Member State report / Art8 / 2018 / D5 / France / NE Atlantic: Bay of Biscay & Iberian Coast

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: Bay of Biscay & Iberian Coast
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 GdG (ABI-FR-MS-GDG-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
4.0
3.0
3.0
Threshold value lower
Threshold qualitative
Threshold value source
National
National
National
National
Water Framework Directive (2000/60/EC)
Threshold value source other
Value achieved upper
18.51
0.73
3.38
2.57
7.5
Value achieved lower
4.09
0.39
0.54
0.39
3.55
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
83.0
83.0
100.0
100.0
83.0
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 allows the assessment of 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 assessment 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 parameter for nitrogen elements (DIN) shows that 83% of the wide area reaches the parameter and that 17% of the wide area could not be evaluated. 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.
The indicator for this parameter allows the assessment of 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 "DIPconcentration" 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 83 % of the wide area reaches the parameter and that 17 % of the wide area could not be evaluated. 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.
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 assessment of the parameter relating to the bottom dissolved oxygen concentration shows that 83% of the wide area reaches the parameter and that 17% of the wide area 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.
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 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 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 Bay of Biscay 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 Bay of Biscay marine sub-region, as it is assessed only in the coastal zone. Indeed, perennial herbaria and macroalgae do not develop under a certain depth (need for light), and the depth being generally proportional to the distance from the coast, most of these herbaria and macroalgae population are mostly located in coastal areas.
Element status
Unknown
Unknown
Unknown
Unknown
Unknown
Not assessed
Not assessed
Description element
The assessment of criterion D5C1 shows that for PID and PID concentrations: 83 % of the MRU (136847 km2 ) achieves good ecological status and 17 % of the MRU (29010 km2 ) is not assessed.
The assessment of criterion D5C1 shows that for PID and PID concentrations: 83 % of the MRU (136847 km2 ) achieves good ecological status and 17 % of the MRU (29010 km2 ) is not assessed.
The assessment of criterion D5C2 shows that 100 % of the MRU (i.e. 165857 km2 ) achieves good ecological status with respect to chlrophyl a concentration.
The assessment of criterion D5C4 shows that 100 % of the MRU (i.e. 165857 km2 ) achieves good ecological status with respect to water transparency.
The assessment of criterion D5C5 shows that for bottom dissolved oxygen concentrations: 83 % of the MRU (i.e. 136847 km2 ) achieves good ecological status and 17 % of the MRU (i.e. 29010 km2 ) is not assessed.
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 Bay of Biscay marine sub-region, the results of the integration of all the criteria show that 100% (i.e. 165857 km2 ) of the area is in good condition. It should be noted that 100% of the surface area of this MRU could be evaluated. The large area does not therefore appear to be affected by eutrophication phenomena, and 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 to the 2012 Initial Assessment, including the use of products from satellite imagery 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 Bay of Biscay marine sub-region, the results of the integration of all the criteria show that 100% (i.e. 165857 km2 ) of the area is in good condition. It should be noted that 100% of the surface area of this MRU could be evaluated. The large area does not therefore appear to be affected by eutrophication phenomena, and 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 to the 2012 Initial Assessment, including the use of products from satellite imagery 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 Bay of Biscay marine sub-region, the results of the integration of all the criteria show that 100% (i.e. 165857 km2 ) of the area is in good condition. It should be noted that 100% of the surface area of this MRU could be evaluated. The large area does not therefore appear to be affected by eutrophication phenomena, and 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 to the 2012 Initial Assessment, including the use of products from satellite imagery 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 Bay of Biscay marine sub-region, the results of the integration of all the criteria show that 100% (i.e. 165857 km2 ) of the area is in good condition. It should be noted that 100% of the surface area of this MRU could be evaluated. The large area does not therefore appear to be affected by eutrophication phenomena, and 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 to the 2012 Initial Assessment, including the use of products from satellite imagery 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 Bay of Biscay marine sub-region, the results of the integration of all the criteria show that 100% (i.e. 165857 km2 ) of the area is in good condition. It should be noted that 100% of the surface area of this MRU could be evaluated. The large area does not therefore appear to be affected by eutrophication phenomena, and 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 to the 2012 Initial Assessment, including the use of products from satellite imagery 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 Bay of Biscay marine