Member State report / Art8 / 2018 / D5 / France / NE Atlantic: Greater North Sea

Report type Member State report to Commission
MSFD Article Art. 8 Initial assessment (and Art. 17 updates)
Report due 2018-10-15
GES Descriptor D5 Eutrophication
Member State France
Region/subregion NE Atlantic: Greater North Sea
Reported by Ministère de la transition Ecologique et Solidaire
Report date 2020-02-19
Report access ART8_GES_FR_2020-02-17.xml

ZL SRM MMN (ANS-FR-MS-MMN-LARGE)

GES component
D5
D5
D5
D5
D5
D5
D5
Feature
Eutrophication
Eutrophication
Eutrophication
Eutrophication
Eutrophication
Eutrophication
Eutrophication
Element
Nutrients (N, P)
Nutrients (N, P)
Chlorophyll-a
Transparency
Dissolved oxygen
Opportunistic macro-algae
Macrophyte communities
Element code
QE3-1-6
QE3-1-6
EEA_3164-01-0
QE3-1-1
EEA_3132-01-2
QE1-2-1
QE1-2
Element code source
Eutrophication (D5)(EQRs) http://dd.eionet.europa.eu/vocabulary/wise/ObservedPropertyBiologyEQR/view
Eutrophication (D5)(EQRs) http://dd.eionet.europa.eu/vocabulary/wise/ObservedPropertyBiologyEQR/view
Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view
Eutrophication (D5)(EQRs) http://dd.eionet.europa.eu/vocabulary/wise/ObservedPropertyBiologyEQR/view
Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view
Eutrophication (D5)(EQRs) http://dd.eionet.europa.eu/vocabulary/wise/ObservedPropertyBiologyEQR/view
Eutrophication (D5)(EQRs) http://dd.eionet.europa.eu/vocabulary/wise/ObservedPropertyBiologyEQR/view
Element 2
Element 2 code
Element 2 code source
Element source
EU
EU
EU
EU
EU
EU
EU
Criterion
D5C1
D5C1
D5C2
D5C4
D5C5
D5C6
D5C7
Parameter
Other
Other
Concentration in water
Other
Concentration in water
Parameter other
Concentration of DIN in water
Concentration of DIP in water
Turbidity of the water column
Threshold value upper
20.3
0.8
3.0
3.0
Threshold value lower
Threshold qualitative
Two thresholds were used depending on the ecotype of the mesh in question: 4 µg.l-1 for meshes in the broad zone of ecotypes NEA 1/26a (Atlantic Channel) and 6 µg.l-1 for meshes in the broad zone of ecotypes NEA 1/26b (Northern France).
Threshold value source
National
National
National
National
Water Framework Directive (2000/60/EC)
Threshold value source other
Value achieved upper
16.45
0.6
5.2
2.7
8.05
Value achieved lower
6.66
0.45
0.97
0.85
7.95
Value unit
micromole per litre
micromole per litre
microgram per litre
Other
milligram per litre
Value unit other
NTU
Proportion threshold value
Proportion value achieved
100.0
100.0
100.0
100.0
100.0
Proportion threshold value unit
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
Trend
Unknown
Unknown
Unknown
Unknown
Unknown
Parameter achieved
Unknown
Unknown
Unknown
Unknown
Unknown
Description parameter
The indicator for this parameter makes it possible to assess good nutrient status (DIN and DIP) at the scale of each coastal water body or grid box (intermediate and wide areas). In intermediate and wide areas: the parameter relating to "DIN concentration in water" is based on data from the hydrodynamic and biological model ECO-MARS3D (https://wwz.ifremer.fr/mars3d/). From these data, a metric is defined at the scale of each grid cell and corresponds to the median nitrate and DIP (phosphate) concentration for the evaluation period. The result of the metric calculation is then compared with the threshold values to determine whether or not the parameter has been reached in the grid cell in question. For example, the evaluation of the Nitrogen Element Parameter (DIN) shows that 100% of the wide area reaches the parameter. The absence of a threshold at the level of the percentage of the MRU in good condition does not make it possible to conclude whether the parameter evaluated at the MRU level has been reached.
The indicator for this parameter makes it possible to assess good nutrient status (DIN and DIP) at the scale of each coastal water body or grid box (intermediate and wide areas). In intermediate and wide areas: the parameter relating to "DIP concentration" is based on data from the hydrodynamic and biological model ECO-MARS3D (https://wwz.ifremer.fr/mars3d/). From these data, a metric is defined at the scale of each grid cell and corresponds to the median nitrate and DIP (phosphate) concentration for the evaluation period. The result of the metric calculation is then compared with the threshold values to determine whether or not the parameter has been reached in the grid cell in question. Thus, the evaluation of the parameter relating to phosphorus elements (DIP) shows that 100% of the wide area reaches the parameter. The absence of a threshold at the level of the percentage of the MRU in good condition does not make it possible to conclude whether or not the parameter evaluated at the MRU level has been reached.
In intermediate and wide areas, the parameter "concentration in water" of chlorophyll-a is based on data from satellite images (MODIS sensor). From these data, a metric is defined at the scale of each grid cell and corresponds to the 90 percentile of surface chlorophyll-a concentrations for the assessment period. The result of the calculation of the metric is then compared with the threshold values to determine whether or not the parameter has been reached in the grid cell in question. Thus, the assessment of the parameter relating to the chlorophyll-a concentration shows that 100% of the wide area reaches the parameter. The absence of a threshold at the level of the percentage of the MRU in good condition does not make it possible to conclude on whether the parameter assessed at the MRU level has been reached or not.
In intermediate and wide areas, the turbidity parameter in the water column is based on data from satellite images (MODIS sensor). From these data, a metric is defined at the scale of each grid cell and corresponds to the 90 percentile of the transparency of the water column for the evaluation period. The result of the metric calculation is then compared with the threshold values to determine whether or not the parameter has been reached in the grid box in question. Thus, the evaluation of the water transparency parameter shows that 100% of the wide area reaches the parameter. The absence of a threshold at the level of the percentage of the MRU in good condition does not make it possible to conclude on whether the parameter assessed at the MRU level has been reached or not.
In intermediate and wide areas, the parameter "dissolved oxygen concentration at the bottom" is based on data from the hydrodynamic and biological model ECO-MARS3D (https://wwz.ifremer.fr/mars3d/). From these data, a metric is defined at the scale of each grid cell and corresponds to the 10th percentile of the bottom dissolved oxygen concentrations for the assessment period. Thus, the evaluation of the parameter relating to the bottom dissolved oxygen concentration shows that 100% of the wide area reaches the parameter. The absence of a threshold at the level of the percentage of the MRU in good condition does not make it possible to conclude whether the parameter assessed at the MRU level has been reached.
Related indicator
Criteria status
Unknown
Unknown
Unknown
Unknown
Unknown
Not assessed
Not assessed
Description criteria
The evaluation of criterion D5C1 shall be carried out at the scale of each grid box considered individually. The D5C1 status of each grid cell shall be obtained by a "One Out, All Out" integration of the parameters for DIn and DIP concentrations. In the absence of a threshold for the percentage of the MRU in good condition, the status of the D5C1 criterion is therefore indicated as "unknown".
The evaluation of criterion D5C1 shall be carried out at the scale of each grid box considered individually. The D5C1 status of each grid cell shall be obtained by a "One Out, All Out" integration of the parameters for DIn and DIP concentrations. In the absence of a threshold for the percentage of the MRU in good condition, the status of the D5C1 criterion is therefore indicated as "unknown".
The evaluation of criterion D5C2 shall be carried out at the scale of each grid box considered individually. The D5C2 status of each grid cell shall be obtained directly from the assessment of the parameter relating to the chlorophyll-a concentration. In the absence of a threshold for the percentage of MRU in good condition, the status of the D5C2 criterion is therefore reported as "unknown".
The evaluation of criterion D5C4 shall be carried out at the scale of each grid box considered individually. The status of each grid cell under D5C4 is obtained directly by evaluating the water transparency parameter . If there is no threshold at the percentage level of the MRU in good condition, the status of criterion D5C4 is therefore set to "unknown".
The evaluation of criterion D5C5 shall be carried out at the scale of each grid box considered individually. The status of each cell under D5C5 is obtained directly by evaluating the parameter relating to the dissolved oxygen concentration. If there is no threshold at the percentage level of the MRU in good condition, the status of criterion D5C5 is therefore set to "unknown".
Criterion D5C6 is "Not relevant" in this MRU, relating to the broad area of the Channel - North Sea marine sub-region, as it is assessed only in the coastal zone. Indeed, opportunistic algal blooms are only expressed at the coastal level of French waters, via stranding phenomena.
Criterion D5C7 is "Not relevant" in this MRU, relating to the broad area of the Channel - North Sea marine sub-region, as it is assessed only in the coastal zone. In fact, perennial meadows and macroalgae do not develop below a certain depth (need for light), and the depth being generally proportional to the distance from the coast, most of these meadows and macroalgae populations are mainly located in the coastal zone.
Element status
Unknown
Unknown
Unknown
Unknown
Unknown
Not assessed
Not assessed
Description element
The assessment of criterion D5C1 shows that 100 % of the MRU achieves good ecological status with respect to DIN and DIP concentrations.
The assessment of criterion D5C1 shows that 100 % of the MRU achieves good ecological status with respect to DIN and DIP concentrations.
The assessment of criterion D5C2 shows that 100 % of the MRU achieves good ecological status with respect to chlrophyl a concentration.
The assessment of criterion D5C4 shows that 100 % of the MRU achieves good ecological status with respect to water transparency.
The assessment of criterion D5C5 shows that 100 % of the MRU achieves good ecological status with respect to the bottom dissolved oxygen concentration.
Integration rule type parameter
Other
Other
Other
Other
Other
Other
Other
Integration rule description parameter
The assessment of the status of criterion D5C1, at the scale of each grid cell, is obtained by integrating the two parameters relating to the NID and PID concentration. The integration method used is "One Out, All Out", which means that if one of the two parameters is not reached then the D5C1 criterion is not in good condition in the mesh considered. For the other criteria, the parameter status directly informs the corresponding criterion, no integration rule is required ("Not relevant" type).
The assessment of the status of criterion D5C1, at the scale of each grid cell, is obtained by integrating the two parameters relating to the NID and PID concentration. The integration method used is "One Out, All Out", which means that if one of the two parameters is not reached then the D5C1 criterion is not in good condition in the mesh considered. For the other criteria, the parameter status directly informs the corresponding criterion, no integration rule is required ("Not relevant" type).
The assessment of the status of criterion D5C1, at the scale of each grid cell, is obtained by integrating the two parameters relating to the NID and PID concentration. The integration method used is "One Out, All Out", which means that if one of the two parameters is not reached then the D5C1 criterion is not in good condition in the mesh considered. For the other criteria, the parameter status directly informs the corresponding criterion, no integration rule is required ("Not relevant" type).
