MS/Art10/2018/D8/Netherlands/NE Atlantic: Greater North Sea

Member State report / Art10 / 2018 / D8 / 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	D8 Contaminants
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

Simplified table

Target code	ANSNL-D8T1	ANSNL-D8T1	ANSNL-D8T2	ANSNL-D8T2	ANSNL-D8T2	ANSNL-D8T2	ANSNL-D8T2	ANSNL-D8T2	ANSNL-D8T2	ANSNL-D8T2	ANSNL-D8T2	ANSNL-D8T2	ANSNL-D8T2	ANSNL-D8T2	ANSNL-D8T2	ANSNL-D8T2	ANSNL-D8T2	ANSNL-D8T2	ANSNL-D8T2	ANSNL-D8T2	ANSNL-D8T2	ANSNL-D8T2	ANSNL-D8T2	ANSNL-D8T2	ANSNL-D8T2	ANSNL-D8T2	ANSNL-D8T2	ANSNL-D8T2	ANSNL-D8T2	ANSNL-D8T2	ANSNL-D8T2	ANSNL-D8T2	ANSNL-D8T2	ANSNL-D8T2	ANSNL-D8T2	ANSNL-D8T2	ANSNL-D8T2	ANSNL-D8T2	ANSNL-D8T2	ANSNL-D8T2	ANSNL-D8T2	ANSNL-D8T2	ANSNL-D8T2	ANSNL-D8T2	ANSNL-D8T2	ANSNL-D8T2	ANSNL-D8T2	ANSNL-D8T2	ANSNL-D8T2	ANSNL-D8T2	ANSNL-D8T2	ANSNL-D8T2	ANSNL-D8T2	ANSNL-D8T2	ANSNL-D8T3	ANSNL-D8T3	ANSNL-D8T3	ANSNL-D8T3	ANSNL-D8T3	ANSNL-D8T3	ANSNL-D8T3	ANSNL-D8T3	ANSNL-D8T3	ANSNL-D8T3	ANSNL-D8T3	ANSNL-D8T3	ANSNL-D8T3	ANSNL-D8T3	ANSNL-D8T3	ANSNL-D8T3	ANSNL-D8T3	ANSNL-D8T3	ANSNL-D8T3	ANSNL-D8T3	ANSNL-D8T4	ANSNL-D8T4	ANSNL-D8T4	ANSNL-D8T4	ANSNL-D8T4	ANSNL-D8T4	ANSNL-D8T4	ANSNL-D8T4	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
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.	Offshore: Where established meet the OSPAR Environmental Assessment Criteria and / or Background Assessment Criteria. Where these standards have not yet been formulated, the aim is a downward trend in the concentrations of pollutants or their pollution effects.	Offshore: Where established meet the OSPAR Environmental Assessment Criteria and / or Background Assessment Criteria. Where these standards have not yet been formulated, the aim is a downward trend in the concentrations of pollutants or their pollution effects.	Offshore: Where established meet the OSPAR Environmental Assessment Criteria and / or Background Assessment Criteria. Where these standards have not yet been formulated, the aim is a downward trend in the concentrations of pollutants or their pollution effects.	Offshore: Where established meet the OSPAR Environmental Assessment Criteria and / or Background Assessment Criteria. Where these standards have not yet been formulated, the aim is a downward trend in the concentrations of pollutants or their pollution effects.	Offshore: Where established meet the OSPAR Environmental Assessment Criteria and / or Background Assessment Criteria. Where these standards have not yet been formulated, the aim is a downward trend in the concentrations of pollutants or their pollution effects.	Offshore: Where established meet the OSPAR Environmental Assessment Criteria and / or Background Assessment Criteria. Where these standards have not yet been formulated, the aim is a downward trend in the concentrations of pollutants or their pollution effects.	Offshore: Where established meet the OSPAR Environmental Assessment Criteria and / or Background Assessment Criteria. Where these standards have not yet been formulated, the aim is a downward trend in the concentrations of pollutants or their pollution effects.	Offshore: Where established meet the OSPAR Environmental Assessment Criteria and / or Background Assessment Criteria. Where these standards have not yet been formulated, the aim is a downward trend in the concentrations of pollutants or their pollution effects.	Offshore: Where established meet the OSPAR Environmental Assessment Criteria and / or Background Assessment Criteria. Where these standards have not yet been formulated, the aim is a downward trend in the concentrations of pollutants or their pollution effects.	Offshore: Where established meet the OSPAR Environmental Assessment Criteria and / or Background Assessment Criteria. Where these standards have not yet been formulated, the aim is a downward trend in the concentrations of pollutants or their pollution effects.	Offshore: Where established meet the OSPAR Environmental Assessment Criteria and / or Background Assessment Criteria. Where these standards have not yet been formulated, the aim is a downward trend in the concentrations of pollutants or their pollution effects.	Offshore: Where established meet the OSPAR Environmental Assessment Criteria and / or Background Assessment Criteria. Where these standards have not yet been formulated, the aim is a downward trend in the concentrations of pollutants or their pollution effects.	Offshore: Where established meet the OSPAR Environmental Assessment Criteria and / or Background Assessment Criteria. Where these standards have not yet been formulated, the aim is a downward trend in the concentrations of pollutants or their pollution effects.	Offshore: Where established meet the OSPAR Environmental Assessment Criteria and / or Background Assessment Criteria. Where these standards have not yet been formulated, the aim is a downward trend in the concentrations of pollutants or their pollution effects.	Offshore: Where established meet the OSPAR Environmental Assessment Criteria and / or Background Assessment Criteria. Where these standards have not yet been formulated, the aim is a downward trend in the concentrations of pollutants or their pollution effects.	Offshore: Where established meet the OSPAR Environmental Assessment Criteria and / or Background Assessment Criteria. Where these standards have not yet been formulated, the aim is a downward trend in the concentrations of pollutants or their pollution effects.	Offshore: Where established meet the OSPAR Environmental Assessment Criteria and / or Background Assessment Criteria. Where these standards have not yet been formulated, the aim is a downward trend in the concentrations of pollutants or their pollution effects.	