sub-region, the results of the integration of all the criteria show that 100% (i.e. 165857 km2 ) of the area is in good condition. It should be noted that 100% of the surface area of this MRU could be evaluated. The large area does not therefore appear to be affected by eutrophication phenomena, and 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 to the 2012 Initial Assessment, including the use of products from satellite imagery 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 Bay of Biscay marine sub-region, the results of the integration of all the criteria show that 100% (i.e. 165857 km2 ) of the area is in good condition. It should be noted that 100% of the surface area of this MRU could be evaluated. The large area does not therefore appear to be affected by eutrophication phenomena, and 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 to the 2012 Initial Assessment, including the use of products from satellite imagery 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 GdG (ABI-FR-MS-GDG-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
10.0
3.0
0.6
Threshold value lower
Threshold qualitative
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
32.4
10.7
24.9
7.3
0.99
Value achieved lower
11.3
1.8
0.4
3.7
0.28
Value unit
micromole per litre
microgram per litre
Other
milligram per litre
Other
Value unit other
NTU
EQR
Proportion threshold value
Proportion value achieved
59.0
61.0
63.0
57.0
36.0
45.0
19.7
45.0
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 allows the assessment of 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 DIN locations are evaluated 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 (nitrate + nitrite + ammonium) concentration normalized to a salinity of 33 ‰ for the assessment period. The result of the metric calculation is then compared with a threshold value to determine whether or not the parameter is reached in the coastal water body in question. Thus, for DINs in the coastal zone, 59% of the zone reaches the parameter, 4% does not reach the parameter (coastal water body in question: Pertuis Breton) and 37% is not assessed (no data acquisition in the framework of WFD monitoring). The absence of a threshold at the percentage level 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.
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 mass (WFD) and corresponds to the 90 percentile of surface chlorophyll-a concentrations for the assessment period. The result of the metric calculation is then confronted with a threshold value to determine whether or not the parameter has been reached in the coastal water body in question. Thus, for the concentration of chlorophyll-a in the coastal zone, 61% of the zone reaches the parameter, 2% does not reach the parameter (coastal water mass concerned: Baie de Vilaine - coast), and 37% is not assessed.The absence of a threshold for the percentage of the MRU in good condition does not allow a conclusion to be drawn on whether or not 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 water column turbidity for the assessment period. The result of the metric calculation is then confronted 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. 37% 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.
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 metric calculation is then confronted 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 dissolved oxygen concentration at the bottom shows that the whole of the coastal zone evaluated meets the parameter. 43% 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.
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 assessment of this parameter shows that: 36 % of the area reaches the parameter, 3 % does not reach the parameter, 52 % is not assessed, and 9 % is not relevant to assess for this parameter. The 3 coastal water masses that do not reach the parameter are Baie de Concarneau, Laïta - Pouldu, and Golfe du Morbihan. The absence of a threshold for the percentage of MRU in good condition does not allow us to conclude 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: 45% of the area reaches the parameter, 4% does not reach the parameter, 32% is not assessed, and 19% is not relevant to assess for this parameter. The absence of a threshold for the percentage of MRU in good condition does not allow to conclude on whether the parameter assessed at MRU level is reached.
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 assessment of this parameter shows that: 19.7 % of the area reaches the parameter, 1.8 % does not reach the parameter, 36.8 % is not assessed, and 41.7 % is not relevant to assess for this parameter. The absence of a threshold at the level of the percentage of MRU in good condition does not allow to conclude on whether the parameter assessed at the MRU level is reached or not.
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: 45% of the area meets the parameter, 12% does not meet the parameter, 26% is not assessed, and 17% is not relevant to assess for this parameter. The absence of a threshold for the percentage of MRU in good condition does not allow to conclude on whether the parameter assessed at MRU level is met.
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: 4% of the MRU (i.e. 325 km2 ) does not achieve good ecological status, 59% of the MRU (i.e. 4822 km2 ) achieves good ecological status, and 37% of the MRU (i.e. 2985 km2 ) is not assessed.
The assessment of criterion D5C2 shows that for chlorophyll-a concentrations: 2 % of the MRU (152 km2 ) does not achieve good ecological status, 61 % of the MRU (4994 km2 ) achieves good ecological status and 37 % of the MRU (2985 km2 ) is not assessed.
The assessment of criterion D5C4 shows that for turbidity 63 % of the MRU (i.e. 5147 km2 ) achieves good ecological status and 37 % of the MRU (i.e. 2984 km2 ) is not assessed.
