Member State report / Art8 / 2018 / D8 / Slovenia / Mediterranean: Adriatic 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 | Slovenia |
Region/subregion | Mediterranean: Adriatic Sea |
Reported by | Institute for Water of the Republic of Slovenia |
Report date | 2020-08-13 |
Report access | MSFD_Article_8_GES__1_modified.xml |
obmoèje morskih voda (MAD-SI-MRU-1)
GES component |
D8
|
---|---|
Feature |
Acute pollution events
|
Element |
|
Element code |
|
Element code source |
|
Element 2 |
|
Element 2 code |
|
Element 2 code source |
|
Element source |
|
Criterion |
D8C3
|
Parameter |
Extent
|
Parameter other |
|
Threshold value upper |
|
Threshold value lower |
|
Threshold qualitative |
spillage volume <7 tonnes
|
Threshold value source |
|
Threshold value source other |
|
Value achieved upper |
|
Value achieved lower |
|
Value unit |
|
Value unit other |
|
Proportion threshold value |
|
Proportion value achieved |
|
Proportion threshold value unit |
|
Trend |
Unknown |
Parameter achieved |
Yes |
Description parameter |
So far, there have been no significant acute pollution in marine waters under the jurisdiction of the Republic of Slovenia by spillage of petroleum products or other dangerous substances (<7t). These are mainly minor operational pollution.
|
Related indicator |
|
Criteria status |
Good |
Description criteria |
|
Element status |
|
Description element |
|
Integration rule type parameter |
|
Integration rule description parameter |
|
Integration rule type criteria |
|
Integration rule description criteria |
|
GES extent threshold |
|
GES extent achieved |
|
GES extent unit |
|
GES achieved |
GES achieved |
Description overall status |
|
Assessments period |
2011-2016 |
Related pressures |
|
Related targets |
|
obalne vode (MAD-SI-MRU-11)
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
|
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
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 - UPBT substances
|
Contaminants - UPBT substances
|
Contaminants - UPBT substances
|
Contaminants - UPBT substances
|
Contaminants - UPBT substances
|
Contaminants - UPBT substances
|
Element |
1,2-Dichloroethane |
Alpha-HCH |
Anthracene |
Antimony |
Arsenic and its compounds |
Beta-HCH |
Cadmium and its compounds |
Cadmium and its compounds |
Chromium and its compounds |
Cobalt and its compounds |
Copper and its compounds |
Delta-HCH |
Dibutyltin |
Fluoranthene |
Gamma-HCH (Lindane) |
Hexachlorobenzene |
Lead and its compounds |
Lead and its compounds |
Mineral oil index |
Molybdenum and its compounds |
Naphthalene |
Nickel and its compounds |
Phenol |
Selenium and its compounds |
Zinc and its compounds |
Benzo(a)pyrene |
Benzo(g,h,i)perylene |
Indeno(1,2,3,-cd)pyrene |
Mercury and its compounds |
Mercury and its compounds |
Tributyltin compounds |
Element code |
CAS_107-06-2 |
CAS_319-84-6 |
CAS_120-12-7 |
CAS_7440-36-0 |
CAS_7440-38-2 |
CAS_319-85-7 |
CAS_7440-43-9 |
CAS_7440-43-9 |
CAS_7440-47-3 |
CAS_7440-48-4 |
CAS_7440-50-8 |
CAS_319-86-8 |
CAS_1002-53-5 |
CAS_206-44-0 |
CAS_58-89-9 |
CAS_118-74-1 |
CAS_7439-92-1 |
CAS_7439-92-1 |
EEA_33-22-7 |
CAS_7439-98-7 |
CAS_91-20-3 |
CAS_7440-02-0 |
CAS_108-95-2 |
CAS_7782-49-2 |
CAS_7440-66-6 |
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
|
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 |