Offshore: Where established meet the OSPAR Environmental Assessment Criteria and / or Background Assessment Criteria. Where these standards have not yet been formulated, the aim is a downward trend in the concentrations of pollutants or their pollution effects.	Offshore: Where established meet the OSPAR Environmental Assessment Criteria and / or Background Assessment Criteria. Where these standards have not yet been formulated, the aim is a downward trend in the concentrations of pollutants or their pollution effects.	Offshore: Where established meet the OSPAR Environmental Assessment Criteria and / or Background Assessment Criteria. Where these standards have not yet been formulated, the aim is a downward trend in the concentrations of pollutants or their pollution effects.	Offshore: Where established meet the OSPAR Environmental Assessment Criteria and / or Background Assessment Criteria. Where these standards have not yet been formulated, the aim is a downward trend in the concentrations of pollutants or their pollution effects.	Offshore: Where established meet the OSPAR Environmental Assessment Criteria and / or Background Assessment Criteria. Where these standards have not yet been formulated, the aim is a downward trend in the concentrations of pollutants or their pollution effects.	Offshore: Where established meet the OSPAR Environmental Assessment Criteria and / or Background Assessment Criteria. Where these standards have not yet been formulated, the aim is a downward trend in the concentrations of pollutants or their pollution effects.	Offshore: Where established meet the OSPAR Environmental Assessment Criteria and / or Background Assessment Criteria. Where these standards have not yet been formulated, the aim is a downward trend in the concentrations of pollutants or their pollution effects.	Offshore: Where established meet the OSPAR Environmental Assessment Criteria and / or Background Assessment Criteria. Where these standards have not yet been formulated, the aim is a downward trend in the concentrations of pollutants or their pollution effects.	Offshore: Where established meet the OSPAR Environmental Assessment Criteria and / or Background Assessment Criteria. Where these standards have not yet been formulated, the aim is a downward trend in the concentrations of pollutants or their pollution effects.	Offshore: Where established meet the OSPAR Environmental Assessment Criteria and / or Background Assessment Criteria. Where these standards have not yet been formulated, the aim is a downward trend in the concentrations of pollutants or their pollution effects.	Offshore: Where established meet the OSPAR Environmental Assessment Criteria and / or Background Assessment Criteria. Where these standards have not yet been formulated, the aim is a downward trend in the concentrations of pollutants or their pollution effects.	Offshore: Where established meet the OSPAR Environmental Assessment Criteria and / or Background Assessment Criteria. Where these standards have not yet been formulated, the aim is a downward trend in the concentrations of pollutants or their pollution effects.	Offshore: Where established meet the OSPAR Environmental Assessment Criteria and / or Background Assessment Criteria. Where these standards have not yet been formulated, the aim is a downward trend in the concentrations of pollutants or their pollution effects.	Offshore: Where established meet the OSPAR Environmental Assessment Criteria and / or Background Assessment Criteria. Where these standards have not yet been formulated, the aim is a downward trend in the concentrations of pollutants or their pollution effects.	Offshore: Where established meet the OSPAR Environmental Assessment Criteria and / or Background Assessment Criteria. Where these standards have not yet been formulated, the aim is a downward trend in the concentrations of pollutants or their pollution effects.	Offshore: Where established meet the OSPAR Environmental Assessment Criteria and / or Background Assessment Criteria. Where these standards have not yet been formulated, the aim is a downward trend in the concentrations of pollutants or their pollution effects.	Offshore: Where established meet the OSPAR Environmental Assessment Criteria and / or Background Assessment Criteria. Where these standards have not yet been formulated, the aim is a downward trend in the concentrations of pollutants or their pollution effects.	Offshore: Where established meet the OSPAR Environmental Assessment Criteria and / or Background Assessment Criteria. Where these standards have not yet been formulated, the aim is a downward trend in the concentrations of pollutants or their pollution effects.	Offshore: Where established meet the OSPAR Environmental Assessment Criteria and / or Background Assessment Criteria. Where these standards have not yet been formulated, the aim is a downward trend in the concentrations of pollutants or their pollution effects.	Offshore: Where established meet the OSPAR Environmental Assessment Criteria and / or Background Assessment Criteria. Where these standards have not yet been formulated, the aim is a downward trend in the concentrations of pollutants or their pollution effects.	Offshore: Where established meet the OSPAR Environmental Assessment Criteria and / or Background Assessment Criteria. Where these standards have not yet been formulated, the aim is a downward trend in the concentrations of pollutants or their pollution effects.	