The assessment of criterion D5C5 shows that for bottom dissolved oxygen concentrations: 57 % of the MRU (4619 km2 ) achieves good ecological status and 43 % of the MRU (3512 km2 ) is not assessed.
The assessment of criterion D5C6 shows that for the abundance of opportunistic macroalgae: 3 % of the MRU (i.e. 260 km2 ) does not achieve good ecological status, 36 % of the MRU (i.e. 2931 km2 ) achieves good ecological status, 9 % of the MRU (i.e. 711 km2 ) is not relevant for this criterion, and 52 % of the MRU (i.e. 4229 km2 ) is not assessed.
The assessment of criterion D5C7 shows that for the abundance of perennial macro-algae and sea grass: 18 % of the MRU (i.e. 1490 km2 ) does not achieve good ecological status, 51 % of the MRU (i.e. 4102 km2 ) achieves good ecological status, 6 % of the MRU (i.e. 509 km2 ) is not relevant for this criterion, and 25 % of the MRU (i.e. 2030 km2 ) is not assessed.
The assessment of criterion D5C7 shows that for the abundance of perennial macro-algae and sea grass: 18 % of the MRU (i.e. 1490 km2 ) does not achieve good ecological status, 51 % of the MRU (i.e. 4102 km2 ) achieves good ecological status, 6 % of the MRU (i.e. 509 km2 ) is not relevant for this criterion, and 25 % of the MRU (i.e. 2030 km2 ) is not assessed.
The assessment of criterion D5C7 shows that for the abundance of perennial macro-algae and sea grass: 18 % of the MRU (i.e. 1490 km2 ) does not achieve good ecological status, 51 % of the MRU (i.e. 4102 km2 ) achieves good ecological status, 6 % of the MRU (i.e. 509 km2 ) is not relevant for this criterion, and 25 % of the MRU (i.e. 2030 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
75.00
75.00
75.00
75.00
75.00
75.00
75.00
75.00
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 Bay of Biscay marine sub-region, the results of the integration of all the criteria show that 75% (i.e. 6077 km2 ) of the area achieves good status. On the other hand, 3% (i.e. 261 km2 ) of the area of the MRU is not in good condition and 22% (i.e. 1,793 km2 ) of the area has not been assessed. On reading the results by criterion, it appears that the eutrophication problems in this MRU are manifested in coastal water bodies by strandings of opportunistic algae of the genus Ulva. In addition, the results show that nutrient concentrations, chlorophyll-a and/or turbidity lead to the non-achievement of good status for a few coastal water masses located at the level of the plumes of the large estuaries of the Bay of Biscay. However, coastal water bodies where opportunistic algae blooms occur are not in poor condition for the nutrient criterion: the link between nutrient inputs (particularly nitrates) and opportunistic algal growth is therefore not directly visible through the MSFD assessment. Indeed, opportunistic algal blooms do not only depend on the parameters directly taken into account by the MSFD assessment of descriptor 5 - other parameters such as hydrodynamics (residual currents, tidal currents, stratification of the water column, tidal range), salinity, temperature, or the nature of the marine sediment (which more or less favours the remineralisation process of detrital organic matter), can influence the eutrophication process of water masses. In addition, this evaluation 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 evaluation methodology compared to the 2012 Initial Evaluation.
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 Bay of Biscay marine sub-region, the results of the integration of all the criteria show that 75% (i.e. 6077 km2 ) of the area achieves good status. On the other hand, 3% (i.e. 261 km2 ) of the area of the MRU is not in good condition and 22% (i.e. 1,793 km2 ) of the area has not been assessed. On reading the results by criterion, it appears that the eutrophication problems in this MRU are manifested in coastal water bodies by strandings of opportunistic algae of the genus Ulva. In addition, the results show that nutrient concentrations, chlorophyll-a and/or turbidity lead to the non-achievement of good status for a few coastal water masses located at the level of the plumes of the large estuaries of the Bay of Biscay. However, coastal water bodies where opportunistic algae blooms occur are not in poor condition for the nutrient criterion: the link between nutrient inputs (particularly nitrates) and opportunistic algal growth is therefore not directly visible through the MSFD assessment. Indeed, opportunistic algal blooms do not only depend on the parameters directly taken into account by the MSFD assessment of descriptor 5 - other parameters such as hydrodynamics (residual currents, tidal currents, stratification of the water column, tidal range), salinity, temperature, or the nature of the marine sediment (which more or less favours the remineralisation process of detrital organic matter), can influence the eutrophication process of water masses. In addition, this evaluation 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 evaluation methodology compared to the 2012 Initial Evaluation.
