl
2,2,3,4,4,5-hexachlorobiphenyl
2,2,4,4,5,5-hexachlorobiphenyl
2,2,4,4,5,5-hexachlorobiphenyl
2,2,4,4,5,5-hexachlorobiphenyl
2,2,4,5,5-pentachlorobiphenyl
2,2,4,5,5-pentachlorobiphenyl
2,2,4,5,5-pentachlorobiphenyl
2,2,5,5-tetrachlorobiphenyl
2,2,5,5-tetrachlorobiphenyl
2,2,5,5-tetrachlorobiphenyl
2,4,4-trichlorobiphenyl
2,4,4-trichlorobiphenyl
2,4,4-trichlorobiphenyl
Anthracene
Anthracene
Anthracene
Arsenic
Benzo(a)anthracene
Benzo(a)anthracene
Biphenyl
Cadmium
Cadmium
Cadmium
Chromium
Chrysene
Chrysene
Copper
Fluoranthene
Fluoranthene
Fluoranthene
Hexachlorobenzene
Hexachlorobenzene
Hexachlorobenzene
Hexachlorocyclohexane
Lead
Lead
Lead
Nickel
Phenanthrene
Phenanthrene
Pyrene
Pyrene
Zinc
hexachlorobutadiene
hexachlorobutadiene
sum of p,p'-DDT (dichlorodiphenyltrichloroethane) and the metabolites p,p'-DDD (dichlorodiphenyldichloroethane) and p,p'-DDE (dichlorodiphenyldichloroethylene)
2,2,4,4,5,5-hexabromodiphenyl ether
2,2,4,4,5,5-hexabromodiphenyl ether
2,2,4,4,5,6-hexabromodiphenyl ether
2,2,4,4,5,6-hexabromodiphenyl ether
2,2,4,4,5-pentabromodiphenyl ether
2,2,4,4,5-pentabromodiphenyl ether
2,2,4,4,6-pentabromodiphenyl ether
2,2,4,4,6-pentabromodiphenyl ether
2,2,4,4-tetrabromodiphenyl ether
2,2,4,4-tetrabromodiphenyl ether
2,3,4,4,5-pentachlorobiphenyl
2,3,4,4,5-pentachlorobiphenyl
2,3,4,4,5-pentachlorobiphenyl
2,4,4-tribromodiphenyl ether
2,4,4-tribromodiphenyl ether
Benzo(a)pyrene
Benzo(a)pyrene
Benzo(ghi)perylene
Benzo(ghi)perylene
Brominated diphenylethers (congener numbers 28, 47, 99, 100, 153 and 154)
Indeno(1,2,3-cd)pyrene
Indeno(1,2,3-cd)pyrene
Mercury
Mercury
Mercury
Mercury
Total PAHs (Benzo(a)pyrene, Benzo(b)fluoranthene, Benzo(k)fluoranthene, Benzo(ghi)perylene, Indeno(1,2,3-cd)pyrene)
Tributyltin compounds
Tributyltin compounds
Tributyltin compounds
Element code
CAS_35065-29-3
CAS_35065-29-3
CAS_35065-29-3
CAS_35065-28-2
CAS_35065-28-2
CAS_35065-28-2
CAS_35065-27-1
CAS_35065-27-1
CAS_35065-27-1
CAS_37680-73-2
CAS_37680-73-2
CAS_37680-73-2
CAS_35693-99-3
CAS_35693-99-3
CAS_35693-99-3
CAS_7012-37-5
CAS_7012-37-5
CAS_7012-37-5
CAS_120-12-7
CAS_120-12-7
CAS_120-12-7
CAS_7440-38-2
CAS_56-55-3
CAS_56-55-3
BIPN
CAS_7440-43-9
CAS_7440-43-9
CAS_7440-43-9
CAS_7440-47-3
CAS_218-01-9
CAS_218-01-9
CAS_7440-50-8
CAS_206-44-0
CAS_206-44-0
CAS_206-44-0
CAS_118-74-1
CAS_118-74-1
CAS_118-74-1
CAS_608-73-1
CAS_7439-92-1
CAS_7439-92-1
CAS_7439-92-1
CAS_7440-02-0
CAS_85-01-8
CAS_85-01-8
CAS_129-00-0
CAS_129-00-0
CAS_7440-66-6
CAS_87-68-3
CAS_87-68-3
SDDTP
CAS_68631-49-2
CAS_68631-49-2
CAS_207122-15-4
CAS_207122-15-4
CAS_60348-60-9
CAS_60348-60-9
CAS_189084-64-8
CAS_189084-64-8
CAS_5436-43-1
CAS_5436-43-1
CAS_31508-00-6
CAS_31508-00-6
CAS_31508-00-6
CAS_41318-75-6
CAS_41318-75-6
CAS_50-32-8
CAS_50-32-8
CAS_191-24-2
CAS_191-24-2
EEA_32-04-2
CAS_193-39-5
CAS_193-39-5
CAS_7439-97-6
CAS_7439-97-6
CAS_7439-97-6
CAS_7439-97-6
EEA_33-56-7
TBTIN
TBTIN
TBTIN
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
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
ICES
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
ICES
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
ICES
ICES
ICES
Element 2
Element 2 code
Element 2 code source
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
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
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
Parameter
CONC-S-63
Other
Other
CONC-S-63
Other
Other
CONC-S-63
Other
Other
CONC-S-63
Other
Other
CONC-S-63
Other
Other
CONC-S-63
Other
Other
CONC-S-63
Concentration in water
Other
CONC-S-63
CONC-S-63
Other
Other
CONC-S-63
Other
Other
CONC-S-63
CONC-S-63
Other
CONC-S-63
CONC-S-63
Concentration in water
Other
Other
Other
Other
Other
CONC-S-63
Other
Other
CONC-S-63
CONC-S-63
Other
CONC-S-63
Other
CONC-S-63
Other
Other
Other
CONC-S-63
Other
CONC-S-63
Other
CONC-S-63
Other
CONC-S-63
Other
CONC-S-63
Other
CONC-S-63
Other
Other
CONC-S-63
Other
CONC-S-63
Other
CONC-S-63
Other
Concentration in water
CONC-S-63
Other
CONC-S-63
Other
Other
Other
Concentration in water
CONC-S-63
Concentration in water
Other
Parameter other
Concentration in liver of Platichthys flesus
Concentration in Mytilus edulis
Concentration in liver of Platichthys flesus
Concentration in Mytilus edulis
Concentration in liver of Platichthys flesus
Concentration in Mytilus edulis
