Member State report / Art10 / 2018 / D9 / Netherlands / NE Atlantic: Greater North Sea

Report type Member State report to Commission
MSFD Article Art. 10 Environmental targets (and Art. 17 updates)
Report due 2018-10-15
GES Descriptor D9 Contaminants in seafood
Member State Netherlands
Region/subregion NE Atlantic: Greater North Sea
Reported by Rijkswaterstaat Centre for Water management, Ministry of infrastructure and the environment
Report date 2019-04-15
Report access XML_ART10_201904091515.xml

Target code
ANSNL-D8T1
ANSNL-D8T1
ANSNL-D8T5
ANSNL-D8T5
ANSNL-D8T5
ANSNL-D8T5
ANSNL-D8T5
ANSNL-D8T5
ANSNL-D8T5
ANSNL-D8T5
ANSNL-D8T5
ANSNL-D8T5
ANSNL-D8T5
ANSNL-D8T5
ANSNL-D8T5
ANSNL-D8T5
ANSNL-D8T5
ANSNL-D8T5
ANSNL-D8T5
ANSNL-D8T5
ANSNL-D8T5
ANSNL-D8T5
ANSNL-D8T5
ANSNL-D8T5
ANSNL-D8T5
ANSNL-D8T5
ANSNL-D8T5
ANSNL-D8T5
ANSNL-D8T5
ANSNL-D8T5
ANSNL-D8T5
ANSNL-D8T5
ANSNL-D8T5
ANSNL-D8T5
ANSNL-D8T5
ANSNL-D8T5
ANSNL-D8T5
ANSNL-D8T5
ANSNL-D8T5
ANSNL-D8T5
ANSNL-D8T5
ANSNL-D8T5
ANSNL-D8T6
ANSNL-D8T6
ANSNL-D8T6
ANSNL-D8T6
ANSNL-D8T6
ANSNL-D8T6
ANSNL-D8T6
ANSNL-D8T6
ANSNL-D9T1
ANSNL-D9T1
ANSNL-D9T1
ANSNL-D9T1
ANSNL-D9T1
ANSNL-D9T1
ANSNL-D9T1
ANSNL-D9T1
ANSNL-D9T1
ANSNL-D9T1
Target description
Coastal waters: reducing the supply of pollutants that do not yet meet the WFD standards, in accordance with the timeline of the river basin management plans. Do not increase concentrations of pollutants that already comply with the WFD standards.
Coastal waters: reducing the supply of pollutants that do not yet meet the WFD standards, in accordance with the timeline of the river basin management plans. Do not increase concentrations of pollutants that already comply with the WFD standards.
Cleaning up acute serious contamination as quickly as possible, where necessary in cooperation within the Bonn Agreement.
Cleaning up acute serious contamination as quickly as possible, where necessary in cooperation within the Bonn Agreement.
Cleaning up acute serious contamination as quickly as possible, where necessary in cooperation within the Bonn Agreement.
Cleaning up acute serious contamination as quickly as possible, where necessary in cooperation within the Bonn Agreement.
Cleaning up acute serious contamination as quickly as possible, where necessary in cooperation within the Bonn Agreement.
Cleaning up acute serious contamination as quickly as possible, where necessary in cooperation within the Bonn Agreement.
Cleaning up acute serious contamination as quickly as possible, where necessary in cooperation within the Bonn Agreement.
Cleaning up acute serious contamination as quickly as possible, where necessary in cooperation within the Bonn Agreement.
Cleaning up acute serious contamination as quickly as possible, where necessary in cooperation within the Bonn Agreement.
Cleaning up acute serious contamination as quickly as possible, where necessary in cooperation within the Bonn Agreement.
Cleaning up acute serious contamination as quickly as possible, where necessary in cooperation within the Bonn Agreement.
Cleaning up acute serious contamination as quickly as possible, where necessary in cooperation within the Bonn Agreement.
Cleaning up acute serious contamination as quickly as possible, where necessary in cooperation within the Bonn Agreement.
Cleaning up acute serious contamination as quickly as possible, where necessary in cooperation within the Bonn Agreement.
Cleaning up acute serious contamination as quickly as possible, where necessary in cooperation within the Bonn Agreement.
Cleaning up acute serious contamination as quickly as possible, where necessary in cooperation within the Bonn Agreement.
Cleaning up acute serious contamination as quickly as possible, where necessary in cooperation within the Bonn Agreement.
Cleaning up acute serious contamination as quickly as possible, where necessary in cooperation within the Bonn Agreement.
Cleaning up acute serious contamination as quickly as possible, where necessary in cooperation within the Bonn Agreement.
Cleaning up acute serious contamination as quickly as possible, where necessary in cooperation within the Bonn Agreement.
Cleaning up acute serious contamination as quickly as possible, where necessary in cooperation within the Bonn Agreement.
Cleaning up acute serious contamination as quickly as possible, where necessary in cooperation within the Bonn Agreement.
Cleaning up acute serious contamination as quickly as possible, where necessary in cooperation within the Bonn Agreement.
Cleaning up acute serious contamination as quickly as possible, where necessary in cooperation within the Bonn Agreement.
Cleaning up acute serious contamination as quickly as possible, where necessary in cooperation within the Bonn Agreement.
Cleaning up acute serious contamination as quickly as possible, where necessary in cooperation within the Bonn Agreement.
Cleaning up acute serious contamination as quickly as possible, where necessary in cooperation within the Bonn Agreement.
Cleaning up acute serious contamination as quickly as possible, where necessary in cooperation within the Bonn Agreement.
Cleaning up acute serious contamination as quickly as possible, where necessary in cooperation within the Bonn Agreement.
Cleaning up acute serious contamination as quickly as possible, where necessary in cooperation within the Bonn Agreement.
Cleaning up acute serious contamination as quickly as possible, where necessary in cooperation within the Bonn Agreement.
Cleaning up acute serious contamination as quickly as possible, where necessary in cooperation within the Bonn Agreement.
Cleaning up acute serious contamination as quickly as possible, where necessary in cooperation within the Bonn Agreement.
Cleaning up acute serious contamination as quickly as possible, where necessary in cooperation within the Bonn Agreement.
