MS/Art8-2024/2024/D1-M/Netherlands/NE Atlantic: Greater North Sea

Member State report / Art8-2024 / 2024 / D1-M / Netherlands / NE Atlantic: Greater North Sea

Report type	Member State report to Commission
MSFD Article	Art8
Report due	2024-10-15
GES Descriptor	D1 Mammals
Member State	Netherlands
Region/subregion	NE Atlantic: Greater North Sea
Report date	2026-04-10 12:40:24

Nederlands Continentaal Plat vanaf de basislijn (0 mijl) (ANS-NL-MS-1)

Simplified table

Regional assessment area	abundance-distribution-cetaceans-qsr23-ospar-Greater North Sea	abundance-distribution-cetaceans-qsr23-ospar-Greater North Sea	abundance-distribution-cetaceans-qsr23-ospar-Greater North Sea	abundance-distribution-cetaceans-qsr23-ospar-Greater North Sea	abundance-distribution-cetaceans-qsr23-ospar-Greater North Sea	abundance-distribution-cetaceans-qsr23-ospar-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea	OSPAR-Greater North Sea
Component MRUs
GES component	D1M	D1M	D1M	D1M	D1M	D1M	D1M	D1M	D1M	D1M	D1M	D1M	D1M	D1M	D1M	D1M
Feature	Small toothed cetaceans	Small toothed cetaceans	Small toothed cetaceans	Small toothed cetaceans	Small toothed cetaceans	Small toothed cetaceans	Seals	Seals	Seals	Seals	Seals	Seals	Seals	Seals	Seals	Seals
Element	Phocoena phocoena	Phocoena phocoena	Phocoena phocoena	Phocoena phocoena	Phocoena phocoena	Phocoena phocoena	Halichoerus grypus	Halichoerus grypus	Halichoerus grypus	Halichoerus grypus	Halichoerus grypus	Phoca vitulina	Phoca vitulina	Phoca vitulina	Phoca vitulina	Phoca vitulina
Element extent
Trend element	Stable	Stable	Stable	Stable	Stable	Stable	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving
Element 2
Element source	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR
Criterion	D1C1	D1C2	D1C2	D1C3	D1C4	D1C5	D1C1	D1C2	D1C3	D1C4	D1C5	D1C1	D1C2	D1C3	D1C4	D1C5
Parameter	BR	Abundance	Abundance		Distribution (range)	Habitat condition	BR	Abundance		Distribution (range)	Habitat condition		Abundance		Distribution (range)	Habitat condition
Threshold value upper	1622.0	-1.6	60000.0		724.0		7171.0	5000.0		728.0			5000.0		762.0
Threshold value lower								1000.0					2000.0
Threshold value operator	<=	>=	>=				<=	>=					>=
Threshold qualitative		Sign of trend in abundance estimate
Threshold value source	OSPAR Convention	OSPAR Convention	HD		HD	HD	OSPAR Convention	HD		HD	HD		HD		HD	HD
Value achieved upper	5974.0		76800.0		724.0		704.0	5500.0		728.0			9000.0		762.0
Value achieved lower			41300.0					2700.0					7000.0
Value unit	individuals	percentage	individuals		Other	square kilometre	individuals	individuals		Other	square kilometre		individuals		Other	square kilometre
Proportion threshold value	100.0	100.0	100.0		100.0	100.0	100.0	100.0		100.0	100.0		100.0		100.0	100.0
Proportion value achieved		100.0	100.0		100.0		100.0	100.0		100.0			100.0		100.0
Proportion threshold value unit	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value		% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value		% of population achieving threshold value	% area of MRU achieving threshold value		% of population achieving threshold value		% of population achieving threshold value	% area of MRU achieving threshold value
Trend parameter	Unknown	Stable	Stable		Stable	Unknown	Unknown	Improving		Stable	Unknown		Improving		Stable	Unknown
Parameter achieved	No	Yes	Yes		Yes	Unknown	Yes	Yes		Yes	Unknown		Yes		Yes	Unknown
Description parameter	The incidental bycatch of harbour porpoises in the International North Sea was estimated at 5974 in 2020, significantly exceeding the threshold value (1622).	The number of harbour porpoises in the North Sea appears to be increasing slightly. However, the differences in counts are not significant. Nevertheless, it is plausible that the population has not declined since 1994, which means that the good environmental status has been maintained for criterion D1C2 concerning harbour porpoises.	An estimated 41300 to 76800 harbor porpoises live in the Dutch part of the North Sea, based on summer counts, which means that the good environmental status has been maintained. Harbor porpoise presence varies throughout the year; in the Dutch North Sea, the highest numbers occur in early spring and lower numbers occur in summer.		No significant changes have occurred in the geographical distribution of the harbour porpoise. The good environmental status has been maintained.	The main pressures for marine mammals are known, but there is still little knowledge on precise and especially cumulative effects, causal relationships and ecological preconditions. For this reason, for harbour porpoises D1C5 Habitat condition has been assessed as 'unknown'.	