Concentration in liver of Platichthys flesus
Concentration in Mytilus edulis
Concentration in liver of Platichthys flesus
Concentration in Mytilus edulis
Concentration in liver of Platichthys flesus
Concentration in Mytilus edulis
Concentration in Mytilus edulis
Concentration in Mytilus edulis
Concentration in eggs of Sterna hirundo
Concentration in Mytilus edulis
Concentration in Platichthys flesus
Concentration in Mytilus edulis
Concentration in Mytilus edulis
Concentration in eggs of Sterna hirundo
Concentration in muscles of Platichthys flesus
Concentration in Mytilus edulis
Concentration in eggs of Sterna hirundo
Concentration in Mytilus edulis
Concentration in Platichthys flesus
Concentration in Mytilus edulis
Concentration in Mytilus edulis
Concentration in muscles of Platichthys flesus
Concentration in Mytilus edulis
Concentration in eggs of Sterna hirundo
Concentration in Mytilus edulis
Concentration in Mytilus edulis
Concentration in Mytilus edulis
Concentration in Mytilus edulis
Concentration in Mytilus edulis
Concentration in liver of Platichthys flesus
Concentration in Mytilus edulis
Concentration in Mytilus edulis
Concentration in Mytilus edulis
Concentration in Mytilus edulis
Concentration in Mytilus edulis
Concentration in eggs of Sterna hirundo
Concentration in Mytilus edulis
Concentration in Platichthys flesus
Concentration in Mytilus edulis
Threshold value upper
12.0
60.97
6.097
7.9
41.21
4.121
40.0
206.05
20.605
3.0
15.73
1.573
2.7
14.04
1.404
1.7
8.71
0.871
85.0
0.1
49.3
25.0
261.0
13.6
20.0
1.2
1000.0
1000.0
81.0
384.0
34.0
600.0
0.12
18.7
2.0
10.0
10.0
2.0
47.0
1500.0
1500.0
240.0
289.0
665.0
17.0
150.0
55.0
55.0
10.0
0.6
3.25
0.325
430.0
102.0
85.0
18.7
0.014
240.0
0.15
160.0
20.0
20.0
0.00017
0.0002
12.0
Threshold value lower
Threshold qualitative
Downward trend
Downward trend
Downward trend
Downward trend
Downward trend
Downward trend
Downward trend
Downward trend
Downward trend
Downward trend
Downward trend
Downward trend
Downward trend
Downward trend
Downward trend
Downward trend
Threshold value source
OSPAR Convention
OSPAR Convention
OSPAR Convention
OSPAR Convention
OSPAR Convention
OSPAR Convention
OSPAR Convention
OSPAR Convention
OSPAR Convention
OSPAR Convention
OSPAR Convention
OSPAR Convention
OSPAR Convention
OSPAR Convention
OSPAR Convention
OSPAR Convention
OSPAR Convention
OSPAR Convention
OSPAR Convention
Priority substances Directive (2013/39/EU)
OSPAR Convention
OSPAR Convention
OSPAR Convention
OSPAR Convention
OSPAR Convention
OSPAR Convention
OSPAR Convention
OSPAR Convention
OSPAR Convention
OSPAR Convention
OSPAR Convention
OSPAR Convention
Priority substances Directive (2013/39/EU)
OSPAR Convention
OSPAR Convention
OSPAR Convention
OSPAR Convention
OSPAR Convention
OSPAR Convention
OSPAR Convention
OSPAR Convention
OSPAR Convention
OSPAR Convention
OSPAR Convention
OSPAR Convention
OSPAR Convention
OSPAR Convention
OSPAR Convention
OSPAR Convention
OSPAR Convention
OSPAR Convention
OSPAR Convention
OSPAR Convention
OSPAR Convention
OSPAR Convention
OSPAR Convention
Priority substances Directive (2013/39/EU)
OSPAR Convention
OSPAR Convention
OSPAR Convention
OSPAR Convention
OSPAR Convention
Priority substances Directive (2013/39/EU)
Priority substances Directive (2013/39/EU)
OSPAR Convention
Threshold value source other
Value achieved upper
1.0
16.75
0.547
1.33
29.38
2.848
2.37
33.8
6.595
1.25
9.73
2.228
0.55
7.78
1.126
1.15
1.3
0.169
36.3
0.0045
0.52
8.2
64.7
2.63
766.3
1.37
362.09
127.25
135.9
87.8
2.75
39.9
217.8
0.0334
13.62
4.6
0.06
0.01
0.5
129.4
319.56
29.24
39.6
108.7
4.55
111.2
11.46
313.8
0.2
0.2
28.3
0.18
0.22
0.18
0.34
0.45
0.09
0.45
0.22
0.57
0.73
1.48
8.48
1.492
0.45
0.04
69.2
0.96
68.9
2.72
0.0131
90.6
1.7
0.37
262.7
39.6
73.7
0.0067
9.53
0.0029
8.7
Value achieved lower
0.61
0.221
1.08
2.315
1.41
4.89
0.59
1.538
0.31
0.971
0.35
0.094
27.2
0.38
6.2
45.3
1.57
0.75
150.18
123.3
63.3
2.18
18.8
165.1
7.95
0.01
46.6
207.15
35.4
79.5
4.16
81.2
7.76
186.0
0.2
0.01
0.01
0.01
0.02
0.02
0.79
1.409
0.01
48.8
0.66
48.6
2.05
57.9
1.27
0.31
25.8
0.0034
1.03
2.4
Value unit
microgram per kilogram of dry weight
microgram per kilogram of wet weight
microgram per kilogram of wet weight
microgram per kilogram of dry weight
microgram per kilogram of wet weight
microgram per kilogram of wet weight