Cleaning up acute serious contamination as quickly as possible, where necessary in cooperation within the Bonn Agreement.
Cleaning up acute serious contamination as quickly as possible, where necessary in cooperation within the Bonn Agreement.
Cleaning up acute serious contamination as quickly as possible, where necessary in cooperation within the Bonn Agreement.
Cleaning up acute serious contamination as quickly as possible, where necessary in cooperation within the Bonn Agreement.
Cleaning up acute serious contamination as quickly as possible, where necessary in cooperation within the Bonn Agreement.
Cleaning up acute serious contamination as quickly as possible, where necessary in cooperation within the Bonn Agreement.
Reducing the use of lead, among others in sport fishing
Reducing the use of lead, among others in sport fishing
Reducing the use of lead, among others in sport fishing
Reducing the use of lead, among others in sport fishing
Reducing the use of lead, among others in sport fishing
Reducing the use of lead, among others in sport fishing
Reducing the use of lead, among others in sport fishing
Reducing the use of lead, among others in sport fishing
The levels of pollutants (including PAHs, dioxins and heavy metals) in fish and fishery products from the North Sea do not exceed the maximum levels set in the EU Regulation 1881/2006.
The levels of pollutants (including PAHs, dioxins and heavy metals) in fish and fishery products from the North Sea do not exceed the maximum levels set in the EU Regulation 1881/2006.
The levels of pollutants (including PAHs, dioxins and heavy metals) in fish and fishery products from the North Sea do not exceed the maximum levels set in the EU Regulation 1881/2006.
The levels of pollutants (including PAHs, dioxins and heavy metals) in fish and fishery products from the North Sea do not exceed the maximum levels set in the EU Regulation 1881/2006.
The levels of pollutants (including PAHs, dioxins and heavy metals) in fish and fishery products from the North Sea do not exceed the maximum levels set in the EU Regulation 1881/2006.
The levels of pollutants (including PAHs, dioxins and heavy metals) in fish and fishery products from the North Sea do not exceed the maximum levels set in the EU Regulation 1881/2006.
The levels of pollutants (including PAHs, dioxins and heavy metals) in fish and fishery products from the North Sea do not exceed the maximum levels set in the EU Regulation 1881/2006.
The levels of pollutants (including PAHs, dioxins and heavy metals) in fish and fishery products from the North Sea do not exceed the maximum levels set in the EU Regulation 1881/2006.
The levels of pollutants (including PAHs, dioxins and heavy metals) in fish and fishery products from the North Sea do not exceed the maximum levels set in the EU Regulation 1881/2006.
The levels of pollutants (including PAHs, dioxins and heavy metals) in fish and fishery products from the North Sea do not exceed the maximum levels set in the EU Regulation 1881/2006.
Feature(s)
  • Contaminants - UPBT substances
  • Contaminants - non UPBT substances
  • Contaminants - UPBT substances
  • Contaminants - non UPBT substances
  • Contaminants - UPBT substances
  • Contaminants - non UPBT substances
  • Contaminants - UPBT substances
  • Contaminants - non UPBT substances
  • Contaminants - UPBT substances
  • Contaminants - non UPBT substances
  • Contaminants - UPBT substances
  • Contaminants - non UPBT substances
  • Contaminants - UPBT substances
  • Contaminants - non UPBT substances
  • Contaminants - UPBT substances
  • Contaminants - non UPBT substances
  • Contaminants - UPBT substances
  • Contaminants - non UPBT substances
  • Contaminants - UPBT substances
  • Contaminants - non UPBT substances
  • Contaminants - UPBT substances
  • Contaminants - non UPBT substances
  • Contaminants - UPBT substances
  • Contaminants - non UPBT substances
  • Contaminants - UPBT substances
  • Contaminants - non UPBT substances
  • Contaminants - UPBT substances
  • Contaminants - non UPBT substances
  • Contaminants - UPBT substances
  • Contaminants - non UPBT substances
  • Contaminants - UPBT substances
  • Contaminants - non UPBT substances
  • Contaminants - UPBT substances
  • Contaminants - non UPBT substances
  • Contaminants - UPBT substances
  • Contaminants - non UPBT substances
  • Contaminants - UPBT substances
  • Contaminants - non UPBT substances
  • Contaminants - UPBT substances
  • Contaminants - non UPBT substances
  • Contaminants - UPBT substances
  • Contaminants - non UPBT substances
  • Contaminants - UPBT substances
  • Contaminants - non UPBT substances
  • Contaminants - UPBT substances
  • Contaminants - non UPBT substances
  • Contaminants - UPBT substances
  • Contaminants - non UPBT substances
  • Contaminants - UPBT substances
  • Contaminants - non UPBT substances
  • Contaminants - UPBT substances
  • Contaminants - non UPBT substances
  • Contaminants - UPBT substances
  • Contaminants - non UPBT substances