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
|
Parameter |
Concentration in water
|
Concentration in water
|
Concentration in sediment
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in sediment
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in sediment
|
Concentration in water
|
Concentration in water
|
Concentration in sediment
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in sediment
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in sediment
|
Concentration in sediment
|
Concentration in sediment
|
Concentration in sediment
|
Concentration in water
|
Concentration in water
|
Parameter other |
|||||||||||||||||||||||||||||||
Threshold value upper |
10.0 |
0.002 |
0.085 |
3.2 |
7.0 |
0.002 |
1.2 |
0.2 |
12.0 |
0.3 |
8.2 |
0.002 |
0.02 |
0.6 |
0.002 |
0.05 |
47.0 |
1.3 |
0.05 |
24.0 |
0.16 |
8.6 |
7.7 |
6.0 |
52.0 |
0.43 |
0.085 |
0.24 |
0.15 |
0.07 |
0.0002 |
Threshold value lower |
|||||||||||||||||||||||||||||||
Threshold qualitative |
|||||||||||||||||||||||||||||||
Threshold value source |
|||||||||||||||||||||||||||||||
Threshold value source other |
|||||||||||||||||||||||||||||||
Value achieved upper |
0.2 |
0.002 |
0.01 |
1.0 |
1.52 |
0.004 |
0.12 |
0.055 |
3.5 |
6.0 |
2.4 |
0.004 |
0.0049 |
0.14 |
0.003 |
0.002 |
45.0 |
1.0 |
15.0 |
14.0 |
0.05 |
6.0 |
0.05 |
1.8 |
30.0 |
0.093 |
0.056 |
0.079 |
0.7 |
0.03 |
0.0007 |
Value achieved lower |
0.2 |
0.002 |
0.01 |
1.0 |
1.02 |
0.004 |
0.081 |
0.028 |
3.5 |
6.0 |
2.4 |
0.004 |
0.0004 |
0.018 |
0.003 |
0.002 |
19.0 |
0.3 |
15.0 |
13.0 |
0.05 |
6.0 |
0.05 |
1.8 |
30.0 |
0.013 |
0.011 |
0.012 |
0.16 |
0.013 |
0.00021 |
Value unit |
microgram per litre
|
microgram per litre
|
Other
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
Other
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
Other
|
microgram per litre
|
microgram per litre
|
Other
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
Other
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
Other
|
Other
|
Other
|
Other
|
microgram per litre
|
microgram per litre
|
Value unit other |
milligram per kilogram
|
milligram per kilogram
|
milligram per kilogram
|
milligram per kilogram
|
milligram per kilogram
|
milligram per kilogram
|
milligram per kilogram
|
milligram per kilogram
|
milligam per kilogram
|
||||||||||||||||||||||
Proportion threshold value |
100.0 |
100.0 |
100.0 |
100.0 |
100.0 |
100.0 |
100.0 |
100.0 |
100.0 |
100.0 |
100.0 |
100.0 |
100.0 |
100.0 |
100.0 |
100.0 |
100.0 |
100.0 |
100.0 |
100.0 |
100.0 |
100.0 |
100.0 |
100.0 |
100.0 |
100.0 |
100.0 |
100.0 |
100.0 |
||
Proportion value achieved |
100.0 |
100.0 |
100.0 |
100.0 |
100.0 |
100.0 |
100.0 |
100.0 |
100.0 |
100.0 |
100.0 |
100.0 |
100.0 |
100.0 |
100.0 |
100.0 |
100.0 |
100.0 |
100.0 |
100.0 |
100.0 |
100.0 |
100.0 |
100.0 |
100.0 |
100.0 |
100.0 |
100.0 |
100.0 |
||
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 |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Parameter achieved |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
No |
Yes |
No |
Description parameter |
The assessment of the situation follows the WFD methodology. The limit value is the environmental quality standard (EQS) for annual averages (LP-EQS). In the absence of this, the EQS for maximum allowable concentrations (VOC-EQS) are taken as the limit value.