microgram per kilogram of dry weight
microgram per kilogram of wet weight
microgram per kilogram of wet weight
microgram per kilogram of dry weight
microgram per kilogram of wet weight
microgram per kilogram of wet weight
microgram per kilogram of dry weight
microgram per kilogram of wet weight
microgram per kilogram of wet weight
microgram per kilogram of dry weight
microgram per kilogram of wet weight
microgram per kilogram of dry weight
microgram per kilogram of dry weight
microgram per litre
microgram per kilogram of wet weight
microgram per kilogram of dry weight
microgram per kilogram of dry weight
microgram per kilogram of wet weight
Other
microgram per kilogram of dry weight
microgram per kilogram of wet weight
microgram per kilogram of wet weight
microgram per kilogram of dry weight
microgram per kilogram of dry weight
microgram per kilogram of wet weight
microgram per kilogram of dry weight
microgram per kilogram of dry weight
microgram per litre
microgram per kilogram of wet weight
Other
microgram per kilogram of wet weight
microgram per kilogram of wet weight
Other
microgram per kilogram of dry weight
microgram per kilogram of wet weight
microgram per kilogram of wet weight
microgram per kilogram of dry weight
microgram per kilogram of dry weight
microgram per kilogram of wet weight
microgram per kilogram of dry weight
microgram per kilogram of wet weight
microgram per kilogram of dry weight
microgram per kilogram of wet weight
microgram per kilogram of wet weight
Other
microgram per kilogram of dry weight
microgram per kilogram of wet weight
microgram per kilogram of dry weight
microgram per kilogram of wet weight
microgram per kilogram of dry weight
microgram per kilogram of wet weight
microgram per kilogram of dry weight
microgram per kilogram of wet weight
microgram per kilogram of dry weight
microgram per kilogram of wet weight
microgram per kilogram of dry weight
microgram per kilogram of wet weight
microgram per kilogram of wet weight
microgram per kilogram of dry weight
microgram per kilogram of wet weight
microgram per kilogram of dry weight
microgram per kilogram of wet weight
microgram per kilogram of dry weight
microgram per kilogram of wet weight
microgram per litre
microgram per kilogram of dry weight
microgram per kilogram of wet weight
microgram per kilogram of dry weight
Other
microgram per kilogram of wet weight
microgram per kilogram of wet weight
microgram per litre
microgram per kilogram of dry weight
microgram per litre
microgram per kilogram of dry weight
Value unit other
ng/g
ng/g
ng/g
ng/g
ng/g
Proportion threshold value
Proportion value achieved
Proportion threshold value unit
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% of samples achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% of samples achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% of samples achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% of samples achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
Trend
Unknown
Improving
Improving
Unknown
Improving
Improving
Unknown
Improving
Improving
Unknown
Improving
Improving
Unknown
Improving
Stable
Unknown
Unknown
Unknown
Unknown
Unknown
Stable
Unknown
Unknown
Stable
Unknown
Unknown
Stable
Stable
Unknown
Unknown
Stable
Unknown
Unknown
Unknown
Stable
Unknown
Improving
Improving
Unknown
Unknown
Improving
Stable
Unknown
Unknown
Stable
Unknown
Stable
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Improving
Improving
Unknown
Unknown
Unknown
Improving
Unknown
Stable
Unknown
Unknown
Stable
Unknown
Unknown
Improving
Stable
Unknown
Unknown
Unknown
Improving
Parameter achieved
Yes
Yes
Yes
Yes
Yes
Yes
Yes
Yes
Yes
Yes
Yes
No
Yes
Yes
Yes
Yes
Yes
Yes
Yes
Yes
Yes
Yes
Yes
Yes
No
No
Yes
Yes
No
Yes
Unknown
No
Yes
Yes
Yes
No
Yes
Yes
Yes
No
Yes
Yes
Unknown
Yes
Yes
Yes
Yes
No
Yes
Yes
No
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
No
No
No
Unknown
Unknown
Yes
Yes
Yes
Yes
Yes
Yes
Unknown
No
No
No
No
No
Unknown
No
Yes
Description parameter
W01-W03, concentrations normalized 2.5% TOC, in accordance with OSPAR methodology (95% confidence interval on modeled concentration)
Sampling of bone over an area representative of the Belgian part of the North Sea. Value of OSPAR assessment (95% confidence interval on modeled concentration for 2016).