The incidental bycatch of gray seal meets the threshold value.	Good environmental status with regard to population size has been maintained for Halichoerus grypus		No significant changes have occurred in the geographical distribution of the Halichoerus grypus. The good environmental status has been maintained.	The main pressures for marine mammals are known, but there is still little knowledge on precise and especially cumulative effects, causal relationships and ecological preconditions. For this reason, for grey seal D1C5 Habitat condition has been assessed as 'unknown'.		Good environmental status with regard to population size has been maintained for Phoca vitulina.		No significant changes have occurred in the geographical distribution of the Phoca vitulina. The good environmental status has been maintained.	The main pressures for marine mammals are known, but there is still little knowledge on precise and especially cumulative effects, causal relationships and ecological preconditions. For this reason, for harbour seal D1C5 Habitat condition has been assessed as 'unknown'.
Related indicator	marine-mammal-bycatch-qsr23-ospar	abundance-distribution-cetaceans-qsr23-ospar	ANS-NL D1M-C2Populatie (HR) bruinvis		Verspreidingsgebied (HR) bruinvis	ANS-NL-HR-leefgebied zeezoogdieren	marine-mammal-bycatch-qsr23-ospar	ANS-NL D1M-C2 Populatie (HR) grijze zeehond		Verspreidingsgebied (HR) grijze zeehond	ANS-NL-HR-leefgebied zeezoogdieren		Populatie (HR) gewone zeehond		Verspreidingsgebied (HR) gewone zeehond	ANS-NL-HR-leefgebied zeezoogdieren
Criteria status	Not good	Good	Good	Not assessed	Good	Unknown	Good	Good	Good	Good	Unknown	Not assessed	Good	Good	Good	Unknown
Description criteria
Element status	Not good	Not good	Not good	Not good	Not good	Not good	Good	Good	Good	Good	Good	Good	Good	Good	Good	Good
Description element	The integrated assessment of harbour porpoise is based on information on incidental by-catch (D1C1), population abundance (D1C2) and distributional range (D1C4). For harbour porpoise the by-catch threshold has been exceeded.	The integrated assessment of harbour porpoise is based on information on incidental by-catch (D1C1), population abundance (D1C2) and distributional range (D1C4). For harbour porpoise the by-catch threshold has been exceeded.	The integrated assessment of harbour porpoise is based on information on incidental by-catch (D1C1), population abundance (D1C2) and distributional range (D1C4). For harbour porpoise the by-catch threshold has been exceeded.	The integrated assessment of harbour porpoise is based on information on incidental by-catch (D1C1), population abundance (D1C2) and distributional range (D1C4). For harbour porpoise the by-catch threshold has been exceeded.	The integrated assessment of harbour porpoise is based on information on incidental by-catch (D1C1), population abundance (D1C2) and distributional range (D1C4). For harbour porpoise the by-catch threshold has been exceeded.	The integrated assessment of harbour porpoise is based on information on incidental by-catch (D1C1), population abundance (D1C2) and distributional range (D1C4). For harbour porpoise the by-catch threshold has been exceeded.	The integrated assessment of seals is based on information on incidental by-catch (D1C1), population abundance (D1C2), pup production (D1C3) and distributional range (D1C4). Overall, grey seal and harbour seal show an upward trend during this planning period, leading to a positive assessment and good environmental status. It remains necessary to remain alert to the status of seals, however, given the sometimes sudden population trends in the past, and - in the case of the harbour seal - a flattening of the upward trend in the assessment period. There has even been a decline in population growth since 2021.	The integrated assessment of seals is based on information on incidental by-catch (D1C1), population abundance (D1C2), pup production (D1C3) and distributional range (D1C4). Overall, grey seal and harbour seal show an upward trend during this planning period, leading to a positive assessment and good environmental status. It remains necessary to remain alert to the status of seals, however, given the sometimes sudden population trends in the past, and - in the case of the harbour seal - a flattening of the upward trend in the assessment period. There has even been a decline in population growth since 2021.	