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 Bay of Biscay marine sub-region, the results of the integration of all the criteria show that 75% (i.e. 6077 km2 ) of the area achieves good status. On the other hand, 3% (i.e. 261 km2 ) of the area of the MRU is not in good condition and 22% (i.e. 1,793 km2 ) of the area has not been assessed. On reading the results by criterion, it appears that the eutrophication problems in this MRU are manifested in coastal water bodies by strandings of opportunistic algae of the genus Ulva. In addition, the results show that nutrient concentrations, chlorophyll-a and/or turbidity lead to the non-achievement of good status for a few coastal water masses located at the level of the plumes of the large estuaries of the Bay of Biscay. However, coastal water bodies where opportunistic algae blooms occur are not in poor condition for the nutrient criterion: the link between nutrient inputs (particularly nitrates) and opportunistic algal growth is therefore not directly visible through the MSFD assessment. Indeed, opportunistic algal blooms do not only depend on the parameters directly taken into account by the MSFD assessment of descriptor 5 - other parameters such as hydrodynamics (residual currents, tidal currents, stratification of the water column, tidal range), salinity, temperature, or the nature of the marine sediment (which more or less favours the remineralisation process of detrital organic matter), can influence the eutrophication process of water masses. In addition, this evaluation 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 evaluation methodology compared to the 2012 Initial Evaluation.
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 Bay of Biscay marine sub-region, the results of the integration of all the criteria show that 75% (i.e. 6077 km2 ) of the area achieves good status. On the other hand, 3% (i.e. 261 km2 ) of the area of the MRU is not in good condition and 22% (i.e. 1,793 km2 ) of the area has not been assessed. On reading the results by criterion, it appears that the eutrophication problems in this MRU are manifested in coastal water bodies by strandings of opportunistic algae of the genus Ulva. In addition, the results show that nutrient concentrations, chlorophyll-a and/or turbidity lead to the non-achievement of good status for a few coastal water masses located at the level of the plumes of the large estuaries of the Bay of Biscay. However, coastal water bodies where opportunistic algae blooms occur are not in poor condition for the nutrient criterion: the link between nutrient inputs (particularly nitrates) and opportunistic algal growth is therefore not directly visible through the MSFD assessment. Indeed, opportunistic algal blooms do not only depend on the parameters directly taken into account by the MSFD assessment of descriptor 5 - other parameters such as hydrodynamics (residual currents, tidal currents, stratification of the water column, tidal range), salinity, temperature, or the nature of the marine sediment (which more or less favours the remineralisation process of detrital organic matter), can influence the eutrophication process of water masses. In addition, this evaluation 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 evaluation methodology compared to the 2012 Initial Evaluation.
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 Bay of Biscay marine sub-region, the results of the integration of all the criteria show that 75% (i.e. 6077 km2 ) of the area achieves good status. On the other hand, 3% (i.e. 261 km2 ) of the area of the MRU is not in good condition and 22% (i.e. 1,793 km2 ) of the area has not been assessed. On reading the results by criterion, it appears that the eutrophication problems in this MRU are manifested in coastal water bodies by strandings of opportunistic algae of the genus Ulva. In addition, the results show that nutrient concentrations, chlorophyll-a and/or turbidity lead to the non-achievement of good status for a few coastal water masses located at the level of the plumes of the large estuaries of the Bay of Biscay. However, coastal water bodies where opportunistic algae blooms occur are not in poor condition for the nutrient criterion: the link between nutrient inputs (particularly nitrates) and opportunistic algal growth is therefore not directly visible through the MSFD assessment. Indeed, opportunistic algal blooms do not only depend on the parameters directly taken into account by the MSFD assessment of descriptor 5 - other parameters such as hydrodynamics (residual currents, tidal currents, stratification of the water column, tidal range), salinity, temperature, or the nature of the marine sediment (which more or less favours the remineralisation process of detrital organic matter), can influence the eutrophication process of water masses. In addition, this evaluation 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 evaluation methodology compared to the 2012 Initial Evaluation.