3 sampling locations (Nieuwpoort, Oostende, Knokke). Value of OSPAR assessment (95% confidence interval on modeled concentration for 2016).
W01-W03, concentrations normalized 2.5% TOC, in accordance with OSPAR methodology (95% confidence interval on modeled concentration)
Sampling of bone over an area representative of the Belgian part of the North Sea. Value of OSPAR assessment (95% confidence interval on modeled concentration for 2016).
3 sampling locations (Nieuwpoort, Oostende, Knokke). Value of OSPAR assessment (95% confidence interval on modeled concentration for 2016).
W01-W03, concentrations normalized 2.5% TOC, in accordance with OSPAR methodology (95% confidence interval on modeled concentration)
Sampling of bone over an area representative of the Belgian part of the North Sea. Value of OSPAR assessment (95% confidence interval on modeled concentration for 2016).
3 sampling locations (Nieuwpoort, Oostende, Knokke). Value of OSPAR assessment (95% confidence interval on modeled concentration for 2016).
W01-W03, concentrations normalized 2.5% TOC, in accordance with OSPAR methodology (95% confidence interval on modeled concentration)
Sampling of bone over an area representative of the Belgian part of the North Sea. Value of OSPAR assessment (95% confidence interval on modeled concentration for 2016).
3 sampling locations (Nieuwpoort, Oostende, Knokke). Value of OSPAR assessment (95% confidence interval on modeled concentration for 2016).
W01-W03, concentrations normalized 2.5% TOC, in accordance with OSPAR methodology (95% confidence interval on modeled concentration)
Sampling of bone over an area representative of the Belgian part of the North Sea. Value of OSPAR assessment (95% confidence interval on modeled concentration for 2016).
3 sampling locations (Nieuwpoort, Oostende, Knokke). Value of OSPAR assessment (95% confidence interval on modeled concentration for 2016).
W01-W03, concentrations normalized 2.5% TOC, in accordance with OSPAR methodology (95% confidence interval on modeled concentration)
Sampling of bone over an area representative of the Belgian part of the North Sea. Value of OSPAR assessment (95% confidence interval on modeled concentration for 2016).
3 sampling locations (Nieuwpoort, Oostende, Knokke). Value of OSPAR assessment (95% confidence interval on modeled concentration for 2016).
W01-03, concentrations normalized 2.5% TOC, in accordance with OSPAR methodology (95% confidence interval on modeled concentration)
W01 max values 2009-2014
3 sampling locations (Nieuwpoort, Oostende, Knokke). Value of OSPAR assessment (95% confidence interval on modeled concentration for 2016).
In accordance with OSPAR methodology. No ERL but values even lower than BAC.
W01-03, concentrations normalized 2.5% TOC, in accordance with OSPAR methodology (95% confidence interval on modeled concentration)
3 sampling locations (Nieuwpoort, Oostende, Knokke). Value of OSPAR assessment (95% confidence interval on modeled concentration for 2016).
Average concentration of eggs (10) collected in 2015.
According to OSPAR methodology.
OSPAR (2017). No significant trend.
OSPAR (2017). No significant trend.
According to OSPAR methodology.
W01-03, concentrations normalized 2.5% TOC, in accordance with OSPAR methodology (95% confidence interval on modeled concentration)
3 sampling locations (Nieuwpoort, Oostende, Knokke). Value of OSPAR assessment (95% confidence interval on modeled concentration for 2016).
According to OSPAR methodology.
W01-03, concentrations normalized 2.5% TOC, in accordance with OSPAR methodology (95% confidence interval on modeled concentration)
W01 max values 2009-2014
3 sampling locations (Nieuwpoort, Oostende, Knokke). Value of OSPAR assessment (95% confidence interval on modeled concentration for 2016).
Average concentration of eggs (10) collected in 2015.
OSPAR assessments
3 sampling locations (Nieuwpoort, Oostende, Knokke), values below detection limit
Average concentration of eggs (10) collected in 2015.
According to OSPAR methodology.
OSPAR (2017).
OSPAR (2017). No significant trend.
In accordance with OSPAR methodology. No ERL.
W01-03, concentrations normalized 2.5% TOC, in accordance with OSPAR methodology (95% confidence interval on modeled concentration)
3 sampling locations (Nieuwpoort, Oostende, Knokke). Value of OSPAR assessment (95% confidence interval on modeled concentration for 2016).
W01-03, concentrations normalized 2.5% TOC, in accordance with OSPAR methodology (95% confidence interval on modeled concentration)
3 sampling locations (Nieuwpoort, Oostende, Knokke). Value of OSPAR assessment (95% confidence interval on modeled concentration for 2016).
According to OSPAR methodology.
OSPAR assessments
3 sampling locations (Nieuwpoort, Oostende, Knokke), values below detection limit
Average concentration of eggs (10) collected in 2015.