All measured values are below the limit of quantification of the method (LOQ <0.2).
|
The assessment of the situation follows the WFD methodology. The limit value is the environmental quality standard (EQS) for annual averages (LP-EQS). In the absence of this, the EQS for maximum allowable concentrations (VOC-EQS) are taken as the limit value. The limit value applies to the sum of HCHs).
All measured values are below the limit of quantification of the method (LOQ <0.002).
|
There are no limit values set at national level for concentrations of pollutants in sediments. Maximum ERLs taken from Lyons et al. (2017) were considered as limit values.
Most of the measured values are below the limit of quantification of the method (LOQ <0.01).
|
The assessment of the situation follows the WFD methodology. The limit value is the environmental quality standard (EQS) for annual averages (LP-EQS). In the absence of this, the EQS for maximum allowable concentrations (VOC-EQS) are taken as the limit value.
All measured values are below the limit of quantification of the method (LOQ <1).
|
The assessment of the situation follows the WFD methodology. The limit value is the environmental quality standard (EQS) for annual averages (LP-EQS). In the absence of this, the EQS for maximum allowable concentrations (VOC-EQS) are taken as the limit value.
|
The assessment of the situation follows the WFD methodology. The limit value is the environmental quality standard (EQS) for annual averages (LP-EQS). In the absence of this, the EQS for maximum allowable concentrations (VOC-EQS) are taken as the limit value. The limit value applies to the sum of HCHs).
All measured values are below the limit of quantification of the method (LOQ <0.004).
|
There are no limit values set at national level for concentrations of pollutants in sediments. Maximum ERLs taken from Lyons et al. (2017) were considered as limit values.
|
The assessment of the situation follows the WFD methodology. The limit value is the environmental quality standard (EQS) for annual averages (LP-EQS). In the absence of this, the EQS for maximum allowable concentrations (VOC-EQS) are taken as the limit value.
|
The assessment of the situation follows the WFD methodology. The limit value is the environmental quality standard (EQS) for annual averages (LP-EQS). In the absence of this, the EQS for maximum allowable concentrations (VOC-EQS) are taken as the limit value.
All measured values are below the limit of quantification of the method (LOQ <3.5).
|
The assessment of the situation follows the WFD methodology. The limit value is the environmental quality standard (EQS) for annual averages (LP-EQS). In the absence of this, the EQS for maximum allowable concentrations (VOC-EQS) are taken as the limit value.
All measured values are below the limit of quantification of the method (LOQ <6).
|
The assessment of the situation follows the WFD methodology. The limit value is the environmental quality standard (EQS) for annual averages (LP-EQS). In the absence of this, the EQS for maximum allowable concentrations (VOC-EQS) are taken as the limit value.
All measured values are below the limit of quantification of the method (LOQ <2.4).
|
The assessment of the situation follows the WFD methodology. The limit value is the environmental quality standard (EQS) for annual averages (LP-EQS). In the absence of this, the EQS for maximum allowable concentrations (VOC-EQS) are taken as the limit value. The limit value applies to the sum of HCHs).
All measured values are below the limit of quantification of the method (LOQ <0.004).
|
The assessment of the situation follows the WFD methodology. The limit value is the environmental quality standard (EQS) for annual averages (LP-EQS). In the absence of this, the EQS for maximum allowable concentrations (VOC-EQS) are taken as the limit value.
|
There are no limit values set at national level for concentrations of pollutants in sediments. Maximum ERLs taken from Lyons et al. (2017) were considered as limit values.
|
The assessment of the situation follows the WFD methodology. The limit value is the environmental quality standard (EQS) for annual averages (LP-EQS). In the absence of this, the EQS for maximum allowable concentrations (VOC-EQS) are taken as the limit value. The limit value applies to the sum of HCHs).
All measured values are below the limit of quantification of the method (LOQ <0.003).
|
The assessment of the situation follows the WFD methodology. The limit value is the environmental quality standard (EQS) for annual averages (LP-EQS). In the absence of this, the EQS for maximum allowable concentrations (VOC-EQS) are taken as the limit value.