The assessment of the status of criterion D5C1, at the scale of each grid cell, is obtained by integrating the two parameters relating to the NID and PID concentration. The integration method used is "One Out, All Out", which means that if one of the two parameters is not reached then the D5C1 criterion is not in good condition in the mesh considered. For the other criteria, the parameter status directly informs the corresponding criterion, no integration rule is required ("Not relevant" type).
The assessment of the status of criterion D5C1, at the scale of each grid cell, is obtained by integrating the two parameters relating to the NID and PID concentration. The integration method used is "One Out, All Out", which means that if one of the two parameters is not reached then the D5C1 criterion is not in good condition in the mesh considered. For the other criteria, the parameter status directly informs the corresponding criterion, no integration rule is required ("Not relevant" type).
The assessment of the status of criterion D5C1, at the scale of each grid cell, is obtained by integrating the two parameters relating to the NID and PID concentration. The integration method used is "One Out, All Out", which means that if one of the two parameters is not reached then the D5C1 criterion is not in good condition in the mesh considered. For the other criteria, the parameter status directly informs the corresponding criterion, no integration rule is required ("Not relevant" type).
The assessment of the status of criterion D5C1, at the scale of each grid cell, is obtained by integrating the two parameters relating to the NID and PID concentration. The integration method used is "One Out, All Out", which means that if one of the two parameters is not reached then the D5C1 criterion is not in good condition in the mesh considered. For the other criteria, the parameter status directly informs the corresponding criterion, no integration rule is required ("Not relevant" type).
Integration rule type criteria
HIE_WEI
HIE_WEI
HIE_WEI
HIE_WEI
HIE_WEI
HIE_WEI
HIE_WEI
Integration rule description criteria
At the level of each grid box (geographical unit of assessment), the integration of the criteria is done in two steps:1/ The first step is to give a score for each criterion on whether the GES has been achieved. Thus, a criterion for which the GES is met receives a score of 0; a criterion for which the GES is not met receives a score of 2 if it is a primary criterion and a score of 1 if it is a secondary criterion. For criterion D5C1, a score of 2 shall be given as soon as one of the phosphate or nitrate elements is downgraded ("One Out All Out").2/ The integration of the criteria is achieved, at the level of each grid cell, by adding up the scores for each criterion. Thus, if the sum of the scores is greater than or equal to 3, then the mesh considered does not reach the GES.
At the level of each grid box (geographical unit of assessment), the integration of the criteria is done in two steps:1/ The first step is to give a score for each criterion on whether the GES has been achieved. Thus, a criterion for which the GES is met receives a score of 0; a criterion for which the GES is not met receives a score of 2 if it is a primary criterion and a score of 1 if it is a secondary criterion. For criterion D5C1, a score of 2 shall be given as soon as one of the phosphate or nitrate elements is downgraded ("One Out All Out").2/ The integration of the criteria is achieved, at the level of each grid cell, by adding up the scores for each criterion. Thus, if the sum of the scores is greater than or equal to 3, then the mesh considered does not reach the GES.
At the level of each grid box (geographical unit of assessment), the integration of the criteria is done in two steps:1/ The first step is to give a score for each criterion on whether the GES has been achieved. Thus, a criterion for which the GES is met receives a score of 0; a criterion for which the GES is not met receives a score of 2 if it is a primary criterion and a score of 1 if it is a secondary criterion. For criterion D5C1, a score of 2 shall be given as soon as one of the phosphate or nitrate elements is downgraded ("One Out All Out").2/ The integration of the criteria is achieved, at the level of each grid cell, by adding up the scores for each criterion. Thus, if the sum of the scores is greater than or equal to 3, then the mesh considered does not reach the GES.
At the level of each grid box (geographical unit of assessment), the integration of the criteria is done in two steps:1/ The first step is to give a score for each criterion on whether the GES has been achieved. Thus, a criterion for which the GES is met receives a score of 0; a criterion for which the GES is not met receives a score of 2 if it is a primary criterion and a score of 1 if it is a secondary criterion. For criterion D5C1, a score of 2 shall be given as soon as one of the phosphate or nitrate elements is downgraded ("One Out All Out").2/ The integration of the criteria is achieved, at the level of each grid cell, by adding up the scores for each criterion. Thus, if the sum of the scores is greater than or equal to 3, then the mesh considered does not reach the GES.
At the level of each grid box (geographical unit of assessment), the integration of the criteria is done in two steps:1/ The first step is to give a score for each criterion on whether the GES has been achieved. Thus, a criterion for which the GES is met receives a score of 0; a criterion for which the GES is not met receives a score of 2 if it is a primary criterion and a score of 1 if it is a secondary criterion. For criterion D5C1, a score of 2 shall be given as soon as one of the phosphate or nitrate elements is downgraded ("One Out All Out").2/ The integration of the criteria is achieved, at the level of each grid cell, by adding up the scores for each criterion. Thus, if the sum of the scores is greater than or equal to 3, then the mesh considered does not reach the GES.
At the level of each grid box (geographical unit of assessment), the integration of the criteria is done in two steps:1/ The first step is to give a score for each criterion on whether the GES has been achieved. Thus, a criterion for which the GES is met receives a score of 0; a criterion for which the GES is not met receives a score of 2 if it is a primary criterion and a score of 1 if it is a secondary criterion. For criterion D5C1, a score of 2 shall be given as soon as one of the phosphate or nitrate elements is downgraded ("One Out All Out").2/ The integration of the criteria is achieved, at the level of each grid cell, by adding up the scores for each criterion. Thus, if the sum of the scores is greater than or equal to 3, then the mesh considered does not reach the GES.
At the level of each grid box (geographical unit of assessment), the integration of the criteria is done in two steps:1/ The first step is to give a score for each criterion on whether the GES has been achieved. Thus, a criterion for which the GES is met receives a score of 0; a criterion for which the GES is not met receives a score of 2 if it is a primary criterion and a score of 1 if it is a secondary criterion. For criterion D5C1, a score of 2 shall be given as soon as one of the phosphate or nitrate elements is downgraded ("One Out All Out").2/ The integration of the criteria is achieved, at the level of each grid cell, by adding up the scores for each criterion. Thus, if the sum of the scores is greater than or equal to 3, then the mesh considered does not reach the GES.
GES extent threshold
GES extent achieved
100.00
100.00
100.00
100.00
100.00
100.00
100.00
GES extent unit
Proportion of area in good status
Proportion of area in good status
Proportion of area in good status
Proportion of area in good status
Proportion of area in good status
Proportion of area in good status
Proportion of area in good status
GES achieved
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Description overall status
Achievement of good ecological status is quantitatively assessed on the basis of 4 criteria relating to the concentration of nutrients, chlorophyll-a and dissolved oxygen, as well as the transparency of the water column. The criteria relating to opportunistic macro-algae and macrophyte communities are not relevant to be assessed in this MRU. In this MRU, relating to the large area of the Channel - North Sea marine sub-region, the results of the integration of all the criteria show that 100% (i.e. 14045 km2 ) of the area achieves good status. It should be noted that 100% of the area of this MRU has been assessed. The large area does not therefore appear to be affected by eutrophication phenomena. Moreover, this assessment has been the subject of collaboration at both national and European level (adaptation of the methodologies of the joint OSPAR-COMP3 procedure). There has also been a marked improvement in the assessment methodology compared with the 2012 Initial Assessment, with the use of products from satellite images and modelling, as well as proposals for thresholds for the wider area.
Achievement of good ecological status is quantitatively assessed on the basis of 4 criteria relating to the concentration of nutrients, chlorophyll-a and dissolved oxygen, as well as the transparency of the water column. The criteria relating to opportunistic macro-algae and macrophyte communities are not relevant to be assessed in this MRU. In this MRU, relating to the large area of the Channel - North Sea marine sub-region, the results of the integration of all the criteria show that 100% (i.e. 14045 km2 ) of the area achieves good status. It should be noted that 100% of the area of this MRU has been assessed. The large area does not therefore appear to be affected by eutrophication phenomena. Moreover, this assessment has been the subject of collaboration at both national and European level (adaptation of the methodologies of the joint OSPAR-COMP3 procedure). There has also been a marked improvement in the assessment methodology compared with the 2012 Initial Assessment, with the use of products from satellite images and modelling, as well as proposals for thresholds for the wider area.
Achievement of good ecological status is quantitatively assessed on the basis of 4 criteria relating to the concentration of nutrients, chlorophyll-a and dissolved oxygen, as well as the transparency of the water column. The criteria relating to opportunistic macro-algae and macrophyte communities are not relevant to be assessed in this MRU. In this MRU, relating to the large area of the Channel - North Sea marine sub-region, the results of the integration of all the criteria show that 100% (i.e. 14045 km2 ) of the area achieves good status. It should be noted that 100% of the area of this MRU has been assessed. The large area does not therefore appear to be affected by eutrophication phenomena. Moreover, this assessment has been the subject of collaboration at both national and European level (adaptation of the methodologies of the joint OSPAR-COMP3 procedure). There has also been a marked improvement in the assessment methodology compared with the 2012 Initial Assessment, with the use of products from satellite images and modelling, as well as proposals for thresholds for the wider area.
Achievement of good ecological status is quantitatively assessed on the basis of 4 criteria relating to the concentration of nutrients, chlorophyll-a and dissolved oxygen, as well as the transparency of the water column. The criteria relating to opportunistic macro-algae and macrophyte communities are not relevant to be assessed in this MRU. In this MRU, relating to the large area of the Channel - North Sea marine sub-region, the results of the integration of all the criteria show that 100% (i.e. 14045 km2 ) of the area achieves good status. It should be noted that 100% of the area of this MRU has been assessed. The large area does not therefore appear to be affected by eutrophication phenomena. Moreover, this assessment has been the subject of collaboration at both national and European level (adaptation of the methodologies of the joint OSPAR-COMP3 procedure). There has also been a marked improvement in the assessment methodology compared with the 2012 Initial Assessment, with the use of products from satellite images and modelling, as well as proposals for thresholds for the wider area.
Achievement of good ecological status is quantitatively assessed on the basis of 4 criteria relating to the concentration of nutrients, chlorophyll-a and dissolved oxygen, as well as the transparency of the water column. The criteria relating to opportunistic macro-algae and macrophyte communities are not relevant to be assessed in this MRU. In this MRU, relating to the large area of the Channel - North Sea marine sub-region, the results of the integration of all the criteria show that 100% (i.e. 14045 km2 ) of the area achieves good status. It should be noted that 100% of the area of this MRU has been assessed. The large area does not therefore appear to be affected by eutrophication phenomena. Moreover, this assessment has been the subject of collaboration at both national and European level (adaptation of the methodologies of the joint OSPAR-COMP3 procedure). There has also been a marked improvement in the assessment methodology compared with the 2012 Initial Assessment, with the use of products from satellite images and modelling, as well as proposals for thresholds for the wider area.
