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
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
Related targets
  • D8C1

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
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
Related targets
  • D8C1
  • D8C1
  • D8C1
  • D8C1
  • D8C1
  • D8C1

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
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
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
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
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
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
  • Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events
Related targets
  • D8C1
  • D8C1
  • D8C1
  • D8C1
  • D8C1
  • D8C1
  • D8C1
  • D8C1
  • D8C1
  • D8C1
  • D8C1
  • D8C1
  • D8C1
  • D8C1
  • D8C1
  • D8C1
  • D8C1
  • D8C1
  • D8C1
  • D8C1
  • D8C1
  • D8C1
  • D8C1