The integrated assessment of seals is based on information on incidental by-catch (D1C1), population abundance (D1C2), pup production (D1C3) and distributional range (D1C4). Overall, grey seal and harbour seal show an upward trend during this planning period, leading to a positive assessment and good environmental status. It remains necessary to remain alert to the status of seals, however, given the sometimes sudden population trends in the past, and - in the case of the harbour seal - a flattening of the upward trend in the assessment period. There has even been a decline in population growth since 2021.	The integrated assessment of seals is based on information on incidental by-catch (D1C1), population abundance (D1C2), pup production (D1C3) and distributional range (D1C4). Overall, grey seal and harbour seal show an upward trend during this planning period, leading to a positive assessment and good environmental status. It remains necessary to remain alert to the status of seals, however, given the sometimes sudden population trends in the past, and - in the case of the harbour seal - a flattening of the upward trend in the assessment period. There has even been a decline in population growth since 2021.	The integrated assessment of seals is based on information on incidental by-catch (D1C1), population abundance (D1C2), pup production (D1C3) and distributional range (D1C4). Overall, grey seal and harbour seal show an upward trend during this planning period, leading to a positive assessment and good environmental status. It remains necessary to remain alert to the status of seals, however, given the sometimes sudden population trends in the past, and - in the case of the harbour seal - a flattening of the upward trend in the assessment period. There has even been a decline in population growth since 2021.	The integrated assessment of seals is based on information on incidental by-catch (D1C1), population abundance (D1C2), pup production (D1C3) and distributional range (D1C4). Overall, grey seal and harbour seal show an upward trend during this planning period, leading to a positive assessment and good environmental status. It remains necessary to remain alert to the status of seals, however, given the sometimes sudden population trends in the past, and - in the case of the harbour seal - a flattening of the upward trend in the assessment period. There has even been a decline in population growth since 2021.	The integrated assessment of seals is based on information on incidental by-catch (D1C1), population abundance (D1C2), pup production (D1C3) and distributional range (D1C4). Overall, grey seal and harbour seal show an upward trend during this planning period, leading to a positive assessment and good environmental status. It remains necessary to remain alert to the status of seals, however, given the sometimes sudden population trends in the past, and - in the case of the harbour seal - a flattening of the upward trend in the assessment period. There has even been a decline in population growth since 2021.	The integrated assessment of seals is based on information on incidental by-catch (D1C1), population abundance (D1C2), pup production (D1C3) and distributional range (D1C4). Overall, grey seal and harbour seal show an upward trend during this planning period, leading to a positive assessment and good environmental status. It remains necessary to remain alert to the status of seals, however, given the sometimes sudden population trends in the past, and - in the case of the harbour seal - a flattening of the upward trend in the assessment period. There has even been a decline in population growth since 2021.	The integrated assessment of seals is based on information on incidental by-catch (D1C1), population abundance (D1C2), pup production (D1C3) and distributional range (D1C4). Overall, grey seal and harbour seal show an upward trend during this planning period, leading to a positive assessment and good environmental status. It remains necessary to remain alert to the status of seals, however, given the sometimes sudden population trends in the past, and - in the case of the harbour seal - a flattening of the upward trend in the assessment period. There has even been a decline in population growth since 2021.	The integrated assessment of seals is based on information on incidental by-catch (D1C1), population abundance (D1C2), pup production (D1C3) and distributional range (D1C4). Overall, grey seal and harbour seal show an upward trend during this planning period, leading to a positive assessment and good environmental status. It remains necessary to remain alert to the status of seals, however, given the sometimes sudden population trends in the past, and - in the case of the harbour seal - a flattening of the upward trend in the assessment period. There has even been a decline in population growth since 2021.