Achievement of good ecological status is quantitatively assessed on the basis of 4 criteria relating to the concentration of nutrients, chlorophyll-a and dissolved oxygen, as well as the transparency of the water column. The criteria relating to opportunistic macro-algae and macrophyte communities are not relevant to be assessed in this MRU. In this MRU, relating to the large area of the Channel - North Sea marine sub-region, the results of the integration of all the criteria show that 100% (i.e. 14045 km2 ) of the area achieves good status. It should be noted that 100% of the area of this MRU has been assessed. The large area does not therefore appear to be affected by eutrophication phenomena. Moreover, this assessment has been the subject of collaboration at both national and European level (adaptation of the methodologies of the joint OSPAR-COMP3 procedure). There has also been a marked improvement in the assessment methodology compared with the 2012 Initial Assessment, with the use of products from satellite images and modelling, as well as proposals for thresholds for the wider area.
Achievement of good ecological status is quantitatively assessed on the basis of 4 criteria relating to the concentration of nutrients, chlorophyll-a and dissolved oxygen, as well as the transparency of the water column. The criteria relating to opportunistic macro-algae and macrophyte communities are not relevant to be assessed in this MRU. In this MRU, relating to the large area of the Channel - North Sea marine sub-region, the results of the integration of all the criteria show that 100% (i.e. 14045 km2 ) of the area achieves good status. It should be noted that 100% of the area of this MRU has been assessed. The large area does not therefore appear to be affected by eutrophication phenomena. Moreover, this assessment has been the subject of collaboration at both national and European level (adaptation of the methodologies of the joint OSPAR-COMP3 procedure). There has also been a marked improvement in the assessment methodology compared with the 2012 Initial Assessment, with the use of products from satellite images and modelling, as well as proposals for thresholds for the wider area.
Assessments period
2010-2016
2010-2016
2010-2016
2010-2016
2010-2016
2010-2016
2010-2016
Related pressures
Related targets

ZC SRM MMN (ANS-FR-MS-MMN-MEC2016)

GES component
D5
D5
D5
D5
D5
D5
D5
D5
Feature
Eutrophication
Eutrophication
Eutrophication
Eutrophication
Eutrophication
Eutrophication
Eutrophication
Eutrophication
Element
Nutrients (N, P)
Chlorophyll-a
Transparency
Dissolved oxygen
Opportunistic macro-algae
Macrophyte communities
Macrophyte communities
Macrophyte communities
Element code
QE3-1-6
EEA_3164-01-0
QE3-1-1
EEA_3132-01-2
QE1-2-1
QE1-2
QE1-2
QE1-2
Element code source
Eutrophication (D5)(EQRs) http://dd.eionet.europa.eu/vocabulary/wise/ObservedPropertyBiologyEQR/view
Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view
Eutrophication (D5)(EQRs) http://dd.eionet.europa.eu/vocabulary/wise/ObservedPropertyBiologyEQR/view
Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view
Eutrophication (D5)(EQRs) http://dd.eionet.europa.eu/vocabulary/wise/ObservedPropertyBiologyEQR/view
Eutrophication (D5)(EQRs) http://dd.eionet.europa.eu/vocabulary/wise/ObservedPropertyBiologyEQR/view
Eutrophication (D5)(EQRs) http://dd.eionet.europa.eu/vocabulary/wise/ObservedPropertyBiologyEQR/view
Eutrophication (D5)(EQRs) http://dd.eionet.europa.eu/vocabulary/wise/ObservedPropertyBiologyEQR/view
Element 2
Element 2 code
Element 2 code source
Element source
EU
EU
EU
EU
EU
EU
EU
EU
Criterion
D5C1
D5C2
D5C4
D5C5
D5C6
D5C7
D5C7
D5C7
Parameter
Other
Concentration in water
Other
Concentration in water
Abundance
Other
Other
Other
Parameter other
Concentration of DIN in water
Turbidity of the water column
EQR - Intertidal/mediolittoral macroalgae
EQR - Meadows
EQR - Subtidal macroalgae
Threshold value upper
29.0
3.0
0.6
Threshold value lower
Threshold qualitative
Two thresholds were used according to the ecotype of the coastal water body: 10 µg.l-1 for coastal water bodies of ecotypes NEA 1/26a (Manche-Atlantique) and 15 µg.l-1 for coastal water bodies of ecotypes NEA 1/26b (Nord de la France).
The threshold used for the coastal water body is 10 NTU (Nephelometric Turbidity Unit) for ecotypes 1 (rocky areas and Mediterranean coasts) and 45 NTU for ecotypes 3 (sandy/muddy areas and mouths of major rivers).
This parameter is based on the WFD (2000/60/EC) classification for the status of the quality element "intertidal hard substrate macroalgae" in each water body. It is achieved if the Ecological Quality Ratio (EQR) is greater than 0,6
This parameter is based on the WFD (2000/60/EC) classification for the status of the quality element "angiosperms" in each water body. It is achieved when the Ecological Quality Ratio (EQR) is greater than 0.6.
This parameter is based on the WFD (2000/60/EC) classification for the status of the quality element "subtidal macroalgae" in each water body. It is achieved when the Ecological Quality Ratio (EQR) is greater than 0,65.
Threshold value source
Water Framework Directive (2000/60/EC)
Water Framework Directive (2000/60/EC)
Water Framework Directive (2000/60/EC)
Water Framework Directive (2000/60/EC)
Water Framework Directive (2000/60/EC)
Water Framework Directive (2000/60/EC)
Water Framework Directive (2000/60/EC)
Water Framework Directive (2000/60/EC)
Threshold value source other
Value achieved upper
34.8
18.6
13.6
7.4
0.99
Value achieved lower
9.9
1.7
1.7
5.6
0.24
Value unit
micromole per litre
microgram per litre
Other
milligram per litre
Other
Value unit other
NTU
no unit
Proportion threshold value
Proportion value achieved
38.0
78.0
88.0
88.0
73.0
24.0
4.4
25.0
Proportion threshold value unit
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
Trend
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Parameter achieved
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Description parameter
The indicator for this parameter makes it possible to assess good nutrient status (DIN and DIP) at the scale of each coastal water body or grid box (intermediate and wide areas). In the coastal zone: Only DINs are assessed and the parameter is based on in situ data collected through perennial monitoring networks. From these data, a metric is defined at the scale of each coastal water body (WFD) and corresponds to the DIN concentration (nitrate + nitrite + ammonium) normalized to a salinity of 33 ‰ for the assessment period. The result of the calculation of the metric is then compared with a threshold value to determine whether or not the parameter has been reached in the coastal water body in question. 38% of the DINs in the coastal zone reach the parameter and 45% do not (coastal water bodies concerned): La Warenne-Ault, Le Havre-Antifer, Côte Fleurie, Baie de Caen, Côte de Nacre Est, Ouest Cotentin and Centre Baie du Mont Saint Michel) and 18 % is not assessed (no data acquisition in the framework of WFD monitoring). The absence of a threshold at the level of the percentage of the MRU in good condition does not make it possible to conclude on whether the parameter assessed at the MRU level has been reached or not.
Achievement of the "concentration in water" parameter for chlorophyll a is assessed at the scale of each coastal water body or grid box (intermediate and wide areas). In coastal areas: The indicator is based on in situ data collected through perennial monitoring networks. From these data, a metric is defined at the scale of each coastal water body (WFD) and corresponds to the 90 percentile of surface chlorophyll-a concentrations for the assessment period. The result of the metric calculation is then compared with a threshold value to determine whether or not the parameter has been reached in the coastal water body in question. For example, for the concentration of chlrophylla-a in the coastal zone, 78% of the zone reaches the parameter, 11% does not reach the parameter, and 11% is not assessed.The absence of a threshold at the percentage level of the MRU in good condition does not allow a conclusion to be drawn on whether the parameter assessed at the MRU level has been reached.
The transparency of the water is assessed on the basis of its turbidity level. Achievement of the water column turbidity parameter is assessed at the scale of each coastal water mass or grid cell (intermediate and wide areas). In coastal areas: The indicator is based on in situ data collected through perennial monitoring networks. From these data, a metric is defined at the scale of each coastal water mass (WFD) and corresponds to the 90 percentile of the turbidity of the water column for the assessment period. The result of the calculation of the metric is then compared with a threshold value to determine whether or not the parameter has been reached in the coastal water body in question. The evaluation of the parameter relating to the turbidity of the water column shows that the entire coastal area evaluated reaches the parameter. 12 % of the coastal zone could not be assessed. The absence of a threshold at the level of the percentage of the MRU in good condition does not make it possible to conclude on whether the parameter assessed at the MRU level has been reached or not.
Achievement of the parameter relating to the "concentration in water" of dissolved oxygen at the bottom of the water column is assessed at the scale of each coastal water mass or grid cell (intermediate and wide areas). In coastal areas: The indicator is based on in situ data collected through perennial monitoring networks. From these data, a metric is defined at the scale of each coastal water mass (WFD) and corresponds to the 10th percentile of dissolved oxygen concentrations at the bottom for the assessment period. The result of the calculation of the metric is then compared with a threshold value to determine whether or not the parameter has been reached in the coastal water mass in question. The assessment of the parameter relating to the bottom dissolved oxygen concentration shows that 88 % of the coastal zone reaches the parameter and 12 % of the coastal zone could not be assessed. The absence of a threshold at the level of the percentage of the MRU in good condition does not make it possible to conclude whether the parameter assessed at the MRU level has been reached.
Achievement of the parameter relating to the abundance of opportunistic macro-algae is achieved at the scale of each coastal water body and results in an Ecological Quality Ratio (EQR). The evaluation of this parameter shows that: 73 % of the area reaches the parameter, 5 % does not reach the parameter and 22 % is not evaluated. The three coastal water bodies that do not reach the parameter are Côte de Nacre Est, Côte de Nacre Ouest and Barfleur. The absence of a threshold for the percentage of the MRU in good condition does not allow to conclude on whether or not the parameter evaluated at the MRU level has been reached.
Achievement of the "Quality Index - Intertidal/mid-littoral macro-algae" parameter is achieved at the scale of each coastal water body and results in an Ecological Quality Ratio (EQR). The assessment of this parameter shows that: 24% of the area achieves the parameter, 4% does not achieve the parameter, 36% is not assessed, and 36% is not relevant to assess for this parameter. The absence of a threshold at the level of the percentage of MRU in good status does not make it possible to conclude on whether the parameter assessed at the scale of the MRU has been achieved or not.
Achievement of the parameter relating to the "Quality Index - Seagrasses" is carried out at the scale of each coastal water body and makes it possible to obtain an Ecological Quality Ratio (EQR). The evaluation of this parameter shows that: 4.4% of the area achieves the parameter, 13.4% does not achieve the parameter, 13.2% is not evaluated, and 69% is not relevant to evaluate for this parameter. The absence of a threshold for the percentage of MRU in good condition does not make it possible to conclude whether or not the parameter evaluated at the scale of the MRU has been achieved.
Achievement of the "Quality Index - Subtidal Macroalgae" parameter is achieved at the scale of each coastal water body and results in an Ecological Quality Ratio (EQR). The assessment of this parameter shows that: 25% of the area reaches the parameter, 14% does not reach the parameter, 32% is not assessed, and 29% is not relevant to be assessed for this parameter. The absence of a threshold for the percentage of MRU in good status does not allow to conclude on whether the parameter assessed at the MRU scale is reached or not.