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 Bay of Biscay marine sub-region, the results of the integration of all the criteria show that 75% (i.e. 6077 km2 ) of the area achieves good status. On the other hand, 3% (i.e. 261 km2 ) of the area of the MRU is not in good condition and 22% (i.e. 1,793 km2 ) of the area has not been assessed. On reading the results by criterion, it appears that the eutrophication problems in this MRU are manifested in coastal water bodies by strandings of opportunistic algae of the genus Ulva. In addition, the results show that nutrient concentrations, chlorophyll-a and/or turbidity lead to the non-achievement of good status for a few coastal water masses located at the level of the plumes of the large estuaries of the Bay of Biscay. However, coastal water bodies where opportunistic algae blooms occur are not in poor condition for the nutrient criterion: the link between nutrient inputs (particularly nitrates) and opportunistic algal growth is therefore not directly visible through the MSFD assessment. Indeed, opportunistic algal blooms do not only depend on the parameters directly taken into account by the MSFD assessment of descriptor 5 - other parameters such as hydrodynamics (residual currents, tidal currents, stratification of the water column, tidal range), salinity, temperature, or the nature of the marine sediment (which more or less favours the remineralisation process of detrital organic matter), can influence the eutrophication process of water masses. In addition, this evaluation 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 evaluation methodology compared to the 2012 Initial Evaluation.
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 Bay of Biscay marine sub-region, the results of the integration of all the criteria show that 75% (i.e. 6077 km2 ) of the area achieves good status. On the other hand, 3% (i.e. 261 km2 ) of the area of the MRU is not in good condition and 22% (i.e. 1,793 km2 ) of the area has not been assessed. On reading the results by criterion, it appears that the eutrophication problems in this MRU are manifested in coastal water bodies by strandings of opportunistic algae of the genus Ulva. In addition, the results show that nutrient concentrations, chlorophyll-a and/or turbidity lead to the non-achievement of good status for a few coastal water masses located at the level of the plumes of the large estuaries of the Bay of Biscay. However, coastal water bodies where opportunistic algae blooms occur are not in poor condition for the nutrient criterion: the link between nutrient inputs (particularly nitrates) and opportunistic algal growth is therefore not directly visible through the MSFD assessment. Indeed, opportunistic algal blooms do not only depend on the parameters directly taken into account by the MSFD assessment of descriptor 5 - other parameters such as hydrodynamics (residual currents, tidal currents, stratification of the water column, tidal range), salinity, temperature, or the nature of the marine sediment (which more or less favours the remineralisation process of detrital organic matter), can influence the eutrophication process of water masses. In addition, this evaluation 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 evaluation methodology compared to the 2012 Initial Evaluation.
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 Bay of Biscay marine sub-region, the results of the integration of all the criteria show that 75% (i.e. 6077 km2 ) of the area achieves good status. On the other hand, 3% (i.e. 261 km2 ) of the area of the MRU is not in good condition and 22% (i.e. 1,793 km2 ) of the area has not been assessed. On reading the results by criterion, it appears that the eutrophication problems in this MRU are manifested in coastal water bodies by strandings of opportunistic algae of the genus Ulva. In addition, the results show that nutrient concentrations, chlorophyll-a and/or turbidity lead to the non-achievement of good status for a few coastal water masses located at the level of the plumes of the large estuaries of the Bay of Biscay. However, coastal water bodies where opportunistic algae blooms occur are not in poor condition for the nutrient criterion: the link between nutrient inputs (particularly nitrates) and opportunistic algal growth is therefore not directly visible through the MSFD assessment. Indeed, opportunistic algal blooms do not only depend on the parameters directly taken into account by the MSFD assessment of descriptor 5 - other parameters such as hydrodynamics (residual currents, tidal currents, stratification of the water column, tidal range), salinity, temperature, or the nature of the marine sediment (which more or less favours the remineralisation process of detrital organic matter), can influence the eutrophication process of water masses. In addition, this evaluation 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 evaluation methodology compared to the 2012 Initial Evaluation.