  • Contaminants - UPBT substances
  • Contaminants - non UPBT substances
  • Contaminants - UPBT substances
  • Contaminants - non UPBT substances
  • Contaminants - UPBT substances
  • Contaminants - non UPBT substances
  • Contaminants - UPBT substances
  • Contaminants - non UPBT substances
  • Contaminants - UPBT substances
  • Contaminants - non UPBT substances
  • Contaminants - UPBT substances
  • Contaminants - non UPBT substances
  • Contaminants - UPBT substances
  • Contaminants - non UPBT substances
  • Contaminants - UPBT substances
  • Contaminants - non UPBT substances
  • Contaminants - UPBT substances
  • Contaminants - non UPBT substances
  • Contaminants - UPBT substances
  • Contaminants - non UPBT substances
  • Contaminants - UPBT substances
  • Contaminants - non UPBT substances
  • Contaminants - UPBT substances
  • Contaminants - non UPBT substances
  • Contaminants - UPBT substances
  • Contaminants - non UPBT substances
  • Contaminants - UPBT substances
  • Contaminants - non UPBT substances
  • Contaminants - UPBT substances
  • Contaminants - non UPBT substances
  • Contaminants - UPBT substances
  • Contaminants - non UPBT substances
  • Contaminants - UPBT substances
  • Contaminants - non UPBT substances
  • Contaminants - UPBT substances
  • Contaminants - non UPBT substances
  • Contaminants - UPBT substances
  • Contaminants - non UPBT substances
  • Contaminants - UPBT substances
  • Contaminants - non UPBT substances
  • Contaminants - UPBT substances
  • Contaminants - non UPBT substances
  • Contaminants - UPBT substances
  • Contaminants - non UPBT substances
  • Contaminants - UPBT substances
  • Contaminants - non UPBT substances
  • Contaminants - in seafood
  • Contaminants - in seafood
  • Contaminants - in seafood
  • Contaminants - in seafood
  • Contaminants - in seafood
  • Contaminants - in seafood
  • Contaminants - in seafood
  • Contaminants - in seafood
  • Contaminants - in seafood
  • Contaminants - in seafood
GES components
  • D8C1 Contaminants in environment (8.1, 8.1.1)
  • D8C2 Adverse effects of contaminants (8.2, 8.2.1)
  • D9C1 Contaminants in seafood (9.1, 9.1.1)
  • D8C1 Contaminants in environment (8.1, 8.1.1)
  • D8C2 Adverse effects of contaminants (8.2, 8.2.1)
  • D9C1 Contaminants in seafood (9.1, 9.1.1)
  • D8C1 Contaminants in environment (8.1, 8.1.1)
  • D8C3 Significant acute pollution events (8.2.2)
  • D9C1 Contaminants in seafood (9.1, 9.1.1)
  • D8C1 Contaminants in environment (8.1, 8.1.1)
  • D8C3 Significant acute pollution events (8.2.2)
  • D9C1 Contaminants in seafood (9.1, 9.1.1)
  • D8C1 Contaminants in environment (8.1, 8.1.1)
  • D8C3 Significant acute pollution events (8.2.2)
  • D9C1 Contaminants in seafood (9.1, 9.1.1)
  • D8C1 Contaminants in environment (8.1, 8.1.1)
  • D8C3 Significant acute pollution events (8.2.2)
  • D9C1 Contaminants in seafood (9.1, 9.1.1)
  • D8C1 Contaminants in environment (8.1, 8.1.1)
  • D8C3 Significant acute pollution events (8.2.2)
  • D9C1 Contaminants in seafood (9.1, 9.1.1)
  • D8C1 Contaminants in environment (8.1, 8.1.1)
  • D8C3 Significant acute pollution events (8.2.2)
  • D9C1 Contaminants in seafood (9.1, 9.1.1)
  • D8C1 Contaminants in environment (8.1, 8.1.1)
  • D8C3 Significant acute pollution events (8.2.2)
  • D9C1 Contaminants in seafood (9.1, 9.1.1)
  • D8C1 Contaminants in environment (8.1, 8.1.1)
  • D8C3 Significant acute pollution events (8.2.2)
  • D9C1 Contaminants in seafood (9.1, 9.1.1)
  • D8C1 Contaminants in environment (8.1, 8.1.1)
  • D8C3 Significant acute pollution events (8.2.2)
  • D9C1 Contaminants in seafood (9.1, 9.1.1)
  • D8C1 Contaminants in environment (8.1, 8.1.1)
  • D8C3 Significant acute pollution events (8.2.2)
  • D9C1 Contaminants in seafood (9.1, 9.1.1)
  • D8C1 Contaminants in environment (8.1, 8.1.1)
  • D8C3 Significant acute pollution events (8.2.2)
  • D9C1 Contaminants in seafood (9.1, 9.1.1)
  • D8C1 Contaminants in environment (8.1, 8.1.1)
  • D8C3 Significant acute pollution events (8.2.2)
  • D9C1 Contaminants in seafood (9.1, 9.1.1)
  • D8C1 Contaminants in environment (8.1, 8.1.1)
  • D8C3 Significant acute pollution events (8.2.2)
  • D9C1 Contaminants in seafood (9.1, 9.1.1)
  • D8C1 Contaminants in environment (8.1, 8.1.1)
  • D8C3 Significant acute pollution events (8.2.2)
  • D9C1 Contaminants in seafood (9.1, 9.1.1)
  • D8C1 Contaminants in environment (8.1, 8.1.1)
  • D8C3 Significant acute pollution events (8.2.2)
  • D9C1 Contaminants in seafood (9.1, 9.1.1)
  • D8C1 Contaminants in environment (8.1, 8.1.1)
  • D8C3 Significant acute pollution events (8.2.2)
  • D9C1 Contaminants in seafood (9.1, 9.1.1)
  • D8C1 Contaminants in environment (8.1, 8.1.1)
  • D8C3 Significant acute pollution events (8.2.2)
  • D9C1 Contaminants in seafood (9.1, 9.1.1)
  • D8C1 Contaminants in environment (8.1, 8.1.1)
  • D8C3 Significant acute pollution events (8.2.2)
  • D9C1 Contaminants in seafood (9.1, 9.1.1)
  • D8C1 Contaminants in environment (8.1, 8.1.1)