Related indicator
Criteria status
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Description criteria
The assessment of criterion D5C1 shall be carried out at the scale of the individual coastal water body. The status of the water body under D5C1 is obtained directly from the assessment of the DIN concentration parameter (DIP concentrations are only determined in the intermediate and broad zones). If there is no threshold at the percentage level of the MRU in good condition, the status of criterion D5C1 is therefore set to "unknown".
The assessment of criterion D5C2 shall be carried out at the scale of the individual coastal water body. The status of the water body for D5C2 is obtained directly from the assessment of the chlorophyll-a concentration parameter. If there is no threshold at the percentage level of the MRU in good condition, the status of criterion D5C2 is therefore set to "unknown".
The assessment of criterion D5C4 is carried out at the scale of the individual coastal water body. The status of the water body under D5C4 is obtained directly from the assessment of the water transparency parameter . If there is no threshold at the percentage level of the MRU in good condition, the status of criterion D5C4 is therefore set to "unknown".
The assessment of criterion D5C5 shall be carried out at the scale of the individual coastal water body. The status of the water body under D5C5 is obtained directly from the assessment of the dissolved oxygen concentration parameter. If there is no threshold at the percentage level of the MRU in good condition, the status of criterion D5C5 is therefore set to "unknown".
The assessment of criterion D5C6 is carried out at the scale of the individual coastal water body. The status of the water body under D5C6 is obtained directly from the assessment of the parameter relating to the abundance of opportunistic macroalgae . In the absence of a threshold at the percentage level of the MRU in good condition, the status of criterion D5C6 is therefore set to "unknown".
The assessment of the D5C7 is based on a combination of several indicators used in the framework of the WFD. These WFD indicators are made up of a number of metrics allowing the calculation of an Ecological Quality Ratio (EQR). The assessment of criterion D5C7 is carried out at the scale of the individual coastal water body. The status of the water body under D5C7 is finally obtained by considering only the assessment of the parameter ("Quality Index - Subtidal Macroalgae", "Quality Index - Intertidal/Midolittoral Macroalgae" and "Quality Index - Seagrasses") with the most declining status of the coastal water body (integration of the "One Out, All Out" type). If there is no threshold for the percentage of the MRU in good condition, the status of criterion D5C7 is set to "unknown".
The assessment of the D5C7 is based on a combination of several indicators used in the framework of the WFD. These WFD indicators are made up of a number of metrics allowing the calculation of an Ecological Quality Ratio (EQR). The assessment of criterion D5C7 is carried out at the scale of the individual coastal water body. The status of the water body under D5C7 is finally obtained by considering only the assessment of the parameter ("Quality Index - Subtidal Macroalgae", "Quality Index - Intertidal/Midolittoral Macroalgae" and "Quality Index - Seagrasses") with the most declining status of the coastal water body (integration of the "One Out, All Out" type). If there is no threshold for the percentage of the MRU in good condition, the status of criterion D5C7 is set to "unknown".
The assessment of the D5C7 is based on a combination of several indicators used in the framework of the WFD. These WFD indicators are made up of a number of metrics allowing the calculation of an Ecological Quality Ratio (EQR). The assessment of criterion D5C7 is carried out at the scale of the individual coastal water body. The status of the water body under D5C7 is finally obtained by considering only the assessment of the parameter ("Quality Index - Subtidal Macroalgae", "Quality Index - Intertidal/Midolittoral Macroalgae" and "Quality Index - Seagrasses") with the most declining status of the coastal water body (integration of the "One Out, All Out" type). If there is no threshold for the percentage of the MRU in good condition, the status of criterion D5C7 is set to "unknown".
Element status
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Description element
The assessment of criterion D5C1 shows that for DIN concentrations: 45 % of the MRU (i.e. 1076 km2 ) does not achieve good ecological status, 38 % of the MRU (i.e. 917 km2 ) achieves good ecological status and 18 % of the MRU (i.e. 424 km2 ) is not assessed.
The assessment of criterion D5C2 shows that for chlorophyll-a concentrations: 11 % of the MRU (267 km2 ) does not achieve good ecological status, 78 % of the MRU (1886 km2 ) achieves good ecological status and 11 % of the MRU (264 km2 ) is not assessed.
The assessment of criterion D5C4 shows that for turbidity 88 % of the MRU (2137 km2 ) achieves good ecological status and 12 % of the MRU (280 km2 ) is not assessed.
The assessment of criterion D5C5 shows that for bottom dissolved oxygen concentrations: 88 % of the MRU (2137 km2 ) achieves good ecological status and 12 % of the MRU (280 km2 ) is not assessed.
The assessment of criterion D5C6 shows that for the abundance of opportunistic macroalgae: 5 % of the MRU (117 km2 ) does not achieve good ecological status, 73 % of the MRU (1772 km2 ) achieves good ecological status, and 22 % of the MRU (528 km2 ) is not assessed.
The assessment of criterion D5C7 shows that for the abundance of perennial macroalgae and sea grass: 36 % of the MRU (871 km2 ) does not achieve good ecological status, 12 % of the MRU (286 km2 ) achieves good ecological status, 20 % of the MRU (486 km2 ) is not relevant for this criterion, and 32 % of the MRU (774 km2 ) is not assessed.
The assessment of criterion D5C7 shows that for the abundance of perennial macroalgae and sea grass: 36 % of the MRU (871 km2 ) does not achieve good ecological status, 12 % of the MRU (286 km2 ) achieves good ecological status, 20 % of the MRU (486 km2 ) is not relevant for this criterion, and 32 % of the MRU (774 km2 ) is not assessed.
The assessment of criterion D5C7 shows that for the abundance of perennial macroalgae and sea grass: 36 % of the MRU (871 km2 ) does not achieve good ecological status, 12 % of the MRU (286 km2 ) achieves good ecological status, 20 % of the MRU (486 km2 ) is not relevant for this criterion, and 32 % of the MRU (774 km2 ) is not assessed.
Integration rule type parameter
Other
Other
Other
Other
Other
Other
Other
Other
Integration rule description parameter
The assessment of criterion D5C7 is carried out at the scale of the individual coastal water body. The status of the water body under D5C7 is obtained by a "One Out, All Out" integration between the three parameters "Quality Index - Subtidal Macroalgae", "Quality Index - Intertidal/Middle-littoral Macroalgae" and "Quality Index - Herbarium". For the other criteria, the parameter status directly informs the corresponding criterion, no integration rule is required ("Not relevant" type).
The assessment of criterion D5C7 is carried out at the scale of the individual coastal water body. The status of the water body under D5C7 is obtained by a "One Out, All Out" integration between the three parameters "Quality Index - Subtidal Macroalgae", "Quality Index - Intertidal/Middle-littoral Macroalgae" and "Quality Index - Herbarium". For the other criteria, the parameter status directly informs the corresponding criterion, no integration rule is required ("Not relevant" type).
The assessment of criterion D5C7 is carried out at the scale of the individual coastal water body. The status of the water body under D5C7 is obtained by a "One Out, All Out" integration between the three parameters "Quality Index - Subtidal Macroalgae", "Quality Index - Intertidal/Middle-littoral Macroalgae" and "Quality Index - Herbarium". For the other criteria, the parameter status directly informs the corresponding criterion, no integration rule is required ("Not relevant" type).
The assessment of criterion D5C7 is carried out at the scale of the individual coastal water body. The status of the water body under D5C7 is obtained by a "One Out, All Out" integration between the three parameters "Quality Index - Subtidal Macroalgae", "Quality Index - Intertidal/Middle-littoral Macroalgae" and "Quality Index - Herbarium". For the other criteria, the parameter status directly informs the corresponding criterion, no integration rule is required ("Not relevant" type).
The assessment of criterion D5C7 is carried out at the scale of the individual coastal water body. The status of the water body under D5C7 is obtained by a "One Out, All Out" integration between the three parameters "Quality Index - Subtidal Macroalgae", "Quality Index - Intertidal/Middle-littoral Macroalgae" and "Quality Index - Herbarium". For the other criteria, the parameter status directly informs the corresponding criterion, no integration rule is required ("Not relevant" type).
The assessment of criterion D5C7 is carried out at the scale of the individual coastal water body. The status of the water body under D5C7 is obtained by a "One Out, All Out" integration between the three parameters "Quality Index - Subtidal Macroalgae", "Quality Index - Intertidal/Middle-littoral Macroalgae" and "Quality Index - Herbarium". For the other criteria, the parameter status directly informs the corresponding criterion, no integration rule is required ("Not relevant" type).
The assessment of criterion D5C7 is carried out at the scale of the individual coastal water body. The status of the water body under D5C7 is obtained by a "One Out, All Out" integration between the three parameters "Quality Index - Subtidal Macroalgae", "Quality Index - Intertidal/Middle-littoral Macroalgae" and "Quality Index - Herbarium". For the other criteria, the parameter status directly informs the corresponding criterion, no integration rule is required ("Not relevant" type).
The assessment of criterion D5C7 is carried out at the scale of the individual coastal water body. The status of the water body under D5C7 is obtained by a "One Out, All Out" integration between the three parameters "Quality Index - Subtidal Macroalgae", "Quality Index - Intertidal/Middle-littoral Macroalgae" and "Quality Index - Herbarium". For the other criteria, the parameter status directly informs the corresponding criterion, no integration rule is required ("Not relevant" type).
Integration rule type criteria
HIE_WEI
HIE_WEI
HIE_WEI
HIE_WEI
HIE_WEI
HIE_WEI
HIE_WEI
HIE_WEI
Integration rule description criteria
At the level of each coastal water body (geographical unit of assessment), the integration of criteria is carried out in two stages:1/ The first stage consists in assigning a mark for each criterion as to whether or not good status has been achieved. Thus, a criterion for which the good condition is reached receives a score of 0, a criterion for which the good condition is not reached receives a score of 2 if it is a primary criterion and 1 if it is a secondary criterion. For criterion D5C1, a score of 2 shall be assigned as soon as one of the phosphate or nitrate elements is downgraded ("One Out All Out").2/ The integration of the criteria is achieved, for each coastal water body, by adding up the scores for each criterion. Thus, if the sum of the scores is greater than or equal to 5, then the coastal water body in question is not in good condition. Note that if good status is not achieved for criterion D5C6, then the coastal water body in question is systematically downgraded.
At the level of each coastal water body (geographical unit of assessment), the integration of criteria is carried out in two stages:1/ The first stage consists in assigning a mark for each criterion as to whether or not good status has been achieved. Thus, a criterion for which the good condition is reached receives a score of 0, a criterion for which the good condition is not reached receives a score of 2 if it is a primary criterion and 1 if it is a secondary criterion. For criterion D5C1, a score of 2 shall be assigned as soon as one of the phosphate or nitrate elements is downgraded ("One Out All Out").2/ The integration of the criteria is achieved, for each coastal water body, by adding up the scores for each criterion. Thus, if the sum of the scores is greater than or equal to 5, then the coastal water body in question is not in good condition. Note that if good status is not achieved for criterion D5C6, then the coastal water body in question is systematically downgraded.