All measured values are below the limit of quantification of the method (LOQ <0.002).
|
There are no limit values set at national level for concentrations of pollutants in sediments. Maximum ERLs taken from Lyons et al. (2017) were considered as limit values.
|
The assessment of the situation follows the WFD methodology. The limit value is the environmental quality standard (EQS) for annual averages (LP-EQS). In the absence of this, the EQS for maximum allowable concentrations (VOC-EQS) are taken as the limit value.
All measured values are below the limit of quantification of the method (for 2011-2015: LOQ <1
|
The assessment of the situation follows the WFD methodology. The limit value is the environmental quality standard (EQS) for annual averages (LP-EQS). In the absence of this, the EQS for maximum allowable concentrations (VOC-EQS) are taken as the limit value.
All measured values are below the limit of quantification of the method (LOQ <15).
|
The assessment of the situation follows the WFD methodology. The limit value is the environmental quality standard (EQS) for annual averages (LP-EQS). In the absence of this, the EQS for maximum allowable concentrations (VOC-EQS) are taken as the limit value.
|
There are no limit values set at national level for concentrations of pollutants in sediments. Maximum ERLs taken from Lyons et al. (2017) were considered as limit values.
All measured values are below the limit of quantification of the method (LOQ <0.05).
|
The assessment of the situation follows the WFD methodology. The limit value is the environmental quality standard (EQS) for annual averages (LP-EQS). In the absence of this, the EQS for maximum allowable concentrations (VOC-EQS) are taken as the limit value.
All measured values are below the limit of quantification of the method (LOQ <6).
|
The assessment of the situation follows the WFD methodology. The limit value is the environmental quality standard (EQS) for annual averages (LP-EQS). In the absence of this, the EQS for maximum allowable concentrations (VOC-EQS) are taken as the limit value.
All measured values are below the limit of quantification of the method (LOQ <0.05).
|
The assessment of the situation follows the WFD methodology. The limit value is the environmental quality standard (EQS) for annual averages (LP-EQS). In the absence of this, the EQS for maximum allowable concentrations (VOC-EQS) are taken as the limit value.
All measured values are below the limit of quantification of the method (LOQ <1.8).
|
The assessment of the situation follows the WFD methodology. The limit value is the environmental quality standard (EQS) for annual averages (LP-EQS). In the absence of this, the EQS for maximum allowable concentrations (VOC-EQS) are taken as the limit value.
All measured values are below the limit of quantification of the method (LOQ <30).
|
There are no limit values set at national level for concentrations of pollutants in sediments. Maximum ERLs taken from Lyons et al. (2017) were considered as limit values.
|
There are no limit values set at national level for concentrations of pollutants in sediments. Maximum ERLs taken from Lyons et al. (2017) were considered as limit values.
|
There are no limit values set at national level for concentrations of pollutants in sediments. Maximum ERLs taken from Lyons et al. (2017) were considered as limit values.
|
There are no limit values set at national level for concentrations of pollutants in sediments. Maximum ERLs taken from Lyons et al. (2017) were considered as limit values.
|
The assessment of the situation follows the WFD methodology. The limit value is the environmental quality standard (EQS) for annual averages (LP-EQS). In the absence of this, the EQS for maximum allowable concentrations (VOC-EQS) are taken as the limit value.
|
The assessment of the situation follows the WFD methodology. The limit value is the environmental quality standard (EQS) for annual averages (LP-EQS). In the absence of this, the EQS for maximum allowable concentrations (VOC-EQS) are taken as the limit value.