  • D8C3 Significant acute pollution events (8.2.2)
  • D9C1 Contaminants in seafood (9.1, 9.1.1)
  • D8C1 Contaminants in environment (8.1, 8.1.1)
  • D8C3 Significant acute pollution events (8.2.2)
  • D9C1 Contaminants in seafood (9.1, 9.1.1)
  • D8C1 Contaminants in environment (8.1, 8.1.1)
  • D8C3 Significant acute pollution events (8.2.2)
  • D9C1 Contaminants in seafood (9.1, 9.1.1)
  • D8C1 Contaminants in environment (8.1, 8.1.1)
  • D8C3 Significant acute pollution events (8.2.2)
  • D9C1 Contaminants in seafood (9.1, 9.1.1)
  • D8C1 Contaminants in environment (8.1, 8.1.1)
  • D8C3 Significant acute pollution events (8.2.2)
  • D9C1 Contaminants in seafood (9.1, 9.1.1)
  • D8C1 Contaminants in environment (8.1, 8.1.1)
  • D8C3 Significant acute pollution events (8.2.2)
  • D9C1 Contaminants in seafood (9.1, 9.1.1)
  • D8C1 Contaminants in environment (8.1, 8.1.1)
  • D8C3 Significant acute pollution events (8.2.2)
  • D9C1 Contaminants in seafood (9.1, 9.1.1)
  • D8C1 Contaminants in environment (8.1, 8.1.1)
  • D8C3 Significant acute pollution events (8.2.2)
  • D9C1 Contaminants in seafood (9.1, 9.1.1)
  • D8C1 Contaminants in environment (8.1, 8.1.1)
  • D8C3 Significant acute pollution events (8.2.2)
  • D9C1 Contaminants in seafood (9.1, 9.1.1)
  • D8C1 Contaminants in environment (8.1, 8.1.1)
  • D8C3 Significant acute pollution events (8.2.2)
  • D9C1 Contaminants in seafood (9.1, 9.1.1)
  • D8C1 Contaminants in environment (8.1, 8.1.1)
  • D8C3 Significant acute pollution events (8.2.2)
  • D9C1 Contaminants in seafood (9.1, 9.1.1)
  • D8C1 Contaminants in environment (8.1, 8.1.1)
  • D8C3 Significant acute pollution events (8.2.2)
  • D9C1 Contaminants in seafood (9.1, 9.1.1)
  • D8C1 Contaminants in environment (8.1, 8.1.1)
  • D8C3 Significant acute pollution events (8.2.2)
  • D9C1 Contaminants in seafood (9.1, 9.1.1)
  • D8C1 Contaminants in environment (8.1, 8.1.1)
  • D8C3 Significant acute pollution events (8.2.2)
  • D9C1 Contaminants in seafood (9.1, 9.1.1)
  • D8C1 Contaminants in environment (8.1, 8.1.1)
  • D8C3 Significant acute pollution events (8.2.2)
  • D9C1 Contaminants in seafood (9.1, 9.1.1)
  • D8C1 Contaminants in environment (8.1, 8.1.1)
  • D8C3 Significant acute pollution events (8.2.2)
  • D9C1 Contaminants in seafood (9.1, 9.1.1)
  • D8C1 Contaminants in environment (8.1, 8.1.1)
  • D8C3 Significant acute pollution events (8.2.2)
  • D9C1 Contaminants in seafood (9.1, 9.1.1)
  • D8C1 Contaminants in environment (8.1, 8.1.1)
  • D8C3 Significant acute pollution events (8.2.2)
  • D9C1 Contaminants in seafood (9.1, 9.1.1)
  • D8C1 Contaminants in environment (8.1, 8.1.1)
  • D8C3 Significant acute pollution events (8.2.2)
  • D9C1 Contaminants in seafood (9.1, 9.1.1)
  • D8C1 Contaminants in environment (8.1, 8.1.1)
  • D8C3 Significant acute pollution events (8.2.2)
  • D9C1 Contaminants in seafood (9.1, 9.1.1)
  • D8C1 Contaminants in environment (8.1, 8.1.1)
  • D8C3 Significant acute pollution events (8.2.2)
  • D9C1 Contaminants in seafood (9.1, 9.1.1)
  • D8C1 Contaminants in environment (8.1, 8.1.1)
  • D8C3 Significant acute pollution events (8.2.2)
  • D9C1 Contaminants in seafood (9.1, 9.1.1)
  • D8C1 Contaminants in environment (8.1, 8.1.1)
  • D9C1 Contaminants in seafood (9.1, 9.1.1)
  • D8C1 Contaminants in environment (8.1, 8.1.1)
  • D9C1 Contaminants in seafood (9.1, 9.1.1)
  • D8C1 Contaminants in environment (8.1, 8.1.1)
  • D9C1 Contaminants in seafood (9.1, 9.1.1)
  • D8C1 Contaminants in environment (8.1, 8.1.1)
  • D9C1 Contaminants in seafood (9.1, 9.1.1)
  • D8C1 Contaminants in environment (8.1, 8.1.1)
  • D9C1 Contaminants in seafood (9.1, 9.1.1)
  • D8C1 Contaminants in environment (8.1, 8.1.1)
  • D9C1 Contaminants in seafood (9.1, 9.1.1)
  • D8C1 Contaminants in environment (8.1, 8.1.1)
  • D9C1 Contaminants in seafood (9.1, 9.1.1)
  • D8C1 Contaminants in environment (8.1, 8.1.1)
  • D9C1 Contaminants in seafood (9.1, 9.1.1)
  • D9C1 Contaminants in seafood (9.1, 9.1.1)
  • D9C1 Contaminants in seafood (9.1, 9.1.1)
  • D9C1 Contaminants in seafood (9.1, 9.1.1)
  • D9C1 Contaminants in seafood (9.1, 9.1.1)
  • D9C1 Contaminants in seafood (9.1, 9.1.1)
  • D9C1 Contaminants in seafood (9.1, 9.1.1)
  • D9C1 Contaminants in seafood (9.1, 9.1.1)
  • D9C1 Contaminants in seafood (9.1, 9.1.1)
  • D9C1 Contaminants in seafood (9.1, 9.1.1)
  • D9C1 Contaminants in seafood (9.1, 9.1.1)
Timescale
202707
202707
202407
202407
202407
202407
202407
202407
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202407
202407
202407
202707
202707
202707
202707
202707
202707
202707
202707
202407
202407
202407
202407
202407
202407
202407
202407
202407
202407
Update date
201807
201807
201807
201807
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201807
Update type
Same as 2012 definition
Same as 2012 definition
Same as 2012 definition
Same as 2012 definition
Same as 2012 definition
Same as 2012 definition
Same as 2012 definition
Same as 2012 definition
Same as 2012 definition