Source assessment feature	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR	OSPAR
Reporting method feature	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A	Type A
Trend feature	Stable	Stable	Stable	Stable	Stable	Stable	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving
Integration rule type parameter	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO
Integration rule description parameter
Integration rule type criteria	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO	OOAO
Integration rule description criteria
GES extent threshold	100.00	100.00	100.00	100.00	100.00	100.00	100.00	100.00	100.00	100.00	100.00	100.00	100.00	100.00	100.00	100.00
GES extent achieved							100.00	100.00	100.00	100.00	100.00	100.00	100.00	100.00	100.00	100.00
GES extent unit	Proportion of populations in good status	Proportion of populations in good status	Proportion of populations in good status	Proportion of populations in good status	Proportion of populations in good status	Proportion of populations in good status	Proportion of populations in good status	Proportion of populations in good status	Proportion of populations in good status	Proportion of populations in good status	Proportion of populations in good status	Proportion of populations in good status	Proportion of populations in good status	Proportion of populations in good status	Proportion of populations in good status	Proportion of populations in good status
GES achieved	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES achieved by 2024	GES achieved by 2024	GES achieved by 2024	GES achieved by 2024	GES achieved by 2024	GES achieved by 2024	GES achieved by 2024	GES achieved by 2024	GES achieved by 2024	GES achieved by 2024
Description overall status	The integrated assessment of small odontocetes (NL harbour porpoise) is based on information on incidental by-catch (D1C1), population abundance (D1C2) and distributional range (D1C4). For harbour porpoise the by-catch threshold has been exceeded, therefore GES not achieved.	The integrated assessment of small odontocetes (NL harbour porpoise) is based on information on incidental by-catch (D1C1), population abundance (D1C2) and distributional range (D1C4). For harbour porpoise the by-catch threshold has been exceeded, therefore GES not achieved.	The integrated assessment of small odontocetes (NL harbour porpoise) is based on information on incidental by-catch (D1C1), population abundance (D1C2) and distributional range (D1C4). For harbour porpoise the by-catch threshold has been exceeded, therefore GES not achieved.	The integrated assessment of small odontocetes (NL harbour porpoise) is based on information on incidental by-catch (D1C1), population abundance (D1C2) and distributional range (D1C4). For harbour porpoise the by-catch threshold has been exceeded, therefore GES not achieved.	The integrated assessment of small odontocetes (NL harbour porpoise) is based on information on incidental by-catch (D1C1), population abundance (D1C2) and distributional range (D1C4). For harbour porpoise the by-catch threshold has been exceeded, therefore GES not achieved.	The integrated assessment of small odontocetes (NL harbour porpoise) is based on information on incidental by-catch (D1C1), population abundance (D1C2) and distributional range (D1C4). For harbour porpoise the by-catch threshold has been exceeded, therefore GES not achieved.	The integrated assessment of seals (NL grey seal and harbour seal) is based on information on incidental by-catch (D1C1), population abundance (D1C2), pup production (D1C3) and distributional range (D1C4). Overall, grey seal and harbour seal show an upward trend during this planning period, leading to a positive assessment and good environmental status. It remains necessary to remain alert to the status of seals, however, given the sometimes sudden population trends in the past, and - in the case of the harbour seal - a flattening of the upward trend in the assessment period. There has even been a decline in population growth since 2021.	The integrated assessment of seals (NL grey seal and harbour seal) is based on information on incidental by-catch (D1C1), population abundance (D1C2), pup production (D1C3) and distributional range (D1C4). Overall, grey seal and harbour seal show an upward trend during this planning period, leading to a positive assessment and good environmental status. It remains necessary to remain alert to the status of seals, however, given the sometimes sudden population trends in the past, and - in the case of the harbour seal - a flattening of the upward trend in the assessment period. There has even been a decline in population growth since 2021.	