|
Related indicator |
|||||||||||||||||||||||||||||||
Criteria status |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Not good |
Not good |
Not good |
Description criteria |
|||||||||||||||||||||||||||||||
Element status |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Not good |
Not good |
Not good |
Description element |
|||||||||||||||||||||||||||||||
Integration rule type parameter |
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
Integration rule description parameter |
|||||||||||||||||||||||||||||||
Integration rule type criteria |
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
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 criteria |
|||||||||||||||||||||||||||||||
GES extent threshold |
|||||||||||||||||||||||||||||||
GES extent achieved |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
60.00 |
60.00 |
60.00 |
60.00 |
60.00 |
60.00 |
GES extent unit |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES expected to be achieved later than 2020, Article 14 exception reported |
GES expected to be achieved later than 2020, Article 14 exception reported |
GES expected to be achieved later than 2020, Article 14 exception reported |
GES expected to be achieved later than 2020, Article 14 exception reported |
GES expected to be achieved later than 2020, Article 14 exception reported |
GES expected to be achieved later than 2020, Article 14 exception reported |
Description overall status |
|||||||||||||||||||||||||||||||
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 |
Related pressures |
|
|
|
|
|
|
|||||||||||||||||||||||||
Related targets |
|
|
|
|
|
|
teritorialno morje (MAD-SI-MRU-12)
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
|
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
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 - UPBT substances
|
Contaminants - UPBT substances
|
Contaminants - UPBT substances
|
Contaminants - UPBT substances
|
Contaminants - UPBT substances
|
Contaminants - UPBT substances
|
Element |
Anthracene |
Antimony |
Arsenic and its compounds |
Cadmium and its compounds |
Cadmium and its compounds |
Chromium and its compounds |
Cobalt and its compounds |
Copper and its compounds |
Dibutyltin |
Fluoranthene |
Lead and its compounds |
Lead and its compounds |
Molybdenum and its compounds |
Naphthalene |
Nickel and its compounds |
Selenium and its compounds |
Zinc and its compounds |
Benzo(a)pyrene |
Benzo(g,h,i)perylene |
Indeno(1,2,3,-cd)pyrene |
Mercury and its compounds |
Mercury and its compounds |
Tributyltin compounds |
Element code |
CAS_120-12-7 |
CAS_7440-36-0 |
CAS_7440-38-2 |
CAS_7440-43-9 |
CAS_7440-43-9 |
CAS_7440-47-3 |
CAS_7440-48-4 |
CAS_7440-50-8 |
CAS_1002-53-5 |
CAS_206-44-0 |
CAS_7439-92-1 |
CAS_7439-92-1 |
CAS_7439-98-7 |
CAS_91-20-3 |
CAS_7440-02-0 |
CAS_7782-49-2 |
CAS_7440-66-6 |
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
|
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 |
Criterion |
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
Parameter |
Concentration in sediment
|
Concentration in water
|
Concentration in water
|
Concentration in sediment
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in sediment
|
Concentration in sediment
|
Concentration in water
|
Concentration in water
|
Concentration in sediment
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in sediment
|
Concentration in sediment
|
Concentration in sediment
|
Concentration in sediment
|
Concentration in water
|
Concentration in water
|
Parameter other |
|||||||||||||||||||||||
Threshold value upper |
0.085 |
3.2 |
7.0 |
1.2 |
0.2 |
12.0 |
0.3 |
8.2 |
0.02 |
0.6 |
47.0 |
1.3 |
24.0 |
0.16 |
8.6 |
6.0 |
52.0 |
0.43 |
0.085 |
0.24 |
0.15 |
0.07 |
0.0002 |
Threshold value lower |
|||||||||||||||||||||||
Threshold qualitative |
|||||||||||||||||||||||
Threshold value source |
Other (specify)
|
National
|
National
|
||||||||||||||||||||
Threshold value source other |