Assessments period
2010-2015
2010-2015
2010-2015
2010-2015
2010-2015
2010-2015
2010-2015
2010-2015
Related pressures
Related targets

ZI SRM GdG (ABI-FR-MS-GDG-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
5.0
7.0
3.0
Threshold value lower
Threshold qualitative
Threshold value source
National
National
National
National
Water Framework Directive (2000/60/EC)
Threshold value source other
Value achieved upper
36.3
1.05
6.1
40.1
7.45
Value achieved lower
6.7
0.46
0.91
0.53
1.67
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
95.0
85.0
99.0
98.0
93.5
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 allows the assessment of good nutrient status (NIDs and PIDs) at the scale of each coastal water body or grid box (intermediate and wide areas). In intermediate and wide areas: the parameter relating to "NID 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 PID (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 mesh under consideration. Concerning the intermediate zone for NIDs, 95 % of the zone reaches the parameter and 5 % does not reach the parameter. The area not reaching the parameter corresponds to areas opposite the Gironde, Loire and Sèvre Niortaise estuary. The absence of a threshold at the level of the percentage of the RMU in good condition does not make it possible to conclude on whether the parameter assessed at the RMU 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 the "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 mesh under consideration. Concerning the intermediate zone for DIPs, 85% of the intermediate zone reaches the parameter while 15% does not reach the parameter. The area not reaching the parameter corresponds to an almost continuous strip from the Gironde estuary to the Loire. 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.
In intermediate and large areas, the "water concentration" parameter of chlorophyll-a is based on data from satellite images (MODIS sensor). From this data, a metric is defined at the scale of each cell and corresponds to the 90th percentile of chlorophyll-a concentrations at the surface 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 mesh in question. Thus, the concentrations of chlrophyll-a in the intermediate zone shows that 99% of the zone reaches the parameter and that 1% does not reach the parameter. Two areas do not reach the parameter, the first is located north of the Gironde estuary and the second opposite the Loire estuary. The absence of a threshold at the level of the percentage of the MRU in good condition does not allow us to conclude on whether or not the parameter evaluated at MRU scale has been reached.
In intermediate and large zones, the turbidity parameter in the water column is based on data from satellite images (MODIS sensor). From this data, a metric is defined at the scale of each mesh and corresponds to the 90th 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 mesh in question. Thus, the evaluation of the parameter relating to the turbidity of the water column shows that 98% of the intermediate zone reaches the parameter and that 2% does not reach the parameter at the outlet of the Gironde estuary . The absence of a threshold at the level of the percentage of the MRU in good condition does not allow us to conclude on whether or not the parameter evaluated at MRU scale has been reached.
In intermediate and large zones, the "dissolved oxygen concentration at the bottom" parameter is based on data from the hydrodynamic and biological model ECO-MARS3D (https://wwz.ifremer.fr/mars3d/). From this data, a metric is defined at the scale of each mesh and corresponds to the 10th percentile of the dissolved oxygen concentrations at the bottom for the evaluation period. Thus, the evaluation of the parameter relating to the dissolved oxygen concentration at the bottom shows that 93.5% of the intermediate zone reaches the parameter and that 6.5% does not reach the parameter at the outlet of the Arcachon. The absence of a threshold at the level of the percentage of the MRU in good condition does not allow us to conclude on whether or not the parameter evaluated at MRU scale 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 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 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 Bay of Biscay 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 Bay of Biscay marine sub-region, as it is assessed only in the coastal zone. Indeed, perennial herbaria and macroalgae do not develop under a certain depth (need for light), and the depth being generally proportional to the distance from the coast, most of these herbaria and macroalgae population are mostly located in coastal areas.
Element status
Unknown
Unknown
Unknown
Unknown
Unknown
Not assessed
Not assessed
Description element
The assessment of criterion D5C1 shows that for DIN concentrations: 5 % of the MRU (i.e. 764 km2 ) does not achieve good ecological status and 95 % of the MRU (i.e. 13370 km2 ) achieves good ecological status. The assessment of criterion D5C1 shows that for DIP concentrations: 15 % of the MRU (i.e. 2164 km2 ) does not achieve good ecological status and 85 % of the MRU (i.e. 11971 km2 ) achieves good ecological status.
The assessment of criterion D5C1 shows that for DIN concentrations: 5 % of the MRU (i.e. 764 km2 ) does not achieve good ecological status and 95 % of the MRU (i.e. 13370 km2 ) achieves good ecological status. The assessment of criterion D5C1 shows that for DIP concentrations: 15 % of the MRU (i.e. 2164 km2 ) does not achieve good ecological status and 85 % of the MRU (i.e. 11971 km2 ) achieves good ecological status.