<0.18, maximum value for the period 2013-2015, W01-03, no EAC
3 sampling locations (Nieuwpoort, Oostende, Knokke)
<0.18, maximum value for the period 2013-2015, W01-03, no EAC
3 sampling locations (Nieuwpoort, Oostende, Knokke), lower value below detection limit
maximum value for the period 2013-2015, values often lower then detection limit, W01-03, no EAC
3 sampling locations (Nieuwpoort, Oostende, Knokke), lower value below detection limit
maximum value for the period 2013-2015, values often lower then detection limit, W01-03, no EAC
3 sampling locations (Nieuwpoort, Oostende, Knokke), lower value below detection limit
maximum value for the period 2013-2015, values often lower then detection limit, W01-03, no EAC
3 sampling locations (Nieuwpoort, Oostende, Knokke), lower value below detection limit
W01-W03, concentrations normalized 2.5% TOC, in accordance with OSPAR methodology (95% confidence interval on modeled concentration)
Sampling of bone over an area representative of the Belgian part of the North Sea. Value of OSPAR assessment (95% confidence interval on modeled concentration for 2016).
3 sampling locations (Nieuwpoort, Oostende, Knokke). Value of OSPAR assessment (95% confidence interval on modeled concentration for 2016).
maximum value for the period 2013-2015, values often lower then detection limit, W01-03, no EAC
3 sampling locations (Nieuwpoort, Oostende, Knokke), lower value below detection limit
W01-03, concentrations normalized 2.5% TOC, in accordance with OSPAR methodology (95% confidence interval on modeled concentration)
3 sampling locations (Nieuwpoort, Oostende, Knokke). Value of OSPAR assessment (95% confidence interval on modeled concentration for 2016).
W07-10, concentrations normalized 2.5% TOC, in accordance with OSPAR methodology (95% confidence interval on modeled concentration)
3 sampling locations (Nieuwpoort, Oostende, Knokke). Value of OSPAR assessment (95% confidence interval on modeled concentration for 2016).
SUM PBDEs: W01 max value 2009-2014
W07-10, concentrations normalized 2.5% TOC, in accordance with OSPAR methodology (95% confidence interval on modeled concentration)
3 sampling locations (Nieuwpoort, Oostende, Knokke). Value of OSPAR assessment (95% confidence interval on modeled concentration for 2016).
According to OSPAR methodology.
Average concentration of eggs (10) collected in 2015.
Average values. Trend analysis by OSPAR (2017).
Average value. No significant trend (OSPAR, 2017).
W01, range of yearly average in period 2009-2014
Most values are lower than the determination limit, so that the trend could not be assessed. W01-03, normalized 2.5% TOC.
average value 2011-2013
according to OSPAR methodology
Related indicator
Criteria status
Good
Good
Good
Good
Good
Good
Good
Good
Good
Not good
Not good
Not good
Good
Good
Good
Good
Good
Good
Good
Good
Good
Good
Good
Good
Not good
Not good
Not good
Not good
Not good
Good
Good
Not good
Good
Good
Good
Not good
Not good
Not good
Good
Not good
Not good
Not good
Unknown
Good
Good
Good
Good
Not good
Not good
Not good
Not good
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Not good
Not good
Not good
Unknown
Unknown
Good
Good
Good
Good
Good
Good
Good
Not good
Not good
Not good
Not good
Not good
Not good
Not good
Not good
Description criteria
Element status
Good
Good
Good
Good
Good
Good
Good
Good
Good
Not good
Not good
Not good
Good
Good
Good
Good
Good
Good
Good
Good
Good
Good
Good
Good
Not good
Not good
Not good
Not good
Not good
Good
Good
Not good
Good
Good
Good
Not good
Not good
Not good
Good
Not good
Not good
Not good
Unknown
Good
Good
Good
Good
Not good
Good
Good
Not good
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Not good
Not good
Not good
Unknown
Unknown
Good
Good
Good
Good
Good
Good
Good
Not good
Not good
Not good
Not good
Not good
Not good
Not good
Not good
Description element
Sum of 62 congeners
Most values are below detection limit of 0.06µg/kg
Most values are below detection limit of 0.06µg/kg
Most values are below detection limit of 0.06µg/kg
Most values are below detection limit of 0.06µg/kg
Most values are below detection limit of 0.06µg/kg
Most values are below detection limit of 0.06µg/kg
Most values are below detection limit of 0.06µg/kg
Most values are below detection limit of 0.06µg/kg
Most values are below detection limit of 0.06µg/kg
Most values are below detection limit of 0.06µg/kg
Most values are below detection limit of 0.06µg/kg
Most values are below detection limit of 0.06µg/kg
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
OOAO
OOAO
OOAO
OOAO
Integration rule description parameter
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Integration rule type criteria
Not relevant
Not relevant
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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
100.00
100.00
100.00
100.00
GES extent achieved
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
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 expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