Offshore: Where established meet the OSPAR Environmental Assessment Criteria and / or Background Assessment Criteria. Where these standards have not yet been formulated, the aim is a downward trend in the concentrations of pollutants or their pollution effects.	Offshore: Where established meet the OSPAR Environmental Assessment Criteria and / or Background Assessment Criteria. Where these standards have not yet been formulated, the aim is a downward trend in the concentrations of pollutants or their pollution effects.	Offshore: Where established meet the OSPAR Environmental Assessment Criteria and / or Background Assessment Criteria. Where these standards have not yet been formulated, the aim is a downward trend in the concentrations of pollutants or their pollution effects.	Offshore: Where established meet the OSPAR Environmental Assessment Criteria and / or Background Assessment Criteria. Where these standards have not yet been formulated, the aim is a downward trend in the concentrations of pollutants or their pollution effects.	Offshore: Where established meet the OSPAR Environmental Assessment Criteria and / or Background Assessment Criteria. Where these standards have not yet been formulated, the aim is a downward trend in the concentrations of pollutants or their pollution effects.	Offshore: Where established meet the OSPAR Environmental Assessment Criteria and / or Background Assessment Criteria. Where these standards have not yet been formulated, the aim is a downward trend in the concentrations of pollutants or their pollution effects.	Offshore: Where established meet the OSPAR Environmental Assessment Criteria and / or Background Assessment Criteria. Where these standards have not yet been formulated, the aim is a downward trend in the concentrations of pollutants or their pollution effects.	Offshore: Where established meet the OSPAR Environmental Assessment Criteria and / or Background Assessment Criteria. Where these standards have not yet been formulated, the aim is a downward trend in the concentrations of pollutants or their pollution effects.	Offshore: Where established meet the OSPAR Environmental Assessment Criteria and / or Background Assessment Criteria. Where these standards have not yet been formulated, the aim is a downward trend in the concentrations of pollutants or their pollution effects.	Offshore: Where established meet the OSPAR Environmental Assessment Criteria and / or Background Assessment Criteria. Where these standards have not yet been formulated, the aim is a downward trend in the concentrations of pollutants or their pollution effects.	Offshore: Where established meet the OSPAR Environmental Assessment Criteria and / or Background Assessment Criteria. Where these standards have not yet been formulated, the aim is a downward trend in the concentrations of pollutants or their pollution effects.	Offshore: Where established meet the OSPAR Environmental Assessment Criteria and / or Background Assessment Criteria. Where these standards have not yet been formulated, the aim is a downward trend in the concentrations of pollutants or their pollution effects.	Offshore: Where established meet the OSPAR Environmental Assessment Criteria and / or Background Assessment Criteria. Where these standards have not yet been formulated, the aim is a downward trend in the concentrations of pollutants or their pollution effects.	Offshore: Where established meet the OSPAR Environmental Assessment Criteria and / or Background Assessment Criteria. Where these standards have not yet been formulated, the aim is a downward trend in the concentrations of pollutants or their pollution effects.	Monitoring copper concentrations at a regional level, now that this heavy metal is being used as a replacement for TBT (OSPAR).	Monitoring copper concentrations at a regional level, now that this heavy metal is being used as a replacement for TBT (OSPAR).	Monitoring copper concentrations at a regional level, now that this heavy metal is being used as a replacement for TBT (OSPAR).	Monitoring copper concentrations at a regional level, now that this heavy metal is being used as a replacement for TBT (OSPAR).	Monitoring copper concentrations at a regional level, now that this heavy metal is being used as a replacement for TBT (OSPAR).	Monitoring copper concentrations at a regional level, now that this heavy metal is being used as a replacement for TBT (OSPAR).	Monitoring copper concentrations at a regional level, now that this heavy metal is being used as a replacement for TBT (OSPAR).	Monitoring copper concentrations at a regional level, now that this heavy metal is being used as a replacement for TBT (OSPAR).	Monitoring copper concentrations at a regional level, now that this heavy metal is being used as a replacement for TBT (OSPAR).	Monitoring copper concentrations at a regional level, now that this heavy metal is being used as a replacement for TBT (OSPAR).	Monitoring copper concentrations at a regional level, now that this heavy metal is being used as a replacement for TBT (OSPAR).	Monitoring copper concentrations at a regional level, now that this heavy metal is being used as a replacement for TBT (OSPAR).	Monitoring copper concentrations at a regional level, now that this heavy metal is being used as a replacement for TBT (OSPAR).	Monitoring copper concentrations at a regional level, now that this heavy metal is being used as a replacement for TBT (OSPAR).	Monitoring copper concentrations at a regional level, now that this heavy metal is being used as a replacement for TBT (OSPAR).	