Same as 2012 definition
Same as 2012 definition
Same as 2012 definition
Same as 2012 definition
Same as 2012 definition
Same as 2012 definition
Same as 2012 definition
Same as 2012 definition
Same as 2012 definition
Same as 2012 definition
Same as 2012 definition
Same as 2012 definition
Same as 2012 definition
Same as 2012 definition
Same as 2012 definition
Same as 2012 definition
Same as 2012 definition
Same as 2012 definition
Same as 2012 definition
Same as 2012 definition
Same as 2012 definition
Same as 2012 definition
Same as 2012 definition
Same as 2012 definition
Same as 2012 definition
Same as 2012 definition
Same as 2012 definition
Same as 2012 definition
Same as 2012 definition
Same as 2012 definition
Same as 2012 definition
Same as 2012 definition
Same as 2012 definition
Same as 2012 definition
Same as 2012 definition
Same as 2012 definition
Same as 2012 definition
Same as 2012 definition
Same as 2012 definition
Same as 2012 definition
Same as 2012 definition
Same as 2012 definition
Same as 2012 definition
Same as 2012 definition
Same as 2012 definition
Same as 2012 definition
Same as 2012 definition
Same as 2012 definition
Same as 2012 definition
Same as 2012 definition
Same as 2012 definition
Marine reporting unit
  • ANS-NL-CW-1
  • ANS-NL-CW-1
  • ANS-NL-MS-1
  • ANS-NL-MS-1
  • ANS-NL-MS-1
  • ANS-NL-MS-1
  • ANS-NL-MS-1
  • ANS-NL-MS-1
  • ANS-NL-MS-1
  • ANS-NL-MS-1
  • ANS-NL-MS-1
  • ANS-NL-MS-1
  • ANS-NL-MS-1
  • ANS-NL-MS-1
  • ANS-NL-MS-1
  • ANS-NL-MS-1
  • ANS-NL-MS-1
  • ANS-NL-MS-1
  • ANS-NL-MS-1
  • ANS-NL-MS-1
  • ANS-NL-MS-1
  • ANS-NL-MS-1
  • ANS-NL-MS-1
  • ANS-NL-MS-1
  • ANS-NL-MS-1
  • ANS-NL-MS-1
  • ANS-NL-MS-1
  • ANS-NL-MS-1
  • ANS-NL-MS-1
  • ANS-NL-MS-1
  • ANS-NL-MS-1
  • ANS-NL-MS-1
  • ANS-NL-MS-1
  • ANS-NL-MS-1
  • ANS-NL-MS-1
  • ANS-NL-MS-1
  • ANS-NL-MS-1
  • ANS-NL-MS-1
  • ANS-NL-MS-1
  • ANS-NL-MS-1
  • ANS-NL-MS-1
  • ANS-NL-MS-1
  • ANS-NL-MS-1
  • ANS-NL-MS-1
  • ANS-NL-MS-1
  • ANS-NL-MS-1
  • ANS-NL-MS-1
  • ANS-NL-MS-1
  • ANS-NL-MS-1
  • ANS-NL-MS-1
  • ANS-NL-MS-1
  • ANS-NL-MS-1
  • ANS-NL-MS-1
  • ANS-NL-MS-1
  • ANS-NL-MS-1
  • ANS-NL-MS-1
  • ANS-NL-MS-1
  • ANS-NL-MS-1
  • ANS-NL-MS-1
  • ANS-NL-MS-1
Element
WFD UPBT substances
WFD non UPBT substances
Anthracene
BDE 100 (2,2’,4,4’,6-pentabromodiphenyl ether)
BDE 153 (2,2’,4,4’,5,5’-hexabromodiphenyl ether)
BDE 153 (2,2’,4,4’,5,5’-hexabromodiphenyl ether)
BDE 28 (2,4,4-tribromodiphenyl ether)
BDE 28 (2,4,4-tribromodiphenyl ether)
BDE 47 (2,2’,4,4’-tetrabromodiphenyl ether)
BDE 47 (2,2’,4,4’-tetrabromodiphenyl ether)
BDE 99 (2,2’,4,4’,5-pentabromodiphenyl ether)
BDE 99 (2,2’,4,4’,5-pentabromodiphenyl ether)
Benz(a)anthracene
Benzo(a)pyrene
Benzo(g,h,i)perylene
Cadmium and its compounds
Cadmium and its compounds
Chrysene
Fluoranthene
Indeno(1,2,3,-cd)pyrene
Lead and its compounds
Lead and its compounds
Mercury and its compounds
Mercury and its compounds
Naphthalene
PCB 101 (2,2’,4,5,5’-pentachlorobiphenyl)
PCB 101 (2,2’,4,5,5’-pentachlorobiphenyl)
PCB 118 (2,3’,4,4’,5-pentachlorobiphenyl)
PCB 118 (2,3’,4,4’,5-pentachlorobiphenyl)
PCB 138 (2,2’,3,4,4’,5’-hexachlorobiphenyl)
PCB 138 (2,2’,3,4,4’,5’-hexachlorobiphenyl)
PCB 153 (2,2’,4,4’,5,5’-hexachlorobiphenyl)
PCB 153 (2,2’,4,4’,5,5’-hexachlorobiphenyl)
PCB 180 (2,2’,3,4,4’,5,5’-heptachlorobiphenyl)
PCB 180 (2,2’,3,4,4’,5,5’-heptachlorobiphenyl)
PCB 28 (2,4,4’-trichlorobiphenyl)
PCB 28 (2,4,4’-trichlorobiphenyl)
PCB 52 (2,2’,5,5’-tetrachlorobiphenyl)
PCB 52 (2,2’,5,5’-tetrachlorobiphenyl)
Phenanthrene
Pyrene
oil spills
Cadmium and its compounds
Cadmium and its compounds
Lead and its compounds
Lead and its compounds
Mercury and its compounds
Mercury and its compounds
WFD UPBT substances
WFD non UPBT substances
Benzo(a)pyrene
Cadmium and its compounds
Cadmium and its compounds
Dioxine TEQ
Lead and its compounds
Lead and its compounds
Mercury and its compounds
Non-dioxin like PCB (sum of 6 PCB: 28, 52, 101, 13
Som-TEQ
Sum of benz (a) pyrene, benz (a) anthracene, benzo
Element 2
mosselen en garnalen
alle vis
mosselen en garnalen
alle vis
Parameter
Concentration in water
Concentration in water
Concentration in sediment
Concentration in biota
Concentration in biota
Concentration in sediment
Concentration in biota
Concentration in sediment
Concentration in biota
Concentration in sediment
Concentration in biota
Concentration in sediment
Concentration in sediment
Concentration in sediment
Concentration in sediment
Concentration in biota
Concentration in sediment
Concentration in sediment
Concentration in sediment
Concentration in sediment
Concentration in biota
Concentration in sediment
Concentration in biota
Concentration in sediment
Concentration in sediment
Concentration in biota
Concentration in sediment
Concentration in biota
Concentration in sediment
Concentration in biota
Concentration in sediment
Concentration in biota
Concentration in sediment
Concentration in biota
Concentration in sediment
Concentration in biota
Concentration in sediment
Concentration in biota
Concentration in sediment