The integrated assessment of seals (NL grey seal and harbour seal) is based on information on incidental by-catch (D1C1), population abundance (D1C2), pup production (D1C3) and distributional range (D1C4). Overall, grey seal and harbour seal show an upward trend during this planning period, leading to a positive assessment and good environmental status. It remains necessary to remain alert to the status of seals, however, given the sometimes sudden population trends in the past, and - in the case of the harbour seal - a flattening of the upward trend in the assessment period. There has even been a decline in population growth since 2021.	The integrated assessment of seals (NL grey seal and harbour seal) is based on information on incidental by-catch (D1C1), population abundance (D1C2), pup production (D1C3) and distributional range (D1C4). Overall, grey seal and harbour seal show an upward trend during this planning period, leading to a positive assessment and good environmental status. It remains necessary to remain alert to the status of seals, however, given the sometimes sudden population trends in the past, and - in the case of the harbour seal - a flattening of the upward trend in the assessment period. There has even been a decline in population growth since 2021.	The integrated assessment of seals (NL grey seal and harbour seal) is based on information on incidental by-catch (D1C1), population abundance (D1C2), pup production (D1C3) and distributional range (D1C4). Overall, grey seal and harbour seal show an upward trend during this planning period, leading to a positive assessment and good environmental status. It remains necessary to remain alert to the status of seals, however, given the sometimes sudden population trends in the past, and - in the case of the harbour seal - a flattening of the upward trend in the assessment period. There has even been a decline in population growth since 2021.	The integrated assessment of seals (NL grey seal and harbour seal) is based on information on incidental by-catch (D1C1), population abundance (D1C2), pup production (D1C3) and distributional range (D1C4). Overall, grey seal and harbour seal show an upward trend during this planning period, leading to a positive assessment and good environmental status. It remains necessary to remain alert to the status of seals, however, given the sometimes sudden population trends in the past, and - in the case of the harbour seal - a flattening of the upward trend in the assessment period. There has even been a decline in population growth since 2021.	The integrated assessment of seals (NL grey seal and harbour seal) is based on information on incidental by-catch (D1C1), population abundance (D1C2), pup production (D1C3) and distributional range (D1C4). Overall, grey seal and harbour seal show an upward trend during this planning period, leading to a positive assessment and good environmental status. It remains necessary to remain alert to the status of seals, however, given the sometimes sudden population trends in the past, and - in the case of the harbour seal - a flattening of the upward trend in the assessment period. There has even been a decline in population growth since 2021.	The integrated assessment of seals (NL grey seal and harbour seal) is based on information on incidental by-catch (D1C1), population abundance (D1C2), pup production (D1C3) and distributional range (D1C4). Overall, grey seal and harbour seal show an upward trend during this planning period, leading to a positive assessment and good environmental status. It remains necessary to remain alert to the status of seals, however, given the sometimes sudden population trends in the past, and - in the case of the harbour seal - a flattening of the upward trend in the assessment period. There has even been a decline in population growth since 2021.	The integrated assessment of seals (NL grey seal and harbour seal) is based on information on incidental by-catch (D1C1), population abundance (D1C2), pup production (D1C3) and distributional range (D1C4). Overall, grey seal and harbour seal show an upward trend during this planning period, leading to a positive assessment and good environmental status. It remains necessary to remain alert to the status of seals, however, given the sometimes sudden population trends in the past, and - in the case of the harbour seal - a flattening of the upward trend in the assessment period. There has even been a decline in population growth since 2021.	The integrated assessment of seals (NL grey seal and harbour seal) is based on information on incidental by-catch (D1C1), population abundance (D1C2), pup production (D1C3) and distributional range (D1C4). Overall, grey seal and harbour seal show an upward trend during this planning period, leading to a positive assessment and good environmental status. It remains necessary to remain alert to the status of seals, however, given the sometimes sudden population trends in the past, and - in the case of the harbour seal - a flattening of the upward trend in the assessment period. There has even been a decline in population growth since 2021.