Description overall status
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
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
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
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
Related targets
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38

Belgische territoriale wateren (1-12 zeemijl) /eaux territoriales belges (1-12 milles nautiques) (BEFED_TEW)

GES component
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
D8
Feature
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - non UPBT substances
Contaminants - UPBT substances
Contaminants - UPBT substances
Contaminants - UPBT substances
Contaminants - UPBT substances
Contaminants - UPBT substances
Contaminants - UPBT substances
Contaminants - UPBT substances
Contaminants - UPBT substances
Contaminants - UPBT substances
Contaminants - UPBT substances
Contaminants - UPBT substances
Contaminants - UPBT substances
Contaminants - UPBT substances
Contaminants - UPBT substances
Contaminants - UPBT substances
Contaminants - UPBT substances
Contaminants - UPBT substances
Element
2,2,3,4,4,5,5-heptachlorobiphenyl
2,2,3,4,4,5,5-heptachlorobiphenyl
2,2,3,4,4,5-hexachlorobiphenyl
2,2,3,4,4,5-hexachlorobiphenyl
2,2,4,4,5,5-hexachlorobiphenyl
2,2,4,4,5,5-hexachlorobiphenyl
2,2,4,5,5-pentachlorobiphenyl
2,2,4,5,5-pentachlorobiphenyl
2,2,5,5-tetrachlorobiphenyl
2,2,5,5-tetrachlorobiphenyl
2,4,4-trichlorobiphenyl
2,4,4-trichlorobiphenyl
Anthracene
Anthracene
Arsenic
Benzo(a)anthracene
Cadmium
Cadmium
Chromium
Chrysene
Copper
Fluoranthene
Fluoranthene
Hexachlorobenzene
Hexachlorobutadiene
Lead
Lead
Nickel
Phenanthrene
Pyrene
Zinc
2,2,4,4,5,5-hexabromodiphenyl ether
2,2,4,4,5,6-hexabromodiphenyl ether
2,2,4,4,5-pentabromodiphenyl ether
2,2,4,4,6-pentabromodiphenyl ether
2,2,4,4-tetrabromodiphenyl ether
2,3,4,4,5-pentachlorobiphenyl
2,3,4,4,5-pentachlorobiphenyl
2,4,4-tribromodiphenyl ether
Benzo(a)pyrene
Benzo(ghi)perylene
Brominated diphenylethers (congener numbers 28, 47, 99, 100, 153 and 154)
Indeno(1,2,3-cd)pyrene
Mercury
Mercury
Total PAHs (Benzo(a)pyrene, Benzo(b)fluoranthene, Benzo(k)fluoranthene, Benzo(ghi)perylene, Indeno(1,2,3-cd)pyrene)
Tributyltin compounds
Tributyltin compounds
Element code
CAS_35065-29-3
CAS_35065-29-3
CAS_35065-28-2
CAS_35065-28-2
CAS_35065-27-1
CAS_35065-27-1
CAS_37680-73-2
CAS_37680-73-2
CAS_35693-99-3
CAS_35693-99-3
CAS_7012-37-5
CAS_7012-37-5
CAS_120-12-7
CAS_120-12-7
CAS_7440-38-2
CAS_56-55-3
CAS_7440-43-9
CAS_7440-43-9
CAS_7440-47-3
CAS_218-01-9
CAS_7440-50-8
CAS_206-44-0
CAS_206-44-0
CAS_118-74-1
CAS_87-68-3
CAS_7439-92-1
CAS_7439-92-1
CAS_7440-02-0
CAS_85-01-8
CAS_129-00-0
CAS_7440-66-6
CAS_68631-49-2
CAS_207122-15-4
CAS_60348-60-9
CAS_189084-64-8
CAS_5436-43-1
CAS_31508-00-6
CAS_31508-00-6
CAS_41318-75-6
CAS_50-32-8
CAS_191-24-2
EEA_32-04-2
CAS_193-39-5
CAS_7439-97-6
CAS_7439-97-6
EEA_33-56-7
TBTIN
TBTIN
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
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
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
ICES
ICES
Element 2
Element 2 code
Element 2 code source
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
EU
EU
EU
EU
EU
EU
EU
Criterion
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
D8C1
Parameter
CONC-S-63
Other
CONC-S-63
Other
CONC-S-63
Other
CONC-S-63
Other
CONC-S-63
Other
CONC-S-63
Other
CONC-S-63
Concentration in water
CONC-S-63
CONC-S-63
CONC-S-63
Other
CONC-S-63
CONC-S-63
CONC-S-63
CONC-S-63
Concentration in water
Other
Other
CONC-S-63
Other
CONC-S-63
CONC-S-63
CONC-S-63
CONC-S-63
CONC-S-63
CONC-S-63
CONC-S-63
CONC-S-63
CONC-S-63
CONC-S-63
Other
CONC-S-63
CONC-S-63
CONC-S-63
Concentration in water
CONC-S-63
CONC-S-63
Other
Concentration in water
CONC-S-63
Concentration in water
Parameter other
Concentration in liver of Platichthys flesus
Concentration in liver of Platichthys flesus
Concentration in liver of Platichthys flesus
Concentration in liver of Platichthys flesus
Concentration in liver of Platichthys flesus
Concentration in liver of Platichthys flesus
Concentration in Platichthys flesus
Concentration in muscles of Platichthys flesus
Concentration in muscles of Platichthys flesus
Concentration in Platichthys flesus
Concentration in liver of Platichthys flesus
Concentration in Platichthys flesus
Threshold value upper
12.0
60.97
7.9
41.21
40.0
206.05
3.0
15.73
2.7
14.04
1.7
8.71
85.0
0.1
261.0
1.2
1000.0
81.0
384.0
34.0
600.0
0.12
10.0
55.0
47.0
1500.0
240.0
665.0
150.0
0.6
3.25
430.0
85.0
0.014
240.0
0.15
20.0
0.00017
0.0002
Threshold value lower
Threshold qualitative
Downward trend
Downward trend
Downward trend
Downward trend
Downward trend
Downward trend
Downward trend
Downward trend
Downward trend
Threshold value source
OSPAR Convention
OSPAR Convention
OSPAR Convention
OSPAR Convention
OSPAR Convention
OSPAR Convention
OSPAR Convention
OSPAR Convention
OSPAR Convention
OSPAR Convention
OSPAR Convention
OSPAR Convention
OSPAR Convention
Priority substances Directive (2013/39/EU)