Lyons, B.P., et al, T. 2017. Determining Good Environmental Status under the MSFD: Case study … Marine Environmental Research 124: 118-129. |
||||||||||||||||||||||
Value achieved upper |
0.01 |
1.0 |
1.53 |
0.12 |
0.03 |
3.5 |
6.0 |
2.4 |
0.00414 |
0.05 |
41.0 |
3.0 |
13.0 |
0.05 |
6.0 |
1.8 |
30.0 |
0.034 |
0.039 |
0.036 |
1.4 |
0.059 |
0.0005 |
Value achieved lower |
0.01 |
1.0 |
1.02 |
0.05 |
0.06 |
3.5 |
6.0 |
2.4 |
0.00171 |
0.034 |
31.0 |
1.0 |
0.05 |
6.0 |
1.8 |
30.0 |
0.023 |
0.017 |
0.017 |
1.1 |
0.01 |
0.0005 |
|
Value unit |
Other
|
microgram per litre
|
microgram per litre
|
Other
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
Other
|
Other
|
microgram per litre
|
microgram per litre
|
Other
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
Other
|
Other
|
Other
|
Other
|
microgram per litre
|
microgram per litre
|
Value unit other |
milligram per kilogram
|
milligram per kilogram
|
milligram per kilogram
|
milligram per kilogram
|
milligram per kilogram
|
milligram per kilogram
|
milligram per kilogram
|
milligram per kilogram
|
milligram per kilogram
|
||||||||||||||
Proportion threshold value |
100.0 |
100.0 |
100.0 |
100.0 |
100.0 |
100.0 |
100.0 |
100.0 |
100.0 |
100.0 |
100.0 |
100.0 |
100.0 |
100.0 |
100.0 |
100.0 |
100.0 |
100.0 |
100.0 |
100.0 |
|||
Proportion value achieved |
100.0 |
100.0 |
100.0 |
100.0 |
100.0 |
100.0 |
100.0 |
100.0 |
100.0 |
100.0 |
100.0 |
100.0 |
100.0 |
100.0 |
100.0 |
100.0 |
100.0 |
100.0 |
100.0 |
100.0 |
|||
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 |
|||
Trend |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Parameter achieved |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
No |
Yes |
No |
Description parameter |
There are no limit values set at national level for concentrations of pollutants in sediments. Maximum ERLs taken from Lyons et al. (2017) were considered as limit values.
All measured values are below the limit of quantification of the method (LOQ <0.01).
|
The assessment of the situation follows the WFD methodology. The limit value is the environmental quality standard (EQS) for annual averages (LP-EQS). In the absence of this, the EQS for maximum allowable concentrations (VOC-EQS) are taken as the limit value.
All measured values are below the limit of quantification of the method (LOQ <1).
|
The assessment of the situation follows the WFD methodology. The limit value is the environmental quality standard (EQS) for annual averages (LP-EQS). In the absence of this, the EQS for maximum allowable concentrations (VOC-EQS) are taken as the limit value.
|
There are no limit values set at national level for concentrations of pollutants in sediments. Maximum ERLs taken from Lyons et al. (2017) were considered as limit values.
|
The assessment of the situation follows the WFD methodology. The limit value is the environmental quality standard (EQS) for annual averages (LP-EQS). In the absence of this, the EQS for maximum allowable concentrations (VOC-EQS) are taken as the limit value.
Most of the measured values are below the limit of quantification of the method (LOQ <0.06).
|
The assessment of the situation follows the WFD methodology. The limit value is the environmental quality standard (EQS) for annual averages (LP-EQS). In the absence of this, the EQS for maximum allowable concentrations (VOC-EQS) are taken as the limit value.
All measured values are below the limit of quantification of the method (LOQ <3.5).
|
The assessment of the situation follows the WFD methodology. The limit value is the environmental quality standard (EQS) for annual averages (LP-EQS). In the absence of this, the EQS for maximum allowable concentrations (VOC-EQS) are taken as the limit value.
All measured values are below the limit of quantification of the method (LOQ <6).
|
The assessment of the situation follows the WFD methodology. The limit value is the environmental quality standard (EQS) for annual averages (LP-EQS). In the absence of this, the EQS for maximum allowable concentrations (VOC-EQS) are taken as the limit value.