At the level of each coastal water body (geographical unit of assessment), the integration of criteria is carried out in two stages:1/ The first stage consists in assigning a mark for each criterion as to whether or not good status has been achieved. Thus, a criterion for which the good condition is reached receives a score of 0, a criterion for which the good condition is not reached receives a score of 2 if it is a primary criterion and 1 if it is a secondary criterion. For criterion D5C1, a score of 2 shall be assigned as soon as one of the phosphate or nitrate elements is downgraded ("One Out All Out").2/ The integration of the criteria is achieved, for each coastal water body, by adding up the scores for each criterion. Thus, if the sum of the scores is greater than or equal to 5, then the coastal water body in question is not in good condition. Note that if good status is not achieved for criterion D5C6, then the coastal water body in question is systematically downgraded.
At the level of each coastal water body (geographical unit of assessment), the integration of criteria is carried out in two stages:1/ The first stage consists in assigning a mark for each criterion as to whether or not good status has been achieved. Thus, a criterion for which the good condition is reached receives a score of 0, a criterion for which the good condition is not reached receives a score of 2 if it is a primary criterion and 1 if it is a secondary criterion. For criterion D5C1, a score of 2 shall be assigned as soon as one of the phosphate or nitrate elements is downgraded ("One Out All Out").2/ The integration of the criteria is achieved, for each coastal water body, by adding up the scores for each criterion. Thus, if the sum of the scores is greater than or equal to 5, then the coastal water body in question is not in good condition. Note that if good status is not achieved for criterion D5C6, then the coastal water body in question is systematically downgraded.
At the level of each coastal water body (geographical unit of assessment), the integration of criteria is carried out in two stages:1/ The first stage consists in assigning a mark for each criterion as to whether or not good status has been achieved. Thus, a criterion for which the good condition is reached receives a score of 0, a criterion for which the good condition is not reached receives a score of 2 if it is a primary criterion and 1 if it is a secondary criterion. For criterion D5C1, a score of 2 shall be assigned as soon as one of the phosphate or nitrate elements is downgraded ("One Out All Out").2/ The integration of the criteria is achieved, for each coastal water body, by adding up the scores for each criterion. Thus, if the sum of the scores is greater than or equal to 5, then the coastal water body in question is not in good condition. Note that if good status is not achieved for criterion D5C6, then the coastal water body in question is systematically downgraded.
At the level of each coastal water body (geographical unit of assessment), the integration of criteria is carried out in two stages:1/ The first stage consists in assigning a mark for each criterion as to whether or not good status has been achieved. Thus, a criterion for which the good condition is reached receives a score of 0, a criterion for which the good condition is not reached receives a score of 2 if it is a primary criterion and 1 if it is a secondary criterion. For criterion D5C1, a score of 2 shall be assigned as soon as one of the phosphate or nitrate elements is downgraded ("One Out All Out").2/ The integration of the criteria is achieved, for each coastal water body, by adding up the scores for each criterion. Thus, if the sum of the scores is greater than or equal to 5, then the coastal water body in question is not in good condition. Note that if good status is not achieved for criterion D5C6, then the coastal water body in question is systematically downgraded.
At the level of each coastal water body (geographical unit of assessment), the integration of criteria is carried out in two stages:1/ The first stage consists in assigning a mark for each criterion as to whether or not good status has been achieved. Thus, a criterion for which the good condition is reached receives a score of 0, a criterion for which the good condition is not reached receives a score of 2 if it is a primary criterion and 1 if it is a secondary criterion. For criterion D5C1, a score of 2 shall be assigned as soon as one of the phosphate or nitrate elements is downgraded ("One Out All Out").2/ The integration of the criteria is achieved, for each coastal water body, by adding up the scores for each criterion. Thus, if the sum of the scores is greater than or equal to 5, then the coastal water body in question is not in good condition. Note that if good status is not achieved for criterion D5C6, then the coastal water body in question is systematically downgraded.
At the level of each coastal water body (geographical unit of assessment), the integration of criteria is carried out in two stages:1/ The first stage consists in assigning a mark for each criterion as to whether or not good status has been achieved. Thus, a criterion for which the good condition is reached receives a score of 0, a criterion for which the good condition is not reached receives a score of 2 if it is a primary criterion and 1 if it is a secondary criterion. For criterion D5C1, a score of 2 shall be assigned as soon as one of the phosphate or nitrate elements is downgraded ("One Out All Out").2/ The integration of the criteria is achieved, for each coastal water body, by adding up the scores for each criterion. Thus, if the sum of the scores is greater than or equal to 5, then the coastal water body in question is not in good condition. Note that if good status is not achieved for criterion D5C6, then the coastal water body in question is systematically downgraded.
GES extent threshold
GES extent achieved
87.00
87.00
87.00
87.00
87.00
87.00
87.00
87.00
GES extent unit
Proportion of area in good status
Proportion of area in good status
Proportion of area in good status
Proportion of area in good status
Proportion of area in good status
Proportion of area in good status
Proportion of area in good status
Proportion of area in good status
GES achieved
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Description overall status
The achievement of good ecological status for descriptor 5 is quantitatively assessed on the basis of 6 criteria relating to the concentration of nutrients, chlorophyll-a and dissolved oxygen, as well as to the transparency of the water column, opportunistic macro-algae and macrophyte communities. In this MRU, relating to the coastal zone of the Channel - North Sea marine sub-region, the results of the integration of all the criteria show that 87.5% (i.e. 2117 km2 ) of the area achieves good status. On the other hand, 5% (i.e. 117 km2 ) of the area of the MRU does not achieve good status and 7.5% (i.e. 183 km2 ) of the area has not been assessed. On reading the results by criterion, it appears that eutrophication problems are associated with the combined action of high nutrient and chlorophyll-a concentrations in the Somme and Seine estuaries. Indeed, there are still significant nutrient fluxes in these two rivers, with a stagnation or a significant increase in nitrate fluxes since the 1990s (and a decrease in phosphates). The absence of eutrophication problems between these two areas may be due to the dilution of the Seine plume at the level of the Normandy flowered coast. Moreover, the results show that macroalgae strandings lead to the failure to achieve good status for some Normandy coastal water masses located in the Seine Bay, and therefore under the potential influence of its discharges. Moreover, this assessment has been the subject of collaboration at both national and European level (adaptation of the methodologies of the joint OSPAR-COMP3 procedure). There has also been a clear improvement in the assessment methodology compared with the 2012 Initial Assessment.
The achievement of good ecological status for descriptor 5 is quantitatively assessed on the basis of 6 criteria relating to the concentration of nutrients, chlorophyll-a and dissolved oxygen, as well as to the transparency of the water column, opportunistic macro-algae and macrophyte communities. In this MRU, relating to the coastal zone of the Channel - North Sea marine sub-region, the results of the integration of all the criteria show that 87.5% (i.e. 2117 km2 ) of the area achieves good status. On the other hand, 5% (i.e. 117 km2 ) of the area of the MRU does not achieve good status and 7.5% (i.e. 183 km2 ) of the area has not been assessed. On reading the results by criterion, it appears that eutrophication problems are associated with the combined action of high nutrient and chlorophyll-a concentrations in the Somme and Seine estuaries. Indeed, there are still significant nutrient fluxes in these two rivers, with a stagnation or a significant increase in nitrate fluxes since the 1990s (and a decrease in phosphates). The absence of eutrophication problems between these two areas may be due to the dilution of the Seine plume at the level of the Normandy flowered coast. Moreover, the results show that macroalgae strandings lead to the failure to achieve good status for some Normandy coastal water masses located in the Seine Bay, and therefore under the potential influence of its discharges. Moreover, this assessment has been the subject of collaboration at both national and European level (adaptation of the methodologies of the joint OSPAR-COMP3 procedure). There has also been a clear improvement in the assessment methodology compared with the 2012 Initial Assessment.
The achievement of good ecological status for descriptor 5 is quantitatively assessed on the basis of 6 criteria relating to the concentration of nutrients, chlorophyll-a and dissolved oxygen, as well as to the transparency of the water column, opportunistic macro-algae and macrophyte communities. In this MRU, relating to the coastal zone of the Channel - North Sea marine sub-region, the results of the integration of all the criteria show that 87.5% (i.e. 2117 km2 ) of the area achieves good status. On the other hand, 5% (i.e. 117 km2 ) of the area of the MRU does not achieve good status and 7.5% (i.e. 183 km2 ) of the area has not been assessed. On reading the results by criterion, it appears that eutrophication problems are associated with the combined action of high nutrient and chlorophyll-a concentrations in the Somme and Seine estuaries. Indeed, there are still significant nutrient fluxes in these two rivers, with a stagnation or a significant increase in nitrate fluxes since the 1990s (and a decrease in phosphates). The absence of eutrophication problems between these two areas may be due to the dilution of the Seine plume at the level of the Normandy flowered coast. Moreover, the results show that macroalgae strandings lead to the failure to achieve good status for some Normandy coastal water masses located in the Seine Bay, and therefore under the potential influence of its discharges. Moreover, this assessment has been the subject of collaboration at both national and European level (adaptation of the methodologies of the joint OSPAR-COMP3 procedure). There has also been a clear improvement in the assessment methodology compared with the 2012 Initial Assessment.
The achievement of good ecological status for descriptor 5 is quantitatively assessed on the basis of 6 criteria relating to the concentration of nutrients, chlorophyll-a and dissolved oxygen, as well as to the transparency of the water column, opportunistic macro-algae and macrophyte communities. In this MRU, relating to the coastal zone of the Channel - North Sea marine sub-region, the results of the integration of all the criteria show that 87.5% (i.e. 2117 km2 ) of the area achieves good status. On the other hand, 5% (i.e. 117 km2 ) of the area of the MRU does not achieve good status and 7.5% (i.e. 183 km2 ) of the area has not been assessed. On reading the results by criterion, it appears that eutrophication problems are associated with the combined action of high nutrient and chlorophyll-a concentrations in the Somme and Seine estuaries. Indeed, there are still significant nutrient fluxes in these two rivers, with a stagnation or a significant increase in nitrate fluxes since the 1990s (and a decrease in phosphates). The absence of eutrophication problems between these two areas may be due to the dilution of the Seine plume at the level of the Normandy flowered coast. Moreover, the results show that macroalgae strandings lead to the failure to achieve good status for some Normandy coastal water masses located in the Seine Bay, and therefore under the potential influence of its discharges. Moreover, this assessment has been the subject of collaboration at both national and European level (adaptation of the methodologies of the joint OSPAR-COMP3 procedure). There has also been a clear improvement in the assessment methodology compared with the 2012 Initial Assessment.
