Member State report / Art10 / 2018 / D5 / 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 | D5 Eutrophication |
| Member State | Netherlands |
| Region/subregion | NE Atlantic: Greater North Sea |
| Reported by | Rijkswaterstaat Centre for Water management, Ministry of infrastructure and the environment |
| Report date | 2019-04-15 |
| Report access | XML_ART10_201904091515.xml |
Target code |
ANSNL-D5T1 |
ANSNL-D5T1 |
ANSNL-D5T1 |
ANSNL-D5T1 |
ANSNL-D5T1 |
ANSNL-D5T1 |
ANSNL-D5T1 |
ANSNL-D5T1 |
ANSNL-D5T1 |
ANSNL-D5T1 |
ANSNL-D5T1 |
ANSNL-D5T2 |
ANSNL-D5T2 |
ANSNL-D5T2 |
ANSNL-D5T2 |
ANSNL-D5T2 |
ANSNL-D5T2 |
ANSNL-D5T2 |
ANSNL-D5T2 |
ANSNL-D5T2 |
ANSNL-D5T2 |
ANSNL-D5T2 |
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Target description |
Reduce nutrient input where these do not meet the WFD objectives according to the timetable of the river basin management plans.
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Reduce nutrient input where these do not meet the WFD objectives according to the timetable of the river basin management plans.
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Reduce nutrient input where these do not meet the WFD objectives according to the timetable of the river basin management plans.
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Reduce nutrient input where these do not meet the WFD objectives according to the timetable of the river basin management plans.
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Reduce nutrient input where these do not meet the WFD objectives according to the timetable of the river basin management plans.
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Reduce nutrient input where these do not meet the WFD objectives according to the timetable of the river basin management plans.
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Reduce nutrient input where these do not meet the WFD objectives according to the timetable of the river basin management plans.
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Reduce nutrient input where these do not meet the WFD objectives according to the timetable of the river basin management plans.
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Reduce nutrient input where these do not meet the WFD objectives according to the timetable of the river basin management plans.
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Reduce nutrient input where these do not meet the WFD objectives according to the timetable of the river basin management plans.
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Reduce nutrient input where these do not meet the WFD objectives according to the timetable of the river basin management plans.
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Do not increase concentrations of nutrients that already meet the WFD standards and, if possible, reduce them further.
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Do not increase concentrations of nutrients that already meet the WFD standards and, if possible, reduce them further.
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Do not increase concentrations of nutrients that already meet the WFD standards and, if possible, reduce them further.
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Do not increase concentrations of nutrients that already meet the WFD standards and, if possible, reduce them further.
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Do not increase concentrations of nutrients that already meet the WFD standards and, if possible, reduce them further.
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Do not increase concentrations of nutrients that already meet the WFD standards and, if possible, reduce them further.
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Do not increase concentrations of nutrients that already meet the WFD standards and, if possible, reduce them further.
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Do not increase concentrations of nutrients that already meet the WFD standards and, if possible, reduce them further.
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Do not increase concentrations of nutrients that already meet the WFD standards and, if possible, reduce them further.
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Do not increase concentrations of nutrients that already meet the WFD standards and, if possible, reduce them further.
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Do not increase concentrations of nutrients that already meet the WFD standards and, if possible, reduce them further.
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Feature(s) |
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GES components |
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Timescale |
202707 |
202707 |
202707 |
202707 |
202707 |
202707 |
202707 |
202707 |
202707 |
202707 |
202707 |
202407 |
202407 |
202407 |
202407 |
202407 |
202407 |
202407 |
202407 |
202407 |
202407 |
202407 |
Update date |
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 |
Marine reporting unit |
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Element |
Chlorophyll-a |
Chlorophyll-a |
Chlorophyll-a |
DIN |
DIN |
DIN |
DIP |
DIP |
Dissolved oxygen |
Dissolved oxygen |
Dissolved oxygen |
Chlorophyll-a |
Chlorophyll-a |
Chlorophyll-a |
DIN |
DIN |
DIN |
DIP |
DIP |
Dissolved oxygen |
Dissolved oxygen |
Dissolved oxygen |
Element 2 |
KRW kust |
kustzone |
offshore |
kust |
kust (KRW) |
offshore |
kust |
offshore |
kust |
kust (KRW) |
offshore |
kust |
kust (KRW) |
offshore |
kust |
kust (KRW) |
offshore |
kust |
offshore |
kust |
kust (KRW) |
offshore |
Parameter |
Concentration in water
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Concentration in water
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Concentration in water
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Concentration in water
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Concentration in water
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Concentration in water
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Concentration in water
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Concentration in water
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Concentration in water
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Concentration in water
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Concentration in water
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Concentration in water
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Concentration in water
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Concentration in water
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Concentration in water
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Concentration in water
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Concentration in water
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Concentration in water
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Concentration in water
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Concentration in water
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Concentration in water
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Concentration in water
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Parameter - other |
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Target value |
15.0 |
4.5 |
30.0 |
0.46 |
15.0 |
0.8 |
0.8 |
6.0 |
60.0 |
6.0 |
15.0 |
4.5 |
30.0 |
0.46 |
15.0 |
0.8 |
0.8 |
6.0 |
60.0 |
6.0 |
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Value achieved - upper |
14.0 |
3.0 |
43.66 |
5.56 |
1.07 |
0.46 |
6.5 |
7.2 |
14.0 |
3.0 |
43.66 |
5.56 |
1.07 |
0.71 |
6.5 |
7.2 |
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Value achieved - lower |
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Value unit |
microgram per litre
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microgram per litre
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microgram per litre
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micromole per litre
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microgram per litre
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micromole per litre
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micromole per litre
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micromole per litre
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microgram per litre
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percentage
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milligram per litre
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microgram per litre
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microgram per litre
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microgram per litre
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micromole per litre
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milligram per litre
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micromole per litre
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micromole per litre
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micromole per litre
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milligram per litre
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percentage
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milligram per litre
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Value unit - other |
percentage saturation
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Target status |
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 achieved |
Target not yet 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 achieved |
Assessment period |
2013-2018 |
2006-2014 |
2006-2014 |
2006-2014 |
2009-2015 |
2006-2014 |
2004-2014 |
2006-2014 |
2006-2014 |
2009-2015 |
2006-2014 |
2006-2014 |
2009-2015 |
2006-2014 |
2006-2014 |
2009-2015 |
2006-2014 |
2006-2014 |
2006-2014 |
2006-2014 |
2009-2015 |
2006-2014 |
Target assessment description |
Algal biomass (established based on chlorophyll measurement) in coastal waters does not exceed the WFD reference values for the relevant coastal water types. See WFD assessment http://cdr.eionet.europa.eu/nl/eea/wise_soe/
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Algal biomass (established on the basis of chlorophyll measurements) does not exceed the objectives of OSPAR COMP for OSPAR coastal waters.