Monitoring copper concentrations at a regional level, now that this heavy metal is being used as a replacement for TBT (OSPAR).	Monitoring copper concentrations at a regional level, now that this heavy metal is being used as a replacement for TBT (OSPAR).	Monitoring copper concentrations at a regional level, now that this heavy metal is being used as a replacement for TBT (OSPAR).	Monitoring copper concentrations at a regional level, now that this heavy metal is being used as a replacement for TBT (OSPAR).	Monitoring copper concentrations at a regional level, now that this heavy metal is being used as a replacement for TBT (OSPAR).	Decrease the supply of heavy metals in the marine environment	Decrease the supply of heavy metals in the marine environment	Decrease the supply of heavy metals in the marine environment	Decrease the supply of heavy metals in the marine environment	Decrease the supply of heavy metals in the marine environment	Decrease the supply of heavy metals in the marine environment	Decrease the supply of heavy metals in the marine environment	Decrease the supply of heavy metals in the marine environment	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
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 - 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 - 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
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) D8C2 Adverse effects of contaminants (8.2, 8.2.1)	D8C1 Contaminants in environment (8.1, 8.1.1) D8C2 Adverse effects of contaminants (8.2, 8.2.1)	D8C1 Contaminants in environment (8.1, 8.1.1) D8C2 Adverse effects of contaminants (8.2, 8.2.1)	D8C1 Contaminants in environment (8.1, 8.1.1) D8C2 Adverse effects of contaminants (8.2, 8.2.1)	D8C1 Contaminants in environment (8.1, 8.1.1) D8C2 Adverse effects of contaminants (8.2, 8.2.1)	D8C1 Contaminants in environment (8.1, 8.1.1) D8C2 Adverse effects of contaminants (8.2, 8.2.1)	D8C1 Contaminants in environment (8.1, 8.1.1) D8C2 Adverse effects of contaminants (8.2, 8.2.1)	D8C1 Contaminants in environment (8.1, 8.1.1) D8C2 Adverse effects of contaminants (8.2, 8.2.1)	D8C1 Contaminants in environment (8.1, 8.1.1) D8C2 Adverse effects of contaminants (8.2, 8.2.1)	D8C1 Contaminants in environment (8.1, 8.1.1) D8C2 Adverse effects of contaminants (8.2, 8.2.1)	D8C1 Contaminants in environment (8.1, 8.1.1) D8C2 Adverse effects of contaminants (8.2, 8.2.1)	D8C1 Contaminants in environment (8.1, 8.1.1) D8C2 Adverse effects of contaminants (8.2, 8.2.1)	D8C1 Contaminants in environment (8.1, 8.1.1) D8C2 Adverse effects of contaminants (8.2, 8.2.1)	D8C1 Contaminants in environment (8.1, 8.1.1) D8C2 Adverse effects of contaminants (8.2, 8.2.1)	D8C1 Contaminants in environment (8.1, 8.1.1) D8C2 Adverse effects of contaminants (8.2, 8.2.1)	D8C1 Contaminants in environment (8.1, 8.1.1) D8C2 Adverse effects of contaminants (8.2, 8.2.1)	D8C1 Contaminants in environment (8.1, 8.1.1) D8C2 Adverse effects of contaminants (8.2, 8.2.1)	D8C1 Contaminants in environment (8.1, 8.1.1) D8C2 Adverse effects of contaminants (8.2, 8.2.1)	D8C1 Contaminants in environment (8.1, 8.1.1) D8C2 Adverse effects of contaminants (8.2, 8.2.1)	D8C1 Contaminants in environment (8.1, 8.1.1) D8C2 Adverse effects of contaminants (8.2, 8.2.1)	D8C1 Contaminants in environment (8.1, 8.1.1) D8C2 Adverse effects of contaminants (8.2, 8.2.1)	D8C1 Contaminants in environment (8.1, 8.1.1) D8C2 Adverse effects of contaminants (8.2, 8.2.1)	D8C1 Contaminants in environment (8.1, 8.1.1) D8C2 Adverse effects of contaminants (8.2, 8.2.1)	D8C1 Contaminants in environment (8.1, 8.1.1) D8C2 Adverse effects of contaminants (8.2, 8.2.1)	D8C1 Contaminants in environment (8.1, 8.1.1) D8C2 Adverse effects of contaminants (8.2, 8.2.1)	D8C1 Contaminants in environment (8.1, 8.1.1) D8C2 Adverse effects of contaminants (8.2, 8.2.1)	D8C1 Contaminants in environment (8.1, 8.1.1) D8C2 Adverse effects of contaminants (8.2, 8.2.1)	D8C1 Contaminants in environment (8.1, 8.1.1) D8C2 Adverse effects of contaminants (8.2, 8.2.1)	D8C1 Contaminants in environment (8.1, 8.1.1) D8C2 Adverse effects of contaminants (8.2, 8.2.1)	D8C1 Contaminants in environment (8.1, 8.1.1) D8C2 Adverse effects of contaminants (8.2, 8.2.1)	D8C1 Contaminants in environment (8.1, 8.1.1) D8C2 Adverse effects of contaminants (8.2, 8.2.1)	D8C1 Contaminants in environment (8.1, 8.1.1) D8C2 Adverse effects of contaminants (8.2, 8.2.1)	D8C1 Contaminants in environment (8.1, 8.1.1) D8C2 Adverse effects of contaminants (8.2, 8.2.1)	D8C1 Contaminants in environment (8.1, 8.1.1) D8C2 Adverse effects of contaminants (8.2, 8.2.1)	D8C1 Contaminants in environment (8.1, 8.1.1) D8C2 Adverse effects of contaminants (8.2, 8.2.1)	D8C1 Contaminants in environment (8.1, 8.1.1) D8C2 Adverse effects of contaminants (8.2, 8.2.1)	D8C1 Contaminants in environment (8.1, 8.1.1) D8C2 Adverse effects of contaminants (8.2, 8.2.1)	D8C1 Contaminants in environment (8.1, 8.1.1) D8C2 Adverse effects of contaminants (8.2, 8.2.1)	D8C1 Contaminants in environment (8.1, 8.1.1) D8C2 Adverse effects of contaminants (8.2, 8.2.1)	D8C1 Contaminants in environment (8.1, 8.1.1) D8C2 Adverse effects of contaminants (8.2, 8.2.1)	D8C1 Contaminants in environment (8.1, 8.1.1) D8C2 Adverse effects of contaminants (8.2, 8.2.1)	D8C1 Contaminants in environment (8.1, 8.1.1) D8C2 Adverse effects of contaminants (8.2, 8.2.1)	D8C1 Contaminants in environment (8.1, 8.1.1) D8C2 Adverse effects of contaminants (8.2, 8.2.1)	D8C1 Contaminants in environment (8.1, 8.1.1) D8C2 Adverse effects of contaminants (8.2, 8.2.1)	D8C1 Contaminants in environment (8.1, 8.1.1) D8C2 Adverse effects of