OSPAR Convention
OSPAR Convention
OSPAR Convention
OSPAR Convention
OSPAR Convention
OSPAR Convention
OSPAR Convention
Priority substances Directive (2013/39/EU)
OSPAR Convention
OSPAR Convention
OSPAR Convention
OSPAR Convention
OSPAR Convention
OSPAR Convention
OSPAR Convention
OSPAR Convention
OSPAR Convention
OSPAR Convention
OSPAR Convention
Priority substances Directive (2013/39/EU)
OSPAR Convention
OSPAR Convention
OSPAR Convention
Priority substances Directive (2013/39/EU)
Priority substances Directive (2013/39/EU)
Threshold value source other
Value achieved upper
1.48
16.75
2.07
29.38
3.47
33.8
0.76
9.73
0.34
7.78
0.71
1.3
34.4
0.0137
81.3
64.1
0.84
127.25
225.1
82.4
58.0
159.8
0.0359
0.06
0.2
583.0
29.24
140.1
123.4
117.5
350.6
0.3
0.19
1.14
0.19
4.55
2.26
8.48
0.19
67.6
61.2
0.0127
76.8
0.29
73.7
0.0031
4.75
0.0042
Value achieved lower
0.42
1.03
1.3
0.43
0.21
0.37
10.0
14.5
16.7
0.26
126.0
22.0
36.0
35.9
203.7
38.7
42.8
31.4
246.9
0.82
22.3
16.9
26.2
0.11
0.0004
0.68
0.0032
Value unit
microgram per kilogram of dry weight
microgram per kilogram of wet weight
microgram per kilogram of dry weight
microgram per kilogram of wet weight
microgram per kilogram of dry weight
microgram per kilogram of wet weight
microgram per kilogram of dry weight
microgram per kilogram of wet weight
microgram per kilogram of dry weight
microgram per kilogram of wet weight
microgram per kilogram of dry weight
microgram per kilogram of wet weight
microgram per kilogram of dry weight
microgram per litre
microgram per kilogram of dry weight
microgram per kilogram of dry weight
microgram per kilogram of dry weight
microgram per kilogram of wet weight
microgram per kilogram of dry weight
microgram per kilogram of dry weight
microgram per kilogram of dry weight
microgram per kilogram of dry weight
microgram per litre
microgram per kilogram of wet weight
microgram per kilogram of wet weight
microgram per kilogram of dry weight
microgram per kilogram of wet weight
microgram per kilogram of dry weight
microgram per kilogram of dry weight
microgram per kilogram of dry weight
microgram per kilogram of dry weight
microgram per kilogram of dry weight
microgram per kilogram of dry weight
microgram per kilogram of dry weight
microgram per kilogram of dry weight
microgram per kilogram of dry weight
microgram per kilogram of dry weight
microgram per kilogram of wet weight
microgram per kilogram of dry weight
microgram per kilogram of dry weight
microgram per kilogram of dry weight
microgram per litre
microgram per kilogram of dry weight
microgram per kilogram of dry weight
microgram per kilogram of wet weight
microgram per litre
microgram per kilogram of dry weight
microgram per litre
Value unit other
Proportion threshold value
Proportion value achieved
Proportion threshold value unit
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
Trend
Unknown
Improving
Unknown
Improving
Unknown
Improving
Unknown
Improving
Unknown
Improving
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Stable
Unknown
Unknown
Unknown
Unknown
Unknown
Improving
Unknown
Unknown
Stable
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Improving
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Stable
Unknown
Unknown
Unknown
Parameter achieved
Yes
Yes
Yes
Yes
Yes
Yes
Yes
Yes
Yes
Yes
Yes
Yes
Yes
Yes
Unknown
Yes
Yes
Yes
No
Yes
No
Yes
Yes
Yes
Yes
No
Yes
Unknown
Yes
Yes
No
Unknown
Unknown
Unknown
Unknown
Unknown
No
No
Unknown
Yes
Yes
Yes
Yes
No
No
No
Unknown
No
Description parameter
W04-W06, concentrations normalized 2.5% TOC, in accordance with OSPAR methodology (95% confidence interval on modeled concentration)
Sampling of bone over an area representative of the Belgian part of the North Sea. Value of OSPAR assessment (95% confidence interval on modeled concentration for 2016).
W04-W06, concentrations normalized 2.5% TOC, in accordance with OSPAR methodology (95% confidence interval on modeled concentration)
Sampling of bone over an area representative of the Belgian part of the North Sea. Value of OSPAR assessment (95% confidence interval on modeled concentration for 2016).
W04-W06, concentrations normalized 2.5% TOC, in accordance with OSPAR methodology (95% confidence interval on modeled concentration)
Sampling of bone over an area representative of the Belgian part of the North Sea. Value of OSPAR assessment (95% confidence interval on modeled concentration for 2016).
W04-W06, concentrations normalized 2.5% TOC, in accordance with OSPAR methodology (95% confidence interval on modeled concentration)
Sampling of bone over an area representative of the Belgian part of the North Sea. Value of OSPAR assessment (95% confidence interval on modeled concentration for 2016).
W04-W06, concentrations normalized 2.5% TOC, in accordance with OSPAR methodology (95% confidence interval on modeled concentration)
Sampling of bone over an area representative of the Belgian part of the North Sea. Value of OSPAR assessment (95% confidence interval on modeled concentration for 2016).