The achievement of good ecological status for descriptor 5 is quantitatively assessed on the basis of 6 criteria relating to the concentration of nutrients, chlorophyll-a and dissolved oxygen, as well as to the transparency of the water column, opportunistic macro-algae and macrophyte communities. In this MRU, relating to the coastal zone of the Channel - North Sea marine sub-region, the results of the integration of all the criteria show that 87.5% (i.e. 2117 km2 ) of the area achieves good status. On the other hand, 5% (i.e. 117 km2 ) of the area of the MRU does not achieve good status and 7.5% (i.e. 183 km2 ) of the area has not been assessed. On reading the results by criterion, it appears that eutrophication problems are associated with the combined action of high nutrient and chlorophyll-a concentrations in the Somme and Seine estuaries. Indeed, there are still significant nutrient fluxes in these two rivers, with a stagnation or a significant increase in nitrate fluxes since the 1990s (and a decrease in phosphates). The absence of eutrophication problems between these two areas may be due to the dilution of the Seine plume at the level of the Normandy flowered coast. Moreover, the results show that macroalgae strandings lead to the failure to achieve good status for some Normandy coastal water masses located in the Seine Bay, and therefore under the potential influence of its discharges. Moreover, this assessment has been the subject of collaboration at both national and European level (adaptation of the methodologies of the joint OSPAR-COMP3 procedure). There has also been a clear improvement in the assessment methodology compared with the 2012 Initial Assessment.
The achievement of good ecological status for descriptor 5 is quantitatively assessed on the basis of 6 criteria relating to the concentration of nutrients, chlorophyll-a and dissolved oxygen, as well as to the transparency of the water column, opportunistic macro-algae and macrophyte communities. In this MRU, relating to the coastal zone of the Channel - North Sea marine sub-region, the results of the integration of all the criteria show that 87.5% (i.e. 2117 km2 ) of the area achieves good status. On the other hand, 5% (i.e. 117 km2 ) of the area of the MRU does not achieve good status and 7.5% (i.e. 183 km2 ) of the area has not been assessed. On reading the results by criterion, it appears that eutrophication problems are associated with the combined action of high nutrient and chlorophyll-a concentrations in the Somme and Seine estuaries. Indeed, there are still significant nutrient fluxes in these two rivers, with a stagnation or a significant increase in nitrate fluxes since the 1990s (and a decrease in phosphates). The absence of eutrophication problems between these two areas may be due to the dilution of the Seine plume at the level of the Normandy flowered coast. Moreover, the results show that macroalgae strandings lead to the failure to achieve good status for some Normandy coastal water masses located in the Seine Bay, and therefore under the potential influence of its discharges. Moreover, this assessment has been the subject of collaboration at both national and European level (adaptation of the methodologies of the joint OSPAR-COMP3 procedure). There has also been a clear improvement in the assessment methodology compared with the 2012 Initial Assessment.
The achievement of good ecological status for descriptor 5 is quantitatively assessed on the basis of 6 criteria relating to the concentration of nutrients, chlorophyll-a and dissolved oxygen, as well as to the transparency of the water column, opportunistic macro-algae and macrophyte communities. In this MRU, relating to the coastal zone of the Channel - North Sea marine sub-region, the results of the integration of all the criteria show that 87.5% (i.e. 2117 km2 ) of the area achieves good status. On the other hand, 5% (i.e. 117 km2 ) of the area of the MRU does not achieve good status and 7.5% (i.e. 183 km2 ) of the area has not been assessed. On reading the results by criterion, it appears that eutrophication problems are associated with the combined action of high nutrient and chlorophyll-a concentrations in the Somme and Seine estuaries. Indeed, there are still significant nutrient fluxes in these two rivers, with a stagnation or a significant increase in nitrate fluxes since the 1990s (and a decrease in phosphates). The absence of eutrophication problems between these two areas may be due to the dilution of the Seine plume at the level of the Normandy flowered coast. Moreover, the results show that macroalgae strandings lead to the failure to achieve good status for some Normandy coastal water masses located in the Seine Bay, and therefore under the potential influence of its discharges. Moreover, this assessment has been the subject of collaboration at both national and European level (adaptation of the methodologies of the joint OSPAR-COMP3 procedure). There has also been a clear improvement in the assessment methodology compared with the 2012 Initial Assessment.
The achievement of good ecological status for descriptor 5 is quantitatively assessed on the basis of 6 criteria relating to the concentration of nutrients, chlorophyll-a and dissolved oxygen, as well as to the transparency of the water column, opportunistic macro-algae and macrophyte communities. In this MRU, relating to the coastal zone of the Channel - North Sea marine sub-region, the results of the integration of all the criteria show that 87.5% (i.e. 2117 km2 ) of the area achieves good status. On the other hand, 5% (i.e. 117 km2 ) of the area of the MRU does not achieve good status and 7.5% (i.e. 183 km2 ) of the area has not been assessed. On reading the results by criterion, it appears that eutrophication problems are associated with the combined action of high nutrient and chlorophyll-a concentrations in the Somme and Seine estuaries. Indeed, there are still significant nutrient fluxes in these two rivers, with a stagnation or a significant increase in nitrate fluxes since the 1990s (and a decrease in phosphates). The absence of eutrophication problems between these two areas may be due to the dilution of the Seine plume at the level of the Normandy flowered coast. Moreover, the results show that macroalgae strandings lead to the failure to achieve good status for some Normandy coastal water masses located in the Seine Bay, and therefore under the potential influence of its discharges. Moreover, this assessment has been the subject of collaboration at both national and European level (adaptation of the methodologies of the joint OSPAR-COMP3 procedure). There has also been a clear improvement in the assessment methodology compared with the 2012 Initial Assessment.
Assessments period
2010-2015
2010-2015
2010-2015
2010-2015
2010-2015
2010-2015
2010-2015
2010-2015
Related pressures
Related targets

ZI SRM MMN (ANS-FR-MS-MMN-ZI)

GES component
D5
D5
D5
D5
D5
D5
D5
Feature
Eutrophication
Eutrophication
Eutrophication
Eutrophication
Eutrophication
Eutrophication
Eutrophication
Element
Nutrients (N, P)
Nutrients (N, P)
Chlorophyll-a
Transparency
Dissolved oxygen
Opportunistic macro-algae
Macrophyte communities
Element code
QE3-1-6
QE3-1-6
EEA_3164-01-0
QE3-1-1
EEA_3132-01-2
QE1-2-1
QE1-2
Element code source
Eutrophication (D5)(EQRs) http://dd.eionet.europa.eu/vocabulary/wise/ObservedPropertyBiologyEQR/view
Eutrophication (D5)(EQRs) http://dd.eionet.europa.eu/vocabulary/wise/ObservedPropertyBiologyEQR/view
Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view
Eutrophication (D5)(EQRs) http://dd.eionet.europa.eu/vocabulary/wise/ObservedPropertyBiologyEQR/view
Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view
Eutrophication (D5)(EQRs) http://dd.eionet.europa.eu/vocabulary/wise/ObservedPropertyBiologyEQR/view
Eutrophication (D5)(EQRs) http://dd.eionet.europa.eu/vocabulary/wise/ObservedPropertyBiologyEQR/view
Element 2
Element 2 code
Element 2 code source
Element source
EU
EU
EU
EU
EU
EU
EU
Criterion
D5C1
D5C1
D5C2
D5C4
D5C5
D5C6
D5C7
Parameter
Other
Other
Concentration in water
Other
Concentration in water
Parameter other
Concentration of DIN in water
Concentration of DIP in water
Turbidity of the water column
Threshold value upper
24.65
0.8
7.0
3.0
Threshold value lower
Threshold qualitative
The threshold used is 5 µg.l-1 for meshes in the intermediate zone of ecotypes NEA 1/26a (Atlantic Channel) and 7,5 µg.l-1 for meshes in the intermediate zone of ecotypes NEA 1/26b (Northern France).
Threshold value source
National
National
National
National
Water Framework Directive (2000/60/EC)
Threshold value source other
Value achieved upper
57.2
1.54
14.4
16.5
7.85
Value achieved lower
7.44
0.45
0.9
0.97
6.8
Value unit
micromole per litre
micromole per litre
microgram per litre
Other
milligram per litre
Value unit other
NTU
Proportion threshold value
Proportion value achieved
72.0
82.0
78.0
99.5
100.0
Proportion threshold value unit
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
% area of MRU achieving threshold value
Trend
Unknown
Unknown
Unknown
Unknown
Unknown
Parameter achieved
Unknown
Unknown
Unknown
Unknown
Unknown
Description parameter
The indicator for this parameter makes it possible to assess good nutrient status (DIN and DIP) at the scale of each coastal water body or grid box (intermediate and wide areas). In intermediate and wide areas: the parameter relating to "DIN concentration in water" is based on data from the hydrodynamic and biological model ECO-MARS3D (https://wwz.ifremer.fr/mars3d/). From these data, a metric is defined at the scale of each grid cell and corresponds to the median nitrate and DIP (phosphate) concentration for the evaluation period. The result of the metric calculation is then compared with the threshold values to determine whether or not the parameter has been reached in the grid cell in question. For the intermediate zone for DINs, 72% of the zone reaches the parameter and 28% does not reach the parameter. The area not reaching the parameter corresponds to a band relatively close to the coast, similar to the so-called coastal river. The absence of a threshold at the level of the percentage of the MRU in good condition does not make it possible to conclude whether or not the parameter assessed at the MRU level has been reached.
The indicator for this parameter makes it possible to assess good nutrient status (DIN and DIP) at the scale of each coastal water body or grid box (intermediate and wide areas). In intermediate and wide areas: the parameter relating to "DIP concentration" is based on data from the hydrodynamic and biological model ECO-MARS3D (https://wwz.ifremer.fr/mars3d/). From these data, a metric is defined at the scale of each grid cell and corresponds to the median nitrate and DIP (phosphate) concentration for the evaluation period. The result of the metric calculation is then compared with the threshold values to determine whether or not the parameter has been reached in the grid cell in question. Concerning the intermediate zone for DIP, 82% of the intermediate zone reaches the parameter while 18% does not reach the parameter. The area not reaching the parameter corresponds to a band relatively close to the coast, similar to the so-called coastal river. The absence of a threshold at the level of the percentage of the MRU in good condition does not make it possible to conclude whether or not the parameter assessed at the MRU level has been reached.
In intermediate and wide areas, the parameter "concentration in water" of chlorophyll-a is based on data from satellite images (MODIS sensor). From these data, a metric is defined at the scale of each grid cell and corresponds to the 90 percentile of surface chlorophyll-a concentrations for the evaluation period. The result of the calculation of the metric is then compared with the threshold values to determine whether or not the parameter has been reached in the grid cell in question. For example, chlrophylla-a concentrations in the intermediate zone show that 78% of the zone meets the parameter and 22% does not meet the parameter. Two areas do not reach the parameter, the first extends from the Bay of the Somme to the North Sea (1,700 km²) and the second is located in the Bay of the Seine (902 km²). The absence of a threshold in terms of the percentage of the MRU in good condition does not make it possible to conclude whether or not the parameter assessed at the MRU level has been reached.
In intermediate and wide areas, the turbidity parameter in the water column is based on data from satellite images (MODIS sensor). From these data, a metric is defined at the scale of each grid cell and corresponds to the 90 percentile of the transparency of the water column for the evaluation period. The result of the metric calculation is then compared with the threshold values to determine whether or not the parameter has been reached in the grid box in question. Thus, the evaluation of the parameter relating to the turbidity of the water column shows that 99.5% of the intermediate zone reaches the parameter and that 0.5% does not reach the parameter at the outlet of the Seine estuary. The absence of a threshold at the level of the percentage of the MRU in good condition does not make it possible to conclude whether or not the parameter evaluated at the MRU level has been reached.