All measured values are below the limit of quantification of the method (LOQ <2.4).
|
The assessment of the situation follows the WFD methodology. The limit value is the environmental quality standard (EQS) for annual averages (LP-EQS). In the absence of this, the EQS for maximum allowable concentrations (VOC-EQS) are taken as the limit value.
|
There are no limit values set at national level for concentrations of pollutants in sediments. Maximum ERLs taken from Lyons et al. (2017) were considered as limit values.
|
There are no limit values set at national level for concentrations of pollutants in sediments. Maximum ERLs taken from Lyons et al. (2017) were considered as limit values.
|
LOQ for 2016: <3).
|
The assessment of the situation follows the WFD methodology. The limit value is the environmental quality standard (EQS) for annual averages (LP-EQS). In the absence of this, the EQS for maximum allowable concentrations (VOC-EQS) are taken as the limit value.
|
There are no limit values set at national level for concentrations of pollutants in sediments. Maximum ERLs taken from Lyons et al. (2017) were considered as limit values.
All measured values are below the limit of quantification of the method (LOQ <0.05).
|
The assessment of the situation follows the WFD methodology. The limit value is the environmental quality standard (EQS) for annual averages (LP-EQS). In the absence of this, the EQS for maximum allowable concentrations (VOC-EQS) are taken as the limit value.
All measured values were below the limit of quantification of the method (LOQ <6).
|
The assessment of the situation follows the WFD methodology. The limit value is the environmental quality standard (EQS) for annual averages (LP-EQS). In the absence of this, the EQS for maximum allowable concentrations (VOC-EQS) are taken as the limit value.
All measured values are below the limit of quantification of the method (LOQ <1.8).
|
The assessment of the situation follows the WFD methodology. The limit value is the environmental quality standard (EQS) for annual averages (LP-EQS). In the absence of this, the EQS for maximum allowable concentrations (VOC-EQS) are taken as the limit value.
All measured values are below the limit of quantification of the method (LOQ <30).
|
There are no limit values set at national level for concentrations of pollutants in sediments. Maximum ERLs taken from Lyons et al. (2017) were considered as limit values.
|
There are no limit values set at national level for concentrations of pollutants in sediments. Maximum ERLs taken from Lyons et al. (2017) were considered as limit values.
|
There are no limit values set at national level for concentrations of pollutants in sediments. Maximum ERLs taken from Lyons et al. (2017) were considered as limit values.
|
There are no limit values set at national level for concentrations of pollutants in sediments. Maximum ERLs taken from Lyons et al. (2017) were considered as limit values.
|
The assessment of the situation follows the WFD methodology. The limit value is the environmental quality standard (EQS) for annual averages (LP-EQS). In the absence of this, the EQS for maximum allowable concentrations (VOC-EQS) are taken as the limit value.
|
The assessment of the situation follows the WFD methodology. The limit value is the environmental quality standard (EQS) for annual averages (LP-EQS). In the absence of this, the EQS for maximum allowable concentrations (VOC-EQS) are taken as the limit value.
|
Related indicator |
|||||||||||||||||||||||
Criteria status |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
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 |
Good |
Good |
Good |
Good |
Good |
Good |
Not good |
Not good |
Not good |
Description element |
|||||||||||||||||||||||
Integration rule type parameter |
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
Integration rule description parameter |
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Integration rule type criteria |
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 criteria |
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GES extent threshold |
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GES extent achieved |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
60.00 |
60.00 |
60.00 |
60.00 |
60.00 |
60.00 |
GES extent unit |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES expected to be achieved later than 2020, Article 14 exception reported |
GES expected to be achieved later than 2020, Article 14 exception reported |
GES expected to be achieved later than 2020, Article 14 exception reported |
GES expected to be achieved later than 2020, Article 14 exception reported |
GES expected to be achieved later than 2020, Article 14 exception reported |
GES expected to be achieved later than 2020, Article 14 exception reported |
Description overall status |
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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 |
Related pressures |
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Related targets |
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