W04-W06, concentrations normalized 2.5% TOC, in accordance with OSPAR methodology (95% confidence interval on modeled concentration)
Sampling of bone over an area representative of the Belgian part of the North Sea. Value of OSPAR assessment (95% confidence interval on modeled concentration for 2016).
W04-06, concentrations normalized 2.5% TOC, in accordance with OSPAR methodology (95% confidence interval on modeled concentration)
W05-W06 max values 2009-2014
In accordance with OSPAR methodology. No ERL.
W04-06, concentrations normalized 2.5% TOC, in accordance with OSPAR methodology (95% confidence interval on modeled concentration)
According to OSPAR methodology.
OSPAR (2017). No significant trend.
According to OSPAR methodology.
W04-06, concentrations normalized 2.5% TOC, in accordance with OSPAR methodology (95% confidence interval on modeled concentration)
According to OSPAR methodology.
W04-06, concentrations normalized 2.5% TOC, in accordance with OSPAR methodology (95% confidence interval on modeled concentration)
W05-W06 max values 2009-2014
OSPAR assessments, 3 sampling locations (Nieuwpoort, Oostende, Knokke), values below detection limit
OSPAR assessments, 3 sampling locations (Nieuwpoort, Oostende, Knokke), values below detection limit
According to OSPAR methodology.
OSPAR (2017). No significant trend.
In accordance with OSPAR methodology. No ERL.
W04-06, concentrations normalized 2.5% TOC, in accordance with OSPAR methodology (95% confidence interval on modeled concentration)
W04-06, concentrations normalized 2.5% TOC, in accordance with OSPAR methodology (95% confidence interval on modeled concentration)
According to OSPAR methodology.
maximum value for the period 2013-2015, values often lower then detection limit, W04-06, no EAC
<0.19, maximum value for the period 2013-2015, W04-06, no EAC
maximum value for the period 2013-2015, values often lower then detection limit, W04-06, no EAC
<0.19, maximum value for the period 2013-2015, W04-06, no EAC
maximum value for the period 2013-2015, values often lower then detection limit, W04-06, no EAC
W04-W06, concentrations normalized 2.5% TOC, in accordance with OSPAR methodology (95% confidence interval on modeled concentration)
Sampling of bone over an area representative of the Belgian part of the North Sea. Value of OSPAR assessment (95% confidence interval on modeled concentration for 2016).
<0.19, maximum value for the period 2013-2015, W04-06, no EAC
W04-06, concentrations normalized 2.5% TOC, in accordance with OSPAR methodology (95% confidence interval on modeled concentration)
W07-10, concentrations normalized 2.5% TOC, in accordance with OSPAR methodology (95% confidence interval on modeled concentration)
SUM PBDEs: W05-W06 max values 2009-2014
W07-10, concentrations normalized 2.5% TOC, in accordance with OSPAR methodology (95% confidence interval on modeled concentration)
According to OSPAR methodology.
Average value. No significant trend (OSPAR, 2017).
W05-W06, range of yearly average in period 2009-2014
Most values are lower than the determination limit, so that the trend could not be assessed. W04-06, normalized 2.5% TOC.
range of average values 2011-2013
Related indicator
Criteria status
Good
Good
Good
Good
Good
Good
Good
Good
Good
Good
Good
Good
Good
Good
Unknown
Good
Good
Good
Not good
Good
Not good
Good
Good
Good
Good
Not good
Not good
Unknown
Good
Good
Not good
Unknown
Unknown
Unknown
Unknown
Unknown
Not good
Not good
Unknown
Good
Good
Good
Good
Not good
Not good
Not good
Not good
Not good
Description criteria
Element status
Good
Good
Good
Good
Good
Good
Good
Good
Good
Good
Good
Good
Good
Good
Unknown
Good
Good
Good
Not good
Good
Not good
Good
Good
Good
Good
Not good
Not good
Unknown
Good
Good
Not good
Unknown
Unknown
Unknown
Unknown
Unknown
Not good
Not good
Unknown
Good
Good
Good
Good
Not good
Not good
Not good
Not good
Not good
Description element
Most values are below detection limit of 0.06µg/kg
Most values are below detection limit of 0.06µg/kg
Most values are below detection limit of 0.06µg/kg
Most values are below detection limit of 0.06µg/kg
Most values are below detection limit of 0.06µg/kg
Most values are below detection limit of 0.06µg/kg
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
Integration rule description parameter
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
Assessment in water, sediment and biota
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
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
GES extent achieved
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
GES achieved
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
Description overall status
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
Standards are not yet available for all substances, e.g. still need improvement for metals. A review of certain environmental criteria will be considered at regional level. Almost all substances for which good environmental status was not achieved belong to the persistent, bio-accumulative and toxic substances (eg. PCBs and mercury). Certainly with top predators, such as the fish thief, high concentrations of persistent pollutants are measured by accumulation in the food chain. Even if measures are taken to limit or eliminate emissions, these substances can still be present in the marine environment for a long time and, due to the persistent nature, concentrations will decrease very gradually. Decreasing concentrations were noted for mercury, lead, tributyl tin, PCBs and PAHs. - Radioactivity measured in the marine environment is mainly of natural origin. The activity of nuclides from nuclear power plants (H-3, Cs-137, Pu and Am isotopes) drops or remains stable, except for H-3.
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
2011-2016
2011-2016
2011-2016
2011-2016
2011-2016
2011-2016
2011-2016
Related pressures
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
Related targets
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38
  • D8.T1
  • D8.T2
  • D8.T3
  • Target 33
  • Target 35
  • Target 38