In intermediate and wide areas, the parameter "dissolved oxygen concentration at the bottom" is based on data from the hydrodynamic and biological model ECO-MARS3D (https://wwz.ifremer.fr/mars3d/). From these data, a metric is defined at the scale of each grid cell and corresponds to the 10th percentile of the bottom dissolved oxygen concentrations for the assessment period. Thus, the evaluation of the parameter relating to the bottom dissolved oxygen concentration shows that 100% of the intermediate zone reaches the parameter. The absence of a threshold at the percentage level of the MRU in good condition does not make it possible to conclude whether the parameter assessed at the MRU level has been reached.
Related indicator
Criteria status
Unknown
Unknown
Unknown
Unknown
Unknown
Not assessed
Not assessed
Description criteria
The evaluation of criterion D5C1 shall be carried out at the scale of each grid box considered individually. The D5C1 status of each grid cell shall be obtained by a "One Out, All Out" integration of the parameters for DIn and DIP concentrations. In the absence of a threshold for the percentage of the MRU in good condition, the status of the D5C1 criterion is therefore indicated as "unknown".
The evaluation of criterion D5C1 shall be carried out at the scale of each grid box considered individually. The D5C1 status of each grid cell shall be obtained by a "One Out, All Out" integration of the parameters for DIn and DIP concentrations. In the absence of a threshold for the percentage of the MRU in good condition, the status of the D5C1 criterion is therefore indicated as "unknown".
The evaluation of criterion D5C2 shall be carried out at the scale of each grid box considered individually. The D5C2 status of each grid cell shall be obtained directly from the assessment of the parameter relating to the chlorophyll-a concentration. In the absence of a threshold for the percentage of MRU in good condition, the status of the D5C2 criterion is therefore reported as "unknown".
The evaluation of criterion D5C4 shall be carried out at the scale of each grid box considered individually. The status of each grid cell under D5C4 is obtained directly by evaluating the water transparency parameter . If there is no threshold at the percentage level of the MRU in good condition, the status of criterion D5C4 is therefore set to "unknown".
The evaluation of criterion D5C5 shall be carried out at the scale of each grid box considered individually. The status of each cell under D5C5 is obtained directly by evaluating the parameter relating to the dissolved oxygen concentration. If there is no threshold at the percentage level of the MRU in good condition, the status of criterion D5C5 is therefore set to "unknown".
Criterion D5C6 is "Not relevant" in this MRU, relating to the intermediate area of the Channel - North Sea marine sub-region, as it is assessed only in the coastal zone. Indeed, opportunistic algal blooms are only expressed at the coastal level of French waters, via stranding phenomena.
Criterion D5C7 is "Not relevant" in this MRU, relating to the intermediate area of the Channel - North Sea marine sub-region, as it is assessed only in the coastal zone. In fact, perennial meadows and macroalgae do not develop below a certain depth (need for light), and as the depth is generally proportional to the distance from the coast, most of these meadows and macroalgae populations are mainly located in the coastal zone.
Element status
Unknown
Unknown
Unknown
Unknown
Unknown
Not assessed
Not assessed
Description element
The assessment of criterion D5C1 shows that for DIN concentrations: 28 % of the MRU (i.e. 3308 km2 ) does not achieve good ecological status and 72 % of the MRU (i.e. 8578 km2 ) achieves good ecological status. The assessment of criterion D5C1 shows that for DIP concentrations: 18 % of the MRU (i.e. 2085 km2 ) does not achieve good ecological status and 82 % of the MRU (i.e. 9801 km2 ) achieves good ecological status.
The assessment of criterion D5C1 shows that for DIN concentrations: 28 % of the MRU (i.e. 3308 km2 ) does not achieve good ecological status and 72 % of the MRU (i.e. 8578 km2 ) achieves good ecological status. The assessment of criterion D5C1 shows that for DIP concentrations: 18 % of the MRU (i.e. 2085 km2 ) does not achieve good ecological status and 82 % of the MRU (i.e. 9801 km2 ) achieves good ecological status.
The assessment of criterion D5C2 shows that for chlorophyll-a concentrations: 22% of the MRU (i.e. 2601 km2 ) does not achieve good ecological status and 78% of the MRU (i.e. 9285 km2 ) achieves good ecological status.
The assessment of criterion D5C4 shows that for turbidity: 0,5 % of the MRU (i.e. 50 km2 ) does not achieve good ecological status and 99,5 % of the MRU (i.e. 11836 km2 ) achieves good ecological status.
The assessment of criterion D5C5 shows that 100 % of the MRU achieves good ecological status with respect to the bottom dissolved oxygen concentration.
Integration rule type parameter
Other
Other
Other
Other
Other
Other
Other
Integration rule description parameter
The assessment of the status of criterion D5C1, at the scale of each grid cell, is obtained by integrating the two parameters relating to the NID and PID concentration. The integration method used is "One Out, All Out", which means that if one of the two parameters is not reached then the D5C1 criterion is not in good condition in the mesh considered. For the other criteria, the parameter status directly informs the corresponding criterion, no integration rule is required ("Not relevant" type).
The assessment of the status of criterion D5C1, at the scale of each grid cell, is obtained by integrating the two parameters relating to the NID and PID concentration. The integration method used is "One Out, All Out", which means that if one of the two parameters is not reached then the D5C1 criterion is not in good condition in the mesh considered. For the other criteria, the parameter status directly informs the corresponding criterion, no integration rule is required ("Not relevant" type).
The assessment of the status of criterion D5C1, at the scale of each grid cell, is obtained by integrating the two parameters relating to the NID and PID concentration. The integration method used is "One Out, All Out", which means that if one of the two parameters is not reached then the D5C1 criterion is not in good condition in the mesh considered. For the other criteria, the parameter status directly informs the corresponding criterion, no integration rule is required ("Not relevant" type).
The assessment of the status of criterion D5C1, at the scale of each grid cell, is obtained by integrating the two parameters relating to the NID and PID concentration. The integration method used is "One Out, All Out", which means that if one of the two parameters is not reached then the D5C1 criterion is not in good condition in the mesh considered. For the other criteria, the parameter status directly informs the corresponding criterion, no integration rule is required ("Not relevant" type).
The assessment of the status of criterion D5C1, at the scale of each grid cell, is obtained by integrating the two parameters relating to the NID and PID concentration. The integration method used is "One Out, All Out", which means that if one of the two parameters is not reached then the D5C1 criterion is not in good condition in the mesh considered. For the other criteria, the parameter status directly informs the corresponding criterion, no integration rule is required ("Not relevant" type).
The assessment of the status of criterion D5C1, at the scale of each grid cell, is obtained by integrating the two parameters relating to the NID and PID concentration. The integration method used is "One Out, All Out", which means that if one of the two parameters is not reached then the D5C1 criterion is not in good condition in the mesh considered. For the other criteria, the parameter status directly informs the corresponding criterion, no integration rule is required ("Not relevant" type).
The assessment of the status of criterion D5C1, at the scale of each grid cell, is obtained by integrating the two parameters relating to the NID and PID concentration. The integration method used is "One Out, All Out", which means that if one of the two parameters is not reached then the D5C1 criterion is not in good condition in the mesh considered. For the other criteria, the parameter status directly informs the corresponding criterion, no integration rule is required ("Not relevant" type).
Integration rule type criteria
HIE_WEI
HIE_WEI
HIE_WEI
HIE_WEI
HIE_WEI
HIE_WEI
HIE_WEI
Integration rule description criteria
At the level of each grid box (geographical unit of assessment), the integration of the criteria is done in two steps:1/ The first step is to give a score for each criterion on whether the GES has been achieved. Thus, a criterion for which the GES is met receives a score of 0; a criterion for which the GES is not met receives a score of 2 if it is a primary criterion and a score of 1 if it is a secondary criterion. For criterion D5C1, a score of 2 shall be given as soon as one of the phosphate or nitrate elements is downgraded ("One Out All Out").2/ The integration of the criteria is achieved, at the level of each grid cell, by adding up the scores for each criterion. Thus, if the sum of the scores is greater than or equal to 3, then the mesh considered does not reach the GES.
At the level of each grid box (geographical unit of assessment), the integration of the criteria is done in two steps:1/ The first step is to give a score for each criterion on whether the GES has been achieved. Thus, a criterion for which the GES is met receives a score of 0; a criterion for which the GES is not met receives a score of 2 if it is a primary criterion and a score of 1 if it is a secondary criterion. For criterion D5C1, a score of 2 shall be given as soon as one of the phosphate or nitrate elements is downgraded ("One Out All Out").2/ The integration of the criteria is achieved, at the level of each grid cell, by adding up the scores for each criterion. Thus, if the sum of the scores is greater than or equal to 3, then the mesh considered does not reach the GES.
At the level of each grid box (geographical unit of assessment), the integration of the criteria is done in two steps:1/ The first step is to give a score for each criterion on whether the GES has been achieved. Thus, a criterion for which the GES is met receives a score of 0; a criterion for which the GES is not met receives a score of 2 if it is a primary criterion and a score of 1 if it is a secondary criterion. For criterion D5C1, a score of 2 shall be given as soon as one of the phosphate or nitrate elements is downgraded ("One Out All Out").2/ The integration of the criteria is achieved, at the level of each grid cell, by adding up the scores for each criterion. Thus, if the sum of the scores is greater than or equal to 3, then the mesh considered does not reach the GES.
At the level of each grid box (geographical unit of assessment), the integration of the criteria is done in two steps:1/ The first step is to give a score for each criterion on whether the GES has been achieved. Thus, a criterion for which the GES is met receives a score of 0; a criterion for which the GES is not met receives a score of 2 if it is a primary criterion and a score of 1 if it is a secondary criterion. For criterion D5C1, a score of 2 shall be given as soon as one of the phosphate or nitrate elements is downgraded ("One Out All Out").2/ The integration of the criteria is achieved, at the level of each grid cell, by adding up the scores for each criterion. Thus, if the sum of the scores is greater than or equal to 3, then the mesh considered does not reach the GES.
At the level of each grid box (geographical unit of assessment), the integration of the criteria is done in two steps:1/ The first step is to give a score for each criterion on whether the GES has been achieved. Thus, a criterion for which the GES is met receives a score of 0; a criterion for which the GES is not met receives a score of 2 if it is a primary criterion and a score of 1 if it is a secondary criterion. For criterion D5C1, a score of 2 shall be given as soon as one of the phosphate or nitrate elements is downgraded ("One Out All Out").2/ The integration of the criteria is achieved, at the level of each grid cell, by adding up the scores for each criterion. Thus, if the sum of the scores is greater than or equal to 3, then the mesh considered does not reach the GES.