contaminants (8.2, 8.2.1)	D8C1 Contaminants in environment (8.1, 8.1.1) D8C2 Adverse effects of contaminants (8.2, 8.2.1)	D8C1 Contaminants in environment (8.1, 8.1.1) D8C2 Adverse effects of contaminants (8.2, 8.2.1)	D8C1 Contaminants in environment (8.1, 8.1.1) D8C2 Adverse effects of contaminants (8.2, 8.2.1)	D8C1 Contaminants in environment (8.1, 8.1.1) D8C2 Adverse effects of contaminants (8.2, 8.2.1)	D8C1 Contaminants in environment (8.1, 8.1.1) D8C2 Adverse effects of contaminants (8.2, 8.2.1)	D8C1 Contaminants in environment (8.1, 8.1.1) D8C2 Adverse effects of contaminants (8.2, 8.2.1)	D8C1 Contaminants in environment (8.1, 8.1.1) D8C2 Adverse effects of contaminants (8.2, 8.2.1)	D8C1 Contaminants in environment (8.1, 8.1.1)	D8C1 Contaminants in environment (8.1, 8.1.1)	D8C1 Contaminants in environment (8.1, 8.1.1)	D8C1 Contaminants in environment (8.1, 8.1.1)	D8C1 Contaminants in environment (8.1, 8.1.1)	D8C1 Contaminants in environment (8.1, 8.1.1)	D8C1 Contaminants in environment (8.1, 8.1.1)	D8C1 Contaminants in environment (8.1, 8.1.1)	D8C1 Contaminants in environment (8.1, 8.1.1)	D8C1 Contaminants in environment (8.1, 8.1.1)	D8C1 Contaminants in environment (8.1, 8.1.1)	D8C1 Contaminants in environment (8.1, 8.1.1)	D8C1 Contaminants in environment (8.1, 8.1.1)	D8C1 Contaminants in environment (8.1, 8.1.1)	D8C1 Contaminants in environment (8.1, 8.1.1)	D8C1 Contaminants in environment (8.1, 8.1.1)	D8C1 Contaminants in environment (8.1, 8.1.1)	D8C1 Contaminants in environment (8.1, 8.1.1)	D8C1 Contaminants in environment (8.1, 8.1.1)	D8C1 Contaminants in environment (8.1, 8.1.1)	D8C1 Contaminants in environment (8.1, 8.1.1)	D8C1 Contaminants in environment (8.1, 8.1.1)	D8C1 Contaminants in environment (8.1, 8.1.1)	D8C1 Contaminants in environment (8.1, 8.1.1)	D8C1 Contaminants in environment (8.1, 8.1.1)	D8C1 Contaminants in environment (8.1, 8.1.1)	D8C1 Contaminants in environment (8.1, 8.1.1)	D8C1 Contaminants in environment (8.1, 8.1.1)	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)
Timescale	202707	202707	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202407	202707	202707	202707	202707	202707	202707	202707	202707
Update date	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	201807	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	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	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	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	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	Anthracene	BDE 100 (2,2’,4,4’,6-pentabromodiphenyl ether)	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	Benz(a)anthracene	Benzo(a)pyrene	Benzo(a)pyrene	Benzo(g,h,i)perylene	Benzo(g,h,i)perylene	Cadmium and its compounds	Cadmium and its compounds	Chrysene	Chrysene	Fluoranthene	Fluoranthene	Indeno(1,2,3,-cd)pyrene	Indeno(1,2,3,-cd)pyrene	Lead and its compounds	Lead and its compounds	Mercury and its compounds	Mercury and its compounds	Monobutyltin ion	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	Phenanthrene	Pyrene	Pyrene	Tributyltin-cation	Vas deferens index	Anthracene	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	Monobutyltin ion	Phenanthrene	Pyrene	Tributyltin-cation	Vas deferens index	WFD UPBT substances	WFD non UPBT substances	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	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
Element 2
Parameter	Concentration in water	Concentration in water	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 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 biota	Concentration in sediment	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 biota	Concentration in sediment	Concentration in biota	Concentration in sediment	Concentration in sediment	Other	Concentration in biota	Concentration in biota	Concentration in biota	Concentration in biota	Concentration in biota	Concentration in sediment	Concentration in biota	Concentration in biota	Concentration in biota	Concentration in biota	Concentration in sediment	Concentration in biota	Concentration in sediment	Concentration in sediment	Concentration in biota	Concentration in biota	Concentration in sediment	Other	Concentration in water	Concentration in water	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 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
Parameter - other																																																						Occurrence of imposex																		Occurse of imposex																																																		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	-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	-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
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	-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		-1.0	-1.0	-1.0	-1.0	-1.0	-1.0			-1.0	1.0	-1.0	-1.0	-1.0		-1.0
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	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	Other	Other	Other	Other	Other	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
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	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	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
Target status	Target not yet 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 achieved	Target not yet achieved	Target achieved	Target not yet achieved	Target 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 achieved	Target achieved	Target not yet achieved	Target achieved	Target not yet achieved	Target achieved	Target not yet 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	Target achieved	Target achieved	Target 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 not yet 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 not yet achieved	Target achieved	Target achieved	Target achieved	Target not yet achieved	Target achieved	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