Concentration in sediment
Concentration in sediment
Other
Concentration in biota
Concentration in sediment
Concentration in biota
Concentration in sediment
Concentration in biota
Concentration in sediment
Concentration in water
Concentration in water
Concentration in biota
Concentration in biota
CONC-B-MU
Concentration in biota
Concentration in biota
CONC-B-MU
Concentration in biota
Concentration in biota
Concentration in biota
Concentration in biota
Parameter - other
Ratio count flighthours
Target value
-1.0
-1.0
-1.0
-1.0
-1.0
-1.0
-1.0
-1.0
-1.0
-1.0
-1.0
-1.0
-1.0
-1.0
-1.0
-1.0
-1.0
-1.0
-1.0
-1.0
-1.0
-1.0
-1.0
-1.0
-1.0
-1.0
-1.0
-1.0
-1.0
-1.0
-1.0
-1.0
-1.0
-1.0
-1.0
-1.0
-1.0
-1.0
-1.0
-1.0
-1.0
-1.0
-1.0
-1.0
-1.0
6.0
0.05
0.05
3.5
0.3
0.3
0.5
75.0
6.5
35.0
Value achieved - upper
-1.0
-1.0
-1.0
-1.0
1.0
-1.0
-1.0
-1.0
-1.0
-1.0
-1.0
-1.0
-1.0
-1.0
-1.0
-1.0
-1.0
-1.0
-1.0
-1.0
-1.0
-1.0
-1.0
1.0
-1.0
-1.0
-1.0
-1.0
0.72
0.05
0.0005
0.78
0.2
0.05
0.2
45.0
4.5
5.0
Value achieved - lower
Value unit
microgram per litre
microgram per litre
Other
Other
Other
Other
Other
Other
Other
Other
Other
Other
Other
Other
Other
Other
Other
Other
Other
Other
Other
Other
Other
Other
Other
Other
Other
Other
Other
Other
Other
Other
Other
Other
Other
Other
Other
Other
Other
Other
Other
Other
Other
Other
Other
Other
Other
Other
microgram per litre
microgram per litre
Other
milligram per kilogram
milligram per kilogram
Other
milligram per kilogram
milligram per kilogram
milligram per kilogram
Other
Other
Other
Value unit - other
Trend indicator
Trend indicator
Trend indicator
Trend indicator
Trend indicator
Trend indicator
Trend indicator
Trend indicator
Trend indicator
Trend indicator
Trend indicator
Trend indicator
Trend indicator
Trend indicator
Trend indicator
Trend indicator
Trend indicator
Trend indicator
Trend indicator
Trend indicator
Trend indicator
Trend indicator
Trend indicator
Trend indicator
Trend indicator
Trend indicator
Trend indicator
Trend indicator
Trend indicator
Trend indicator
Trend indicator
Trend indicator
Trend indicator
Trend indicator
Trend indicator
Trend indicator
Trend indicator
Trend indicator
Trend indicator
Trend indicator
Trend indicator
Trend indicator
Trend indicator
Trend indicator
Trend indicator
Trend indicator
ng/g
pg TEQ / g product
ng/g
pg TEQ / g product
ng/g
Target status
Target not yet achieved
Target not yet achieved
Target not yet achieved
Target achieved
Target not yet achieved
Target not yet achieved
Target achieved
Target not yet achieved
Target achieved
Target not yet achieved
Target achieved
Target not yet achieved
Target not yet achieved
Target not yet achieved
Target not yet achieved
Target not yet achieved
Target achieved
Target not yet achieved
Target not yet achieved
Target not yet achieved
Target achieved
Target achieved
Target not yet achieved
Target achieved
Target not yet achieved
Target achieved
Target achieved
Target achieved
Target achieved
Target achieved
Target achieved
Target achieved
Target not yet achieved
Target achieved
Target achieved
Target achieved
Target achieved
Target achieved
Target achieved
Target not yet achieved
Target not yet achieved
Target achieved
Target not yet achieved
Target achieved
Target achieved
Target achieved
Target not yet achieved
Target achieved
Target achieved
Target not yet achieved
Target achieved
Target achieved
Target achieved
Target achieved
Target achieved
Target achieved
Target achieved
Target achieved
Target achieved
Target achieved
Assessment period
2012-2014
2012-2014
1995-2015
2009-2015
2009-2015
2010-2015
2009-2015
2010-2015
2009-2015
2010-2015
2009-2015
2010-2015
1995-2015
1995-2015
1995-2015
1995-2015
1995-2015
1995-2015
1995-2015
1995-2015
1995-2015
1995-2015
1995-2015
1995-2015
1995-2015
1995-2015
1995-2015
1995-2015
1995-2015
1995-2015
1995-2015
1995-2015
2010-2015
1995-2015
1995-2015
1995-2015
1995-2015
1995-2015
1995-2015
1995-2015
1995-2015
1986-2016
1995-2015
1995-2015
1995-2015
1995-2015
1995-2015
1995-2015
2012-2014
2012-2014
2016-2016
2016-2016
2016-2016
2016-2016
2016-2016
2016-2016
2016-2016
2016-2016
2016-2016
2016-2016
Target assessment description
The WFD targets are projected to be achieved. Therefore, the environmental risks of undesirable pollution effects on the marine environment continue to fall, due to existing policies The environmental risks will be even small between 2020 and 2027 and beyond. Good environmental status for most of the substances is expected to be within reach in the years after 2020. However, D8 dangerous substances have been reported with an Article 14 exception. The MSFD programme of measures provides the maximum possible commitment to achieving good environmental status for the descriptor dangerous substances, both for measures on land (WFD implementation) and for measures at sea. No technical measures may be taken to eliminate the presence of dangerous substances in the Dutch part of the North Sea. Natural conditions do not allow for a timely improvement of the situation of this part of the North Sea.