At the level of each grid box (geographical unit of assessment), the integration of the criteria is done in two steps:1/ The first step is to give a score for each criterion on whether the GES has been achieved. Thus, a criterion for which the GES is met receives a score of 0; a criterion for which the GES is not met receives a score of 2 if it is a primary criterion and a score of 1 if it is a secondary criterion. For criterion D5C1, a score of 2 shall be given as soon as one of the phosphate or nitrate elements is downgraded ("One Out All Out").2/ The integration of the criteria is achieved, at the level of each grid cell, by adding up the scores for each criterion. Thus, if the sum of the scores is greater than or equal to 3, then the mesh considered does not reach the GES.
At the level of each grid box (geographical unit of assessment), the integration of the criteria is done in two steps:1/ The first step is to give a score for each criterion on whether the GES has been achieved. Thus, a criterion for which the GES is met receives a score of 0; a criterion for which the GES is not met receives a score of 2 if it is a primary criterion and a score of 1 if it is a secondary criterion. For criterion D5C1, a score of 2 shall be given as soon as one of the phosphate or nitrate elements is downgraded ("One Out All Out").2/ The integration of the criteria is achieved, at the level of each grid cell, by adding up the scores for each criterion. Thus, if the sum of the scores is greater than or equal to 3, then the mesh considered does not reach the GES.
GES extent threshold
GES extent achieved
90.00
90.00
90.00
90.00
90.00
90.00
90.00
GES extent unit
Proportion of area in good status
Proportion of area in good status
Proportion of area in good status
Proportion of area in good status
Proportion of area in good status
Proportion of area in good status
Proportion of area in good status
GES achieved
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Description overall status
Achievement of good ecological status is quantitatively assessed on the basis of 4 criteria relating to the concentration of nutrients, chlorophyll-a and dissolved oxygen, as well as the transparency of the water column. The criteria relating to opportunistic macro-algae and macrophyte communities are not relevant to be assessed in this MRU. In this MRU, relating to the intermediate zone of the Channel - North Sea marine sub-region, the results of the integration of all the criteria show that 90% (i.e. 10703 km2 ) of the area achieves good status. On the other hand, 10% (i.e. 1183 km2 ) of the MRU area does not achieve good status. It should be noted that 100% of the area of this MRU could be assessed. Reading the results by criterion, it appears that eutrophication problems are associated with the combined action of high nutrient and chlorophyll-a concentrations in the Somme and Seine estuaries. Indeed, there are still significant nutrient fluxes in these two rivers, with a stagnation or a significant increase in nitrate fluxes since the 1990s (and a decrease in phosphates). The absence of eutrophication problems between these two areas may be due to the dilution of the Seine plume at the level of the Normandy flowered coast. Furthermore, this assessment has been the subject of collaboration at both national and European level (adaptation of the methodologies of the joint OSPAR-COMP3 procedure). There has also been a clear improvement in the assessment methodology compared with the 2012 Initial Assessment, in particular with the use of products from satellite images and modelling, as well as proposals for thresholds for the intermediate zone.
Achievement of good ecological status is quantitatively assessed on the basis of 4 criteria relating to the concentration of nutrients, chlorophyll-a and dissolved oxygen, as well as the transparency of the water column. The criteria relating to opportunistic macro-algae and macrophyte communities are not relevant to be assessed in this MRU. In this MRU, relating to the intermediate zone of the Channel - North Sea marine sub-region, the results of the integration of all the criteria show that 90% (i.e. 10703 km2 ) of the area achieves good status. On the other hand, 10% (i.e. 1183 km2 ) of the MRU area does not achieve good status. It should be noted that 100% of the area of this MRU could be assessed. Reading the results by criterion, it appears that eutrophication problems are associated with the combined action of high nutrient and chlorophyll-a concentrations in the Somme and Seine estuaries. Indeed, there are still significant nutrient fluxes in these two rivers, with a stagnation or a significant increase in nitrate fluxes since the 1990s (and a decrease in phosphates). The absence of eutrophication problems between these two areas may be due to the dilution of the Seine plume at the level of the Normandy flowered coast. Furthermore, this assessment has been the subject of collaboration at both national and European level (adaptation of the methodologies of the joint OSPAR-COMP3 procedure). There has also been a clear improvement in the assessment methodology compared with the 2012 Initial Assessment, in particular with the use of products from satellite images and modelling, as well as proposals for thresholds for the intermediate zone.
Achievement of good ecological status is quantitatively assessed on the basis of 4 criteria relating to the concentration of nutrients, chlorophyll-a and dissolved oxygen, as well as the transparency of the water column. The criteria relating to opportunistic macro-algae and macrophyte communities are not relevant to be assessed in this MRU. In this MRU, relating to the intermediate zone of the Channel - North Sea marine sub-region, the results of the integration of all the criteria show that 90% (i.e. 10703 km2 ) of the area achieves good status. On the other hand, 10% (i.e. 1183 km2 ) of the MRU area does not achieve good status. It should be noted that 100% of the area of this MRU could be assessed. Reading the results by criterion, it appears that eutrophication problems are associated with the combined action of high nutrient and chlorophyll-a concentrations in the Somme and Seine estuaries. Indeed, there are still significant nutrient fluxes in these two rivers, with a stagnation or a significant increase in nitrate fluxes since the 1990s (and a decrease in phosphates). The absence of eutrophication problems between these two areas may be due to the dilution of the Seine plume at the level of the Normandy flowered coast. Furthermore, this assessment has been the subject of collaboration at both national and European level (adaptation of the methodologies of the joint OSPAR-COMP3 procedure). There has also been a clear improvement in the assessment methodology compared with the 2012 Initial Assessment, in particular with the use of products from satellite images and modelling, as well as proposals for thresholds for the intermediate zone.
Achievement of good ecological status is quantitatively assessed on the basis of 4 criteria relating to the concentration of nutrients, chlorophyll-a and dissolved oxygen, as well as the transparency of the water column. The criteria relating to opportunistic macro-algae and macrophyte communities are not relevant to be assessed in this MRU. In this MRU, relating to the intermediate zone of the Channel - North Sea marine sub-region, the results of the integration of all the criteria show that 90% (i.e. 10703 km2 ) of the area achieves good status. On the other hand, 10% (i.e. 1183 km2 ) of the MRU area does not achieve good status. It should be noted that 100% of the area of this MRU could be assessed. Reading the results by criterion, it appears that eutrophication problems are associated with the combined action of high nutrient and chlorophyll-a concentrations in the Somme and Seine estuaries. Indeed, there are still significant nutrient fluxes in these two rivers, with a stagnation or a significant increase in nitrate fluxes since the 1990s (and a decrease in phosphates). The absence of eutrophication problems between these two areas may be due to the dilution of the Seine plume at the level of the Normandy flowered coast. Furthermore, this assessment has been the subject of collaboration at both national and European level (adaptation of the methodologies of the joint OSPAR-COMP3 procedure). There has also been a clear improvement in the assessment methodology compared with the 2012 Initial Assessment, in particular with the use of products from satellite images and modelling, as well as proposals for thresholds for the intermediate zone.
Achievement of good ecological status is quantitatively assessed on the basis of 4 criteria relating to the concentration of nutrients, chlorophyll-a and dissolved oxygen, as well as the transparency of the water column. The criteria relating to opportunistic macro-algae and macrophyte communities are not relevant to be assessed in this MRU. In this MRU, relating to the intermediate zone of the Channel - North Sea marine sub-region, the results of the integration of all the criteria show that 90% (i.e. 10703 km2 ) of the area achieves good status. On the other hand, 10% (i.e. 1183 km2 ) of the MRU area does not achieve good status. It should be noted that 100% of the area of this MRU could be assessed. Reading the results by criterion, it appears that eutrophication problems are associated with the combined action of high nutrient and chlorophyll-a concentrations in the Somme and Seine estuaries. Indeed, there are still significant nutrient fluxes in these two rivers, with a stagnation or a significant increase in nitrate fluxes since the 1990s (and a decrease in phosphates). The absence of eutrophication problems between these two areas may be due to the dilution of the Seine plume at the level of the Normandy flowered coast. Furthermore, this assessment has been the subject of collaboration at both national and European level (adaptation of the methodologies of the joint OSPAR-COMP3 procedure). There has also been a clear improvement in the assessment methodology compared with the 2012 Initial Assessment, in particular with the use of products from satellite images and modelling, as well as proposals for thresholds for the intermediate zone.
Achievement of good ecological status is quantitatively assessed on the basis of 4 criteria relating to the concentration of nutrients, chlorophyll-a and dissolved oxygen, as well as the transparency of the water column. The criteria relating to opportunistic macro-algae and macrophyte communities are not relevant to be assessed in this MRU. In this MRU, relating to the intermediate zone of the Channel - North Sea marine sub-region, the results of the integration of all the criteria show that 90% (i.e. 10703 km2 ) of the area achieves good status. On the other hand, 10% (i.e. 1183 km2 ) of the MRU area does not achieve good status. It should be noted that 100% of the area of this MRU could be assessed. Reading the results by criterion, it appears that eutrophication problems are associated with the combined action of high nutrient and chlorophyll-a concentrations in the Somme and Seine estuaries. Indeed, there are still significant nutrient fluxes in these two rivers, with a stagnation or a significant increase in nitrate fluxes since the 1990s (and a decrease in phosphates). The absence of eutrophication problems between these two areas may be due to the dilution of the Seine plume at the level of the Normandy flowered coast. Furthermore, this assessment has been the subject of collaboration at both national and European level (adaptation of the methodologies of the joint OSPAR-COMP3 procedure). There has also been a clear improvement in the assessment methodology compared with the 2012 Initial Assessment, in particular with the use of products from satellite images and modelling, as well as proposals for thresholds for the intermediate zone.
Achievement of good ecological status is quantitatively assessed on the basis of 4 criteria relating to the concentration of nutrients, chlorophyll-a and dissolved oxygen, as well as the transparency of the water column. The criteria relating to opportunistic macro-algae and macrophyte communities are not relevant to be assessed in this MRU. In this MRU, relating to the intermediate zone of the Channel - North Sea marine sub-region, the results of the integration of all the criteria show that 90% (i.e. 10703 km2 ) of the area achieves good status. On the other hand, 10% (i.e. 1183 km2 ) of the MRU area does not achieve good status. It should be noted that 100% of the area of this MRU could be assessed. Reading the results by criterion, it appears that eutrophication problems are associated with the combined action of high nutrient and chlorophyll-a concentrations in the Somme and Seine estuaries. Indeed, there are still significant nutrient fluxes in these two rivers, with a stagnation or a significant increase in nitrate fluxes since the 1990s (and a decrease in phosphates). The absence of eutrophication problems between these two areas may be due to the dilution of the Seine plume at the level of the Normandy flowered coast. Furthermore, this assessment has been the subject of collaboration at both national and European level (adaptation of the methodologies of the joint OSPAR-COMP3 procedure). There has also been a clear improvement in the assessment methodology compared with the 2012 Initial Assessment, in particular with the use of products from satellite images and modelling, as well as proposals for thresholds for the intermediate zone.
Assessments period
2010-2016
2010-2016
2010-2016
2010-2016
2010-2016
2010-2016
2010-2016
Related pressures
Related targets