Assessments period	1994-2016	1994-2016	1994-2016	1994-2016	1994-2016	1994-2016	2008-2019	2008-2019	2008-2019	2008-2019	2008-2019	2008-2019	2008-2019	2008-2019	2008-2019	2008-2019
Related pressures	Disturbance of species (e.g. where they breed, rest and feed) due to human presence Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities) Input of anthropogenic sound (impulsive, continuous) Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events Physical disturbance to seabed Physical loss of the seabed	Disturbance of species (e.g. where they breed, rest and feed) due to human presence Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities) Input of anthropogenic sound (impulsive, continuous) Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events Physical disturbance to seabed Physical loss of the seabed	Disturbance of species (e.g. where they breed, rest and feed) due to human presence Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities) Input of anthropogenic sound (impulsive, continuous) Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events Physical disturbance to seabed Physical loss of the seabed	Disturbance of species (e.g. where they breed, rest and feed) due to human presence Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities) Input of anthropogenic sound (impulsive, continuous) Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events Physical disturbance to seabed Physical loss of the seabed	Disturbance of species (e.g. where they breed, rest and feed) due to human presence Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities) Input of anthropogenic sound (impulsive, continuous) Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events Physical disturbance to seabed Physical loss of the seabed	Disturbance of species (e.g. where they breed, rest and feed) due to human presence Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities) Input of anthropogenic sound (impulsive, continuous) Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events Physical disturbance to seabed Physical loss of the seabed	Disturbance of species (e.g. where they breed, rest and feed) due to human presence Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities) Input of anthropogenic sound (impulsive, continuous) Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events Physical disturbance to seabed Physical loss of the seabed	Disturbance of species (e.g. where they breed, rest and feed) due to human presence Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities) Input of anthropogenic sound (impulsive, continuous) Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events Physical disturbance to seabed Physical loss of the seabed	Disturbance of species (e.g. where they breed, rest and feed) due to human presence Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities) Input of anthropogenic sound (impulsive, continuous) Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events Physical disturbance to seabed Physical loss of the seabed	Disturbance of species (e.g. where they breed, rest and feed) due to human presence Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities) Input of anthropogenic sound (impulsive, continuous) Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events Physical disturbance to seabed Physical loss of the seabed	Disturbance of species (e.g. where they breed, rest and feed) due to human presence Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities) Input of anthropogenic sound (impulsive, continuous) Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events Physical disturbance to seabed Physical loss of the seabed	Disturbance of species (e.g. where they breed, rest and feed) due to human presence Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities) Input of anthropogenic sound (impulsive, continuous) Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events Physical disturbance to seabed Physical loss of the seabed	Disturbance of species (e.g. where they breed, rest and feed) due to human presence Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities) Input of anthropogenic sound (impulsive, continuous) Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events Physical disturbance to seabed Physical loss of the seabed	Disturbance of species (e.g. where they breed, rest and feed) due to human presence Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities) Input of anthropogenic sound (impulsive, continuous) Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events Physical disturbance to seabed Physical loss of the seabed	Disturbance of species (e.g. where they breed, rest and feed) due to human presence Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities) Input of anthropogenic sound (impulsive, continuous) Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events Physical disturbance to seabed Physical loss of the seabed	Disturbance of species (e.g. where they breed, rest and feed) due to human presence Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities) Input of anthropogenic sound (impulsive, continuous) Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) - diffuse sources, point sources, atmospheric deposition, acute events Physical disturbance to seabed Physical loss of the seabed
Related targets	ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1M-T1.10 ANSNL-D1M-T1.11 ANSNL-D1T8	ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1M-T1.10 ANSNL-D1M-T1.11 ANSNL-D1T8	ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1M-T1.10 ANSNL-D1M-T1.11 ANSNL-D1T8	ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1M-T1.10 ANSNL-D1M-T1.11 ANSNL-D1T8	ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1M-T1.10 ANSNL-D1M-T1.11 ANSNL-D1T8	ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1M-T1.10 ANSNL-D1M-T1.11 ANSNL-D1T8	ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1M-T1.10 ANSNL-D1M-T1.11 ANSNL-D1T8	ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1M-T1.10 ANSNL-D1M-T1.11 ANSNL-D1T8	ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1M-T1.10 ANSNL-D1M-T1.11 ANSNL-D1T8	ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1M-T1.10 ANSNL-D1M-T1.11 ANSNL-D1T8	ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1M-T1.10 ANSNL-D1M-T1.11 ANSNL-D1T8	ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1M-T1.10 ANSNL-D1M-T1.11 ANSNL-D1T8	ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1M-T1.10 ANSNL-D1M-T1.11 ANSNL-D1T8	ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1M-T1.10 ANSNL-D1M-T1.11 ANSNL-D1T8	ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1M-T1.10 ANSNL-D1M-T1.11 ANSNL-D1T8	ANSNL-D1M-D1B-D1F-D6/D1-T1.1 ANSNL-D1M-D1B-D1F-D6/D1-T1.2 ANSNL-D1M-D1B-D1F-D6/D1-T1.3 ANSNL-D1M-D1B-D1F-T1.4a ANSNL-D1M-D1B-D1F-T1.4b ANSNL-D1M-T1.10 ANSNL-D1M-T1.11 ANSNL-D1T8
Test TV	No	Yes	Yes	NA	NA	NA	Yes	Yes	NA	NA	NA	NA	Yes	NA	NA	NA
Test results	Correct	Correct	Correct	False	False	Correct	Correct	Correct	False	False	Correct	False	Correct	False	False	Correct