Assessment period	2012-2014	2012-2014	2000-2015	1995-2015	2009-2015	2010-2015	2009-2015	2010-2015	2009-2015	2010-2015	2009-2015	2010-2015	2009-2015	2010-2015	2000-2015	1995-2015	2000-2015	1995-2015	2000-2015	1995-2015	1995-2015	1995-2015	2000-2015	1995-2015	2000-2015	1995-2015	2000-2015	1995-2015	2010-2015	1995-2015	1995-2015	1995-2015	2000-2015	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	2000-2015	1995-2015	2000-2015	1995-2015	2000-2015	2010-2015	2000-2015	2000-2015	2000-2015	2000-2015	1995-2015	1995-2015	2000-2015	2000-2015	2000-2015	1995-2015	1995-2015	1995-2015	1995-2015	2000-2015	2000-2015	2000-2015	2000-2015	2010-2015	2012-2014	2012-2014	1995-2015	1995-2015	1995-2015	1995-2015	1995-2015	1995-2015	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
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 concentrations of mercury, lead, cadmium in sediment are decreasing								The concentrations of mercury, lead, cadmium in sediment are decreasing		The concentrations of mercury, lead, cadmium in sediment are decreasing	The concentrations of all organotins in sediment are falling		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.	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.	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 concentrations of all organotins in sediment are falling															The concentrations of all organotins in sediment are falling			The concentrations of all organotins in sediment are falling		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 concentrations of mercury, lead and cadmium in sediment are decreasing.		The concentrations of mercury, lead and cadmium in sediment are decreasing.		The concentrations of mercury, lead and cadmium in sediment are decreasing.	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.
Related indicator	KRW verontreinigende stoffen in water	KRW verontreinigende stoffen in water	Status and Trends in the Concentrations of Polycyclic Aromatic Hydrocarbons (PAHs) in Shellfish	Status and Trends in the Concentrations of Polycyclic Aromatic Hydrocarbons (PAHs) in Sediment	Trends in Concentrations of Polybrominated Diphenyl Ethers (PBDEs) in Fish and Shellfish	Trends in Concentrations of Polybrominated Diphenyl Ethers (PBDEs) in Sediments	Trends in Concentrations of Polybrominated Diphenyl Ethers (PBDEs) in Fish and Shellfish	Trends in Concentrations of Polybrominated Diphenyl Ethers (PBDEs) in Sediments	Trends in Concentrations of Polybrominated Diphenyl Ethers (PBDEs) in Fish and Shellfish	Trends in Concentrations of Polybrominated Diphenyl Ethers (PBDEs) in Sediments	Trends in Concentrations of Polybrominated Diphenyl Ethers (PBDEs) in Fish and Shellfish	Trends in Concentrations of Polybrominated Diphenyl Ethers (PBDEs) in Sediments	Trends in Concentrations of Polybrominated Diphenyl Ethers (PBDEs) in Fish and Shellfish	Trends in Concentrations of Polybrominated Diphenyl Ethers (PBDEs) in Sediments	Status and Trends in the Concentrations of Polycyclic Aromatic Hydrocarbons (PAHs) in Shellfish	Status and Trends in the Concentrations of Polycyclic Aromatic Hydrocarbons (PAHs) in Sediment	Status and Trends in the Concentrations of Polycyclic Aromatic Hydrocarbons (PAHs) in Shellfish	Status and Trends in the Concentrations of Polycyclic Aromatic Hydrocarbons (PAHs) in Sediment	Status and Trends in the Concentrations of Polycyclic Aromatic Hydrocarbons (PAHs) in Shellfish	Status and Trends in the Concentrations of Polycyclic Aromatic Hydrocarbons (PAHs) in Sediment	Status and Trend for Heavy Metals (Mercury, Cadmium, and Lead) in Fish and Shellfish	Status en trends in de concentratie van metalen in sediment	Status and Trends in the Concentrations of Polycyclic Aromatic Hydrocarbons (PAHs) in Shellfish	Status and Trends in the Concentrations of Polycyclic Aromatic Hydrocarbons (PAHs) in Sediment	Status and Trends in the Concentrations of Polycyclic Aromatic Hydrocarbons (PAHs) in Shellfish	Status and Trends in the Concentrations of Polycyclic Aromatic Hydrocarbons (PAHs) in Sediment	Status and Trends in the Concentrations of Polycyclic Aromatic Hydrocarbons (PAHs) in Shellfish	Status and Trends in the Concentrations of Polycyclic Aromatic Hydrocarbons (PAHs) in Sediment	Status and Trend for Heavy Metals (Mercury, Cadmium, and Lead) in Fish and Shellfish	Status en trends in de concentratie van metalen in sediment	Status and Trend for Heavy Metals (Mercury, Cadmium, and Lead) in Fish and Shellfish	Status en trends in de concentratie van metalen in sediment	Trends of Organotin in Sediments in the Southern North Sea	Status and Trends in the Concentrations of Polycyclic Aromatic Hydrocarbons (PAHs) in Sediment	Status and Trends of Polychlorinated Biphenyls (PCB) in Fish and Shellfish	Status and Trends of Polychlorinated Biphenyls (PCB) in Sediment	Status and Trends of Polychlorinated Biphenyls (PCB) in Fish and Shellfish	Status and Trends of Polychlorinated Biphenyls (PCB) in Sediment	Status and Trends of Polychlorinated Biphenyls (PCB) in Fish and Shellfish	Status and Trends of Polychlorinated Biphenyls (PCB) in Sediment	Status and Trends of Polychlorinated Biphenyls (PCB) in Fish and Shellfish	Status and Trends of Polychlorinated Biphenyls (PCB) in Sediment	Status and Trends of Polychlorinated Biphenyls (PCB) in Fish and Shellfish	Status and Trends of