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Algal biomass (established on the basis of chlorophyll measurements does not exceed the objectives of OSPAR COMP for offshore waters.
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For the coastal waters (WFD/OSPAR), the high nitrogen concentrations can lead to the effects of eutrophication. Further at sea, due to the low concentrations that meet the assessment standard for winter nitrogen concentrations, no effects due to eutrophication are to be expected.
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For the coastal waters (WFD / OSPAR), the high nitrogen concentrations can lead to the effects of eutrophication. Further at sea, due to the low concentrations that meet the assessment standard for winter nitrogen concentrations, no effects due to eutrophication are to be expected. See http://cdr.eionet.europa.eu/nl/eea/wise_soe/
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For the coastal waters (WFD/OSPAR), the concentrations of nitrogen too high can lead to effects of eutrophication. No effects due to eutrophication are to be expected from the sea due to the low concentrations that comply with the assessment centre standard for winter nitrogen concentrations.
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For the coastal waters (WFD/OSPAR), the high nitrogen concentrations can lead to the effects of eutrophication. Further at sea, due to the low concentrations that meet the assessment standard for winter nitrogen concentrations, no effects due to eutrophication are to be expected.
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For the coastal waters (WFD/OSPAR), the concentrations of nitrogen too high can lead to effects of eutrophication. No effects due to eutrophication are to be expected from the sea due to the low concentrations that comply with the assessment centre standard for winter nitrogen concentrations.
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Major research areas in the Northern and Southern North Sea, the Channel, the Celtic Sea and the Bay of Biscay and the Iberian Coast have not observed widespread lack of oxygen
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No oxygen deficiency was observed in the Dutch coastal waters (WFD). See WFD reporting: http://cdr.eionet.europa.eu/nl/eea/wise_soe/
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Major research areas in the Northern and Southern North Sea, the Channel, the Celtic Sea and the Bay of Biscay and the Iberian Coast have not observed widespread lack of oxygen
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Algal biomass (established on the basis of chlorophyll measurements) does not exceed the objectives of OSPAR COMP for OSPAR coastal waters.
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Algal biomass (established from chlorophyll a measurement) in coastal waters is not higher than the WFD reference values for the relevant coastal water types. http://cdr.eionet.europa.eu/nl/eea/wise_soe/
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Algal biomass (established on the basis of chlorophyll measurements) does not exceed the objectives of OSPAR COMP for OSPAR coastal waters.
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For the coastal waters (WFD/OSPAR), the high nitrogen concentrations can lead to the effects of eutrophication. Further at sea, due to the low concentrations that meet the assessment standard for winter nitrogen concentrations, no effects due to eutrophication are to be expected.
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For the coastal waters (WFD/OSPAR), the high nitrogen concentrations can lead to the effects of eutrophication. See also http://cdr.eionet.europa.eu/nl/eea/wise_soe/
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For the coastal waters (WFD/OSPAR), the high nitrogen concentrations can lead to the effects of eutrophication. Further at sea, due to the low concentrations that meet the assessment standard for winter nitrogen concentrations, no effects due to eutrophication are to be expected.
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For coastal waters (WFD/OSPAR) money that the excess nitrogen concentrations can lead to effects of eutrophication.
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For the coastal waters (WFD/OSPAR), the high nitrogen concentrations can lead to the effects of eutrophication. Further at sea, due to the low concentrations that meet the assessment standard for winter nitrogen concentrations, no effects due to eutrophication are to be expected.
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Major research areas in the Northern and Southern North Sea, the Channel, the Celtic Sea and the Bay of Biscay and the Iberian Coast have not observed widespread lack of oxygen
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No oxygen deficiency was observed in the Dutch coastal waters (WFD). See WFD reporting: http://cdr.eionet.europa.eu/nl/eea/wise_soe/
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Major research areas in the Northern and Southern North Sea, the Channel, the Celtic Sea and the Bay of Biscay and the Iberian Coast have not observed widespread lack of oxygen
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Related indicator |
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Related measures |
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