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 |
|
|
|
|
|
|
Related targets |
|
|
|
|
|
|
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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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 |
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Related targets |
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BELGISCHE KUSTZONE (BEFED_CW)
GES component |
D8
|
D8
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D8
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D8
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D8
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D8
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D8
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D8
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D8
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D8
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D8
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D8
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D8
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D8
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D8
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D8
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D8
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D8
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D8
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D8
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D8
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D8
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D8
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D8
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D8
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D8
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D8
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D8
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D8
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D8
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D8
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D8
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D8
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D8
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D8
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D8
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D8
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D8
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D8
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D8
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D8
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D8
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D8
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D8
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D8
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D8
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D8
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D8
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D8
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D8
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D8
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D8
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D8
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D8
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D8
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D8
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D8
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D8
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D8
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D8
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D8
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D8
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D8
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D8
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D8
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D8
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D8
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D8
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D8
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D8
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D8
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D8
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D8
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D8
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D8
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D8
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D8
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D8
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D8
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D8
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D8
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---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
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 |
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Element 2 code |
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Element 2 code source |
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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
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Integration rule description criteria |
|||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
GES extent threshold |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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 |
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Related targets |
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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 |
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