Polychlorinated Biphenyls (PCB) in Sediment	Status and Trends of Polychlorinated Biphenyls (PCB) in Fish and Shellfish	Status and Trends of Polychlorinated Biphenyls (PCB) in Sediment	Status and Trends of Polychlorinated Biphenyls (PCB) in Fish and Shellfish	Status and Trends of Polychlorinated Biphenyls (PCB) in Sediment	Status and Trends in the Concentrations of Polycyclic Aromatic Hydrocarbons (PAHs) in Shellfish	Status and Trends in the Concentrations of Polycyclic Aromatic Hydrocarbons (PAHs) in Sediment	Status and Trends in the Concentrations of Polycyclic Aromatic Hydrocarbons (PAHs) in Shellfish	Status and Trends in the Concentrations of Polycyclic Aromatic Hydrocarbons (PAHs) in Sediment	Trends of Organotin in Sediments in the Southern North Sea	Trends in New Records of Non-Indigenous Species Introduced by Human Activities	Status and Trends in the Concentrations of Polycyclic Aromatic Hydrocarbons (PAHs) in Shellfish	Status and Trends in the Concentrations of Polycyclic Aromatic Hydrocarbons (PAHs) in Shellfish	Status and Trends in the Concentrations of Polycyclic Aromatic Hydrocarbons (PAHs) in Shellfish	Status and Trends in the Concentrations of Polycyclic Aromatic Hydrocarbons (PAHs) in Shellfish	Status and Trend for Heavy Metals (Mercury, Cadmium, and Lead) in Fish and Shellfish	Status en trends in de concentratie van metalen in sediment	Status and Trends in the Concentrations of Polycyclic Aromatic Hydrocarbons (PAHs) in Shellfish	Status and Trends in the Concentrations of Polycyclic Aromatic Hydrocarbons (PAHs) in Shellfish	Status and Trends in the Concentrations of Polycyclic Aromatic Hydrocarbons (PAHs) in Shellfish	Status and Trend for Heavy Metals (Mercury, Cadmium, and Lead) in Fish and Shellfish	Status en trends in de concentratie van metalen in sediment	Status and Trend for Heavy Metals (Mercury, Cadmium, and Lead) in Fish and Shellfish	Status en trends in de concentratie van metalen in sediment	Trends of Organotin in Sediments in the Southern North Sea	Status and Trends in the Concentrations of Polycyclic Aromatic Hydrocarbons (PAHs) in Shellfish	Status and Trends in the Concentrations of Polycyclic Aromatic Hydrocarbons (PAHs) in Shellfish	Trends of Organotin in Sediments in the Southern North Sea	Trends in New Records of Non-Indigenous Species Introduced by Human Activities	KRW verontreinigende stoffen in water	KRW verontreinigende stoffen in water	Status and Trend for Heavy Metals (Mercury, Cadmium, and Lead) in Fish and Shellfish	Status en trends in de concentratie van metalen in sediment	Status and Trend for Heavy Metals (Mercury, Cadmium, and Lead) in Fish and Shellfish	Status en trends in de concentratie van metalen in sediment	Status and Trend for Heavy Metals (Mercury, Cadmium, and Lead) in Fish and Shellfish	Status en trends in de concentratie van metalen in sediment	KRW verontreinigende stoffen in water	KRW verontreinigende stoffen in water	Status and Trends in the Concentrations of Polycyclic Aromatic Hydrocarbons (PAHs) in Sediment	Trends in Concentrations of Polybrominated Diphenyl Ethers (PBDEs) in Fish and Shellfish	Trends in Concentrations of Polybrominated Diphenyl Ethers (PBDEs) in Fish and Shellfish	Trends in Concentrations of Polybrominated Diphenyl Ethers (PBDEs) in Sediments	Trends in Concentrations of Polybrominated Diphenyl Ethers (PBDEs) in Fish and Shellfish	Trends in Concentrations of Polybrominated Diphenyl Ethers (PBDEs) in Sediments	Trends in Concentrations of Polybrominated Diphenyl Ethers (PBDEs) in Fish and Shellfish	Trends in Concentrations of Polybrominated Diphenyl Ethers (PBDEs) in Sediments	Trends in Concentrations of Polybrominated Diphenyl Ethers (PBDEs) in Fish and Shellfish	Trends in Concentrations of Polybrominated Diphenyl Ethers (PBDEs) in Sediments	Status and Trends in the Concentrations of Polycyclic Aromatic Hydrocarbons (PAHs) in Sediment	Status and Trends in the Concentrations of Polycyclic Aromatic Hydrocarbons (PAHs) in Sediment	Status and Trends in the Concentrations of Polycyclic Aromatic Hydrocarbons (PAHs) in Sediment	Status and Trend for Heavy Metals (Mercury, Cadmium, and Lead) in Fish and Shellfish	Status en trends in de concentratie van metalen in sediment	Status and Trends in the Concentrations of Polycyclic Aromatic Hydrocarbons (PAHs) in Sediment	Status and Trends in the Concentrations of Polycyclic Aromatic Hydrocarbons (PAHs) in Sediment	Status and Trends in the Concentrations of Polycyclic Aromatic Hydrocarbons (PAHs) in Sediment	Status and Trend for Heavy Metals (Mercury, Cadmium, and Lead) in Fish and Shellfish	Status en trends in de concentratie van metalen in sediment	Status and Trend for Heavy Metals (Mercury, Cadmium, and Lead) in Fish and Shellfish	Status en trends in de concentratie van metalen in sediment	Status and Trends in the Concentrations of Polycyclic Aromatic Hydrocarbons (PAHs) in Sediment	Status and Trends of Polychlorinated Biphenyls (PCB) in Fish and Shellfish	Status and Trends of Polychlorinated Biphenyls (PCB) in Sediment	Status and Trends of Polychlorinated Biphenyls (PCB) in Fish and Shellfish	Status and Trends of Polychlorinated Biphenyls (PCB) in Sediment	Status and Trends of Polychlorinated Biphenyls (PCB) in Fish and Shellfish	Status and Trends of Polychlorinated Biphenyls (PCB) in Sediment	Status and Trends of Polychlorinated Biphenyls (PCB) in Fish and Shellfish	Trends in Concentrations of Polybrominated Diphenyl Ethers (PBDEs) in Sediments	Status and Trends of Polychlorinated Biphenyls (PCB) in Fish and Shellfish	Status and Trends of Polychlorinated Biphenyls (PCB) in Sediment	Status and Trends of Polychlorinated Biphenyls (PCB) in Fish and Shellfish	Status and Trends of Polychlorinated Biphenyls (PCB) in Sediment	Status and Trends of Polychlorinated Biphenyls (PCB) in Fish and Shellfish	Status and Trends of Polychlorinated Biphenyls (PCB) in Sediment	Status and Trends in the Concentrations of Polycyclic Aromatic Hydrocarbons (PAHs) in Sediment	Status and Trends in the Concentrations of Polycyclic Aromatic Hydrocarbons (PAHs) in Sediment	Verontreinigingen van olie en olieachtige stoffen.	