The WFD targets are projected to be achieved. Therefore, the environmental risks of undesirable pollution effects on the marine environment continue to fall, due to existing policies The environmental risks will be even small between 2020 and 2027 and beyond. Good environmental status for most of the substances is expected to be within reach in the years after 2020. However, D8 dangerous substances have been reported with an Article 14 exception. The MSFD programme of measures provides the maximum possible commitment to achieving good environmental status for the descriptor dangerous substances, both for measures on land (WFD implementation) and for measures at sea. No technical measures may be taken to eliminate the presence of dangerous substances in the Dutch part of the North Sea. Natural conditions do not allow for a timely improvement of the situation of this part of the North Sea.
The WFD targets are projected to be achieved. Therefore, the environmental risks of undesirable pollution effects on the marine environment continue to fall, due to existing policies The environmental risks will be even small between 2020 and 2027 and beyond. Good environmental status for most of the substances is expected to be within reach in the years after 2020. However, D8 dangerous substances have been reported with an Article 14 exception. The MSFD programme of measures provides the maximum possible commitment to achieving good environmental status for the descriptor dangerous substances, both for measures on land (WFD implementation) and for measures at sea. No technical measures may be taken to eliminate the presence of dangerous substances in the Dutch part of the North Sea. Natural conditions do not allow for a timely improvement of the situation of this part of the North Sea.
Polychlorinated biphenyls (PCBs) were banned in many countries in the mid-1980s. Since then, concentrations of PCBs in sediment have decreased in most OSPAR sub-regions - although there are still problems at the local level. With the exception of the most toxic congener (CB118), the concentrations in sediment are below the level at which they can pose an unacceptable risk to the environment.
The WFD targets are projected to be achieved. Therefore, the environmental risks of undesirable pollution effects on the marine environment continue to fall, due to existing policies The environmental risks will be even small between 2020 and 2027 and beyond. Good environmental status for most of the substances is expected to be within reach in the years after 2020. However, D8 dangerous substances have been reported with an Article 14 exception. The MSFD programme of measures provides the maximum possible commitment to achieving good environmental status for the descriptor dangerous substances, both for measures on land (WFD implementation) and for measures at sea. No technical measures may be taken to eliminate the presence of dangerous substances in the Dutch part of the North Sea. Natural conditions do not allow for a timely improvement of the situation of this part of the North Sea.
Polychlorinated biphenyls (PCBs) were banned in many countries in the mid-1980s. Since then, concentrations of PCBs in sediment have decreased in most OSPAR sub-regions - although there are still problems at the local level. With the exception of the most toxic congener (CB118), the concentrations in sediment are below the level at which they can pose an unacceptable risk to the environment.
The WFD targets are projected to be achieved. Therefore, the environmental risks of undesirable pollution effects on the marine environment continue to fall, due to existing policies The environmental risks will be even small between 2020 and 2027 and beyond. Good environmental status for most of the substances is expected to be within reach in the years after 2020. However, D8 dangerous substances have been reported with an Article 14 exception. The MSFD programme of measures provides the maximum possible commitment to achieving good environmental status for the descriptor dangerous substances, both for measures on land (WFD implementation) and for measures at sea. No technical measures may be taken to eliminate the presence of dangerous substances in the Dutch part of the North Sea. Natural conditions do not allow for a timely improvement of the situation of this part of the North Sea.
Polychlorinated biphenyls (PCBs) were banned in many countries in the mid-1980s. Since then, concentrations of PCBs in sediment have decreased in most OSPAR sub-regions - although there are still problems at the local level. With the exception of the most toxic congener (CB118), the concentrations in sediment are below the level at which they can pose an unacceptable risk to the environment.
The WFD targets are projected to be achieved. Therefore, the environmental risks of undesirable pollution effects on the marine environment continue to fall, due to existing policies The environmental risks will be even small between 2020 and 2027 and beyond. Good environmental status for most of the substances is expected to be within reach in the years after 2020. However, D8 dangerous substances have been reported with an Article 14 exception. The MSFD programme of measures provides the maximum possible commitment to achieving good environmental status for the descriptor dangerous substances, both for measures on land (WFD implementation) and for measures at sea. No technical measures may be taken to eliminate the presence of dangerous substances in the Dutch part of the North Sea. Natural conditions do not allow for a timely improvement of the situation of this part of the North Sea.
The WFD targets are projected to be achieved. Therefore, the environmental risks of undesirable pollution effects on the marine environment continue to fall, due to existing policies The environmental risks will be even small between 2020 and 2027 and beyond. Good environmental status for most of the substances is expected to be within reach in the years after 2020. However, D8 dangerous substances have been reported with an Article 14 exception. The MSFD programme of measures provides the maximum possible commitment to achieving good environmental status for the descriptor dangerous substances, both for measures on land (WFD implementation) and for measures at sea. No technical measures may be taken to eliminate the presence of dangerous substances in the Dutch part of the North Sea. Natural conditions do not allow for a timely improvement of the situation of this part of the North Sea.
Polychlorinated biphenyls (PCBs) were banned in many countries in the mid-1980s. Since then, concentrations of PCBs in sediment have decreased in most OSPAR sub-regions - although there are still problems at the local level. With the exception of the most toxic congener (CB118), the concentrations in sediment are below the level at which they can pose an unacceptable risk to the environment.
The WFD targets are projected to be achieved. Therefore, the environmental risks of undesirable pollution effects on the marine environment continue to fall, due to existing policies The environmental risks will be even small between 2020 and 2027 and beyond. Good environmental status for most of the substances is expected to be within reach in the years after 2020. However, D8 dangerous substances have been reported with an Article 14 exception. The MSFD programme of measures provides the maximum possible commitment to achieving good environmental status for the descriptor dangerous substances, both for measures on land (WFD implementation) and for measures at sea. No technical measures may be taken to eliminate the presence of dangerous substances in the Dutch part of the North Sea. Natural conditions do not allow for a timely improvement of the situation of this part of the North Sea.