Status and Trend for Heavy Metals (Mercury, Cadmium, and Lead) in Fish and Shellfish	Status en trends in de concentratie van metalen in sediment	Status and Trend for Heavy Metals (Mercury, Cadmium, and Lead) in Fish and Shellfish	Status en trends in de concentratie van metalen in sediment	Status and Trend for Heavy Metals (Mercury, Cadmium, and Lead) in Fish and Shellfish	Status en trends in de concentratie van metalen in sediment	KRW verontreinigende stoffen in water	KRW verontreinigende stoffen in water
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-M013 ANSNL-M014 ANSNL-M015 ANSNL-M016 ANSNL-M020 ANSNL-M022	ANSNL-M013 ANSNL-M014 ANSNL-M015 ANSNL-M016 ANSNL-M020 ANSNL-M022	ANSNL-M013 ANSNL-M014 ANSNL-M015 ANSNL-M016 ANSNL-M020 ANSNL-M022	ANSNL-M013 ANSNL-M014 ANSNL-M015 ANSNL-M016 ANSNL-M020 ANSNL-M022	ANSNL-M013 ANSNL-M014 ANSNL-M015 ANSNL-M016 ANSNL-M020 ANSNL-M022	ANSNL-M013 ANSNL-M014 ANSNL-M015 ANSNL-M016 ANSNL-M020 ANSNL-M022	ANSNL-M013 ANSNL-M014 ANSNL-M015 ANSNL-M016 ANSNL-M020 ANSNL-M022	ANSNL-M013 ANSNL-M014 ANSNL-M015 ANSNL-M016 ANSNL-M020 ANSNL-M022	ANSNL-M013 ANSNL-M014 ANSNL-M015 ANSNL-M016 ANSNL-M020 ANSNL-M022	ANSNL-M013 ANSNL-M014 ANSNL-M015 ANSNL-M016 ANSNL-M020 ANSNL-M022	ANSNL-M013 ANSNL-M014 ANSNL-M015 ANSNL-M016 ANSNL-M020 ANSNL-M022	ANSNL-M013 ANSNL-M014 ANSNL-M015 ANSNL-M016 ANSNL-M020 ANSNL-M022	ANSNL-M013 ANSNL-M014 ANSNL-M015 ANSNL-M016 ANSNL-M020 ANSNL-M022	ANSNL-M013 ANSNL-M014 ANSNL-M015 ANSNL-M016 ANSNL-M020 ANSNL-M022	ANSNL-M013 ANSNL-M014 ANSNL-M015 ANSNL-M016 ANSNL-M020 ANSNL-M022	ANSNL-M013 ANSNL-M014 ANSNL-M015 ANSNL-M016 ANSNL-M020 ANSNL-M022	ANSNL-M013 ANSNL-M014 ANSNL-M015 ANSNL-M016 ANSNL-M020 ANSNL-M022	ANSNL-M013 ANSNL-M014 ANSNL-M015 ANSNL-M016 ANSNL-M020 ANSNL-M022	ANSNL-M013 ANSNL-M014 ANSNL-M015 ANSNL-M016 ANSNL-M020 ANSNL-M022	ANSNL-M013 ANSNL-M014 ANSNL-M015 ANSNL-M016 ANSNL-M020 ANSNL-M022	ANSNL-M013 ANSNL-M014 ANSNL-M015 ANSNL-M016 ANSNL-M020 ANSNL-M022	ANSNL-M013 ANSNL-M014 ANSNL-M015 ANSNL-M016 ANSNL-M020 ANSNL-M022	ANSNL-M013 ANSNL-M014 ANSNL-M015 ANSNL-M016 ANSNL-M020 ANSNL-M022	ANSNL-M013 ANSNL-M014 ANSNL-M015 ANSNL-M016 ANSNL-M020 ANSNL-M022	ANSNL-M013 ANSNL-M014 ANSNL-M015 ANSNL-M016 ANSNL-M020 ANSNL-M022	ANSNL-M013 ANSNL-M014 ANSNL-M015 ANSNL-M016 ANSNL-M020 ANSNL-M022	ANSNL-M013 ANSNL-M014 ANSNL-M015 ANSNL-M016 ANSNL-M020 ANSNL-M022	ANSNL-M013 ANSNL-M014 ANSNL-M015 ANSNL-M016 ANSNL-M020 ANSNL-M022	ANSNL-M013 ANSNL-M014 ANSNL-M015 ANSNL-M016 ANSNL-M020 ANSNL-M022	ANSNL-M013 ANSNL-M014 ANSNL-M015 ANSNL-M016 ANSNL-M020 ANSNL-M022	ANSNL-M013 ANSNL-M014 ANSNL-M015 ANSNL-M016 ANSNL-M020 ANSNL-M022	ANSNL-M013 ANSNL-M014 ANSNL-M015 ANSNL-M016 ANSNL-M020 ANSNL-M022	ANSNL-M013 ANSNL-M014 ANSNL-M015 ANSNL-M016 ANSNL-M020 ANSNL-M022	ANSNL-M013 ANSNL-M014 ANSNL-M015 ANSNL-M016 ANSNL-M020 ANSNL-M022	ANSNL-M013 ANSNL-M014 ANSNL-M015 ANSNL-M016 ANSNL-M020 ANSNL-M022	ANSNL-M013 ANSNL-M014 ANSNL-M015 ANSNL-M016 ANSNL-M020 ANSNL-M022	ANSNL-M013 ANSNL-M014 ANSNL-M015 ANSNL-M016 ANSNL-M020 ANSNL-M022	ANSNL-M013 ANSNL-M014 ANSNL-M015 ANSNL-M016 ANSNL-M020 ANSNL-M022	ANSNL-M013 ANSNL-M014 ANSNL-M015 ANSNL-M016 ANSNL-M020 ANSNL-M022	ANSNL-M013 ANSNL-M014 ANSNL-M015 ANSNL-M016 ANSNL-M020 ANSNL-M022	ANSNL-M013 ANSNL-M014 ANSNL-M015 ANSNL-M016 ANSNL-M020 ANSNL-M022	ANSNL-M013 ANSNL-M014 ANSNL-M015 ANSNL-M016 ANSNL-M020 ANSNL-M022	ANSNL-M013 ANSNL-M014 ANSNL-M015 ANSNL-M016 ANSNL-M020 ANSNL-M022	ANSNL-M013 ANSNL-M014 ANSNL-M015 ANSNL-M016 ANSNL-M020 ANSNL-M022	ANSNL-M013 ANSNL-M014 ANSNL-M015 ANSNL-M016 ANSNL-M020 ANSNL-M022	ANSNL-M013 ANSNL-M014 ANSNL-M015 ANSNL-M016 ANSNL-M020 ANSNL-M022	ANSNL-M013 ANSNL-M014 ANSNL-M015 ANSNL-M016 ANSNL-M020 ANSNL-M022	ANSNL-M013 ANSNL-M014 ANSNL-M015 ANSNL-M016 ANSNL-M020 ANSNL-M022	ANSNL-M013 ANSNL-M014 ANSNL-M015 ANSNL-M016 ANSNL-M020 ANSNL-M022	ANSNL-M013 ANSNL-M014 ANSNL-M015 ANSNL-M016 ANSNL-M020 ANSNL-M022	ANSNL-M013 ANSNL-M014 ANSNL-M015 ANSNL-M016 ANSNL-M020 ANSNL-M022	ANSNL-M013 ANSNL-M014 ANSNL-M015 ANSNL-M016 ANSNL-M020 ANSNL-M022	NotApplicable	NotApplicable	NotApplicable	NotApplicable	NotApplicable	NotApplicable	NotApplicable	NotApplicable	NotApplicable	NotApplicable	NotApplicable	NotApplicable	NotApplicable	NotApplicable	NotApplicable	NotApplicable	NotApplicable	NotApplicable	NotApplicable	NotApplicable	ANSNL-M012 ANSNL-M013 ANSNL-M014 ANSNL-M015 ANSNL-M016 ANSNL-M017 ANSNL-M018 ANSNL-M019 ANSNL-M020	ANSNL-M012 ANSNL-M013 ANSNL-M014 ANSNL-M015 ANSNL-M016 ANSNL-M017 ANSNL-M018 ANSNL-M019 ANSNL-M020	ANSNL-M012 ANSNL-M013 ANSNL-M014 ANSNL-M015 ANSNL-M016 ANSNL-M017 ANSNL-M018 ANSNL-M019 ANSNL-M020	ANSNL-M012 ANSNL-M013 ANSNL-M014 ANSNL-M015 ANSNL-M016 ANSNL-M017 ANSNL-M018 ANSNL-M019 ANSNL-M020	ANSNL-M012 ANSNL-M013 ANSNL-M014 ANSNL-M015 ANSNL-M016 ANSNL-M017 ANSNL-M018 ANSNL-M019 ANSNL-M020	ANSNL-M012 ANSNL-M013 ANSNL-M014 ANSNL-M015 ANSNL-M016 ANSNL-M017 ANSNL-M018 ANSNL-M019 ANSNL-M020	ANSNL-M012 ANSNL-M013 ANSNL-M014 ANSNL-M015 ANSNL-M016 ANSNL-M017 ANSNL-M018 ANSNL-M019 ANSNL-M020	ANSNL-M012 ANSNL-M013 ANSNL-M014 ANSNL-M015 ANSNL-M016 ANSNL-M017 ANSNL-M018 ANSNL-M019 ANSNL-M020	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