Polychlorinated biphenyls (PCBs) were banned in many countries in the mid-1980s. Since then, concentrations of PCBs in sediment have decreased in most OSPAR sub-regions - although there are still problems at the local level. With the exception of the most toxic congener (CB118), the concentrations in sediment are below the level at which they can pose an unacceptable risk to the environment.
The WFD targets are projected to be achieved. Therefore, the environmental risks of undesirable pollution effects on the marine environment continue to fall, due to existing policies The environmental risks will be even small between 2020 and 2027 and beyond. Good environmental status for most of the substances is expected to be within reach in the years after 2020. However, D8 dangerous substances have been reported with an Article 14 exception. The MSFD programme of measures provides the maximum possible commitment to achieving good environmental status for the descriptor dangerous substances, both for measures on land (WFD implementation) and for measures at sea. No technical measures may be taken to eliminate the presence of dangerous substances in the Dutch part of the North Sea. Natural conditions do not allow for a timely improvement of the situation of this part of the North Sea.
Polychlorinated biphenyls (PCBs) were banned in many countries in the mid-1980s. Since then, concentrations of PCBs in sediment have decreased in most OSPAR sub-regions - although there are still problems at the local level. With the exception of the most toxic congener (CB118), the concentrations in sediment are below the level at which they can pose an unacceptable risk to the environment.
The WFD targets are projected to be achieved. Therefore, the environmental risks of undesirable pollution effects on the marine environment continue to fall, due to existing policies The environmental risks will be even small between 2020 and 2027 and beyond. Good environmental status for most of the substances is expected to be within reach in the years after 2020. However, D8 dangerous substances have been reported with an Article 14 exception. The MSFD programme of measures provides the maximum possible commitment to achieving good environmental status for the descriptor dangerous substances, both for measures on land (WFD implementation) and for measures at sea. No technical measures may be taken to eliminate the presence of dangerous substances in the Dutch part of the North Sea. Natural conditions do not allow for a timely improvement of the situation of this part of the North Sea.
The WFD targets are projected to be achieved. Therefore, the environmental risks of undesirable pollution effects on the marine environment continue to fall, due to existing policies The environmental risks will be even small between 2020 and 2027 and beyond. Good environmental status for most of the substances is expected to be within reach in the years after 2020. However, D8 dangerous substances have been reported with an Article 14 exception. The MSFD programme of measures provides the maximum possible commitment to achieving good environmental status for the descriptor dangerous substances, both for measures on land (WFD implementation) and for measures at sea. No technical measures may be taken to eliminate the presence of dangerous substances in the Dutch part of the North Sea. Natural conditions do not allow for a timely improvement of the situation of this part of the North Sea.
Levels must be below the maximum levels for all substances.
Levels must be below the maximum levels for all substances.
Levels must be below the maximum levels for all substances.
Levels must be below the maximum levels for all substances.
Levels must be below the maximum levels for all substances.
Levels must be below the maximum levels for all substances.
Levels must be below the maximum levels for all substances.
Levels must be below the maximum levels for all substances.
Levels must be below the maximum levels for all substances.
Levels must be below the maximum levels for all substances.
Related indicator
Related measures
  • ANSNL-M012
  • ANSNL-M017
  • ANSNL-M018
  • ANSNL-M019
  • ANSNL-M021
  • ANSNL-M038
  • ANSNL-M012
  • ANSNL-M017
  • ANSNL-M018
  • ANSNL-M019
  • ANSNL-M021
  • ANSNL-M038
  • ANSNL-M021
  • ANSNL-M022
  • ANSNL-M021
  • ANSNL-M022
  • ANSNL-M021
  • ANSNL-M022
  • ANSNL-M021
  • ANSNL-M022
  • ANSNL-M021
  • ANSNL-M022
  • ANSNL-M021
  • ANSNL-M022
  • ANSNL-M021
  • ANSNL-M022
  • ANSNL-M021
  • ANSNL-M022
  • ANSNL-M021
  • ANSNL-M022
  • ANSNL-M021
  • ANSNL-M022
  • ANSNL-M021
  • ANSNL-M022
  • ANSNL-M021
  • ANSNL-M022
  • ANSNL-M021
  • ANSNL-M022
  • ANSNL-M021
  • ANSNL-M022
  • ANSNL-M021
  • ANSNL-M022
  • ANSNL-M021
  • ANSNL-M022
  • ANSNL-M021
  • ANSNL-M022
  • ANSNL-M021
  • ANSNL-M022
  • ANSNL-M021
  • ANSNL-M022
  • ANSNL-M021
  • ANSNL-M022
  • ANSNL-M021
  • ANSNL-M022
  • ANSNL-M021
  • ANSNL-M022
  • ANSNL-M021
  • ANSNL-M022
  • ANSNL-M021
  • ANSNL-M022
  • ANSNL-M021
  • ANSNL-M022
  • ANSNL-M021
  • ANSNL-M022
  • ANSNL-M021
  • ANSNL-M022
  • ANSNL-M021
  • ANSNL-M022
  • ANSNL-M021
  • ANSNL-M022
  • ANSNL-M021
  • ANSNL-M022
  • ANSNL-M021
  • ANSNL-M022
  • ANSNL-M021
  • ANSNL-M022
  • ANSNL-M021
  • ANSNL-M022
  • ANSNL-M021
  • ANSNL-M022
  • ANSNL-M021
  • ANSNL-M022
  • ANSNL-M021
  • ANSNL-M022
  • ANSNL-M021
  • ANSNL-M022
  • ANSNL-M021
  • ANSNL-M022
  • ANSNL-M021
  • ANSNL-M022
  • ANSNL-M021
  • ANSNL-M022
  • NotApplicable
  • NotApplicable
  • NotApplicable
  • NotApplicable
  • NotApplicable
  • NotApplicable
  • NotApplicable
  • NotApplicable
  • ANSNL-M023
  • ANSNL-M023
  • ANSNL-M023
  • ANSNL-M023
  • ANSNL-M023
  • ANSNL-M023
  • ANSNL-M023
  • ANSNL-M023
  • ANSNL-M023
  • ANSNL-M023