The assessment of criterion D5C2 shows that for chlorophyll-a concentrations: 1 % of the MRU (117 km2 ) does not achieve good ecological status and 99 % of the MRU (14018 km2 ) achieves good ecological status.
The assessment of criterion D5C4 shows that for turbidity: 2 % of the MRU (251 km2 ) does not achieve good ecological status and 98 % of the MRU (13885 km2 ) achieves good ecological status.
The assessment of criterion D5C5 shows that for the bottom dissolved oxygen concentration: 6,5 % of the MRU (i.e. 912 km2 ) does not achieve good ecological status and 93,5 % of the MRU (i.e. 13218 km2 ) achieves good ecological status.
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
98.00
98.00
98.00
98.00
98.00
98.00
98.00
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 Bay of Biscay marine sub-region, the results of the integration of all the criteria show that 98% (i.e. 13844 km2 ) of the area is in good condition. On the other hand, 2% (or 287 km2 ) of the MRU's surface area is not in good condition. It should be noted that 100 % of the surface area of this MRU has been assessed. On reading the results by criterion, it appears that the eutrophication problems in this MRU are located at the mouths of the Loire and Gironde rivers and are associated with the combined action of high concentrations of nutrients, chlorophyll-a, and/or turbidity. 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 evaluation methodology compared to the 2012 Initial Evaluation, including the use of products from satellite imagery 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 Bay of Biscay marine sub-region, the results of the integration of all the criteria show that 98% (i.e. 13844 km2 ) of the area is in good condition. On the other hand, 2% (or 287 km2 ) of the MRU's surface area is not in good condition. It should be noted that 100 % of the surface area of this MRU has been assessed. On reading the results by criterion, it appears that the eutrophication problems in this MRU are located at the mouths of the Loire and Gironde rivers and are associated with the combined action of high concentrations of nutrients, chlorophyll-a, and/or turbidity. 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 evaluation methodology compared to the 2012 Initial Evaluation, including the use of products from satellite imagery 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 Bay of Biscay marine sub-region, the results of the integration of all the criteria show that 98% (i.e. 13844 km2 ) of the area is in good condition. On the other hand, 2% (or 287 km2 ) of the MRU's surface area is not in good condition. It should be noted that 100 % of the surface area of this MRU has been assessed. On reading the results by criterion, it appears that the eutrophication problems in this MRU are located at the mouths of the Loire and Gironde rivers and are associated with the combined action of high concentrations of nutrients, chlorophyll-a, and/or turbidity. 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 evaluation methodology compared to the 2012 Initial Evaluation, including the use of products from satellite imagery 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 Bay of Biscay marine sub-region, the results of the integration of all the criteria show that 98% (i.e. 13844 km2 ) of the area is in good condition. On the other hand, 2% (or 287 km2 ) of the MRU's surface area is not in good condition. It should be noted that 100 % of the surface area of this MRU has been assessed. On reading the results by criterion, it appears that the eutrophication problems in this MRU are located at the mouths of the Loire and Gironde rivers and are associated with the combined action of high concentrations of nutrients, chlorophyll-a, and/or turbidity. 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 evaluation methodology compared to the 2012 Initial Evaluation, including the use of products from satellite imagery 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 Bay of Biscay marine sub-region, the results of the integration of all the criteria show that 98% (i.e. 13844 km2 ) of the area is in good condition. On the other hand, 2% (or 287 km2 ) of the MRU's surface area is not in good condition. It should be noted that 100 % of the surface area of this MRU has been assessed. On reading the results by criterion, it appears that the eutrophication problems in this MRU are located at the mouths of the Loire and Gironde rivers and are associated with the combined action of high concentrations of nutrients, chlorophyll-a, and/or turbidity. 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 evaluation methodology compared to the 2012 Initial Evaluation, including the use of products from satellite imagery 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 Bay of Biscay marine sub-region, the results of the integration of all the criteria show that 98% (i.e. 13844 km2 ) of the area is in good condition. On the other hand, 2% (or 287 km2 ) of the MRU's surface area is not in good condition. It should be noted that 100 % of the surface area of this MRU has been assessed. On reading the results by criterion, it appears that the eutrophication problems in this MRU are located at the mouths of the Loire and Gironde rivers and are associated with the combined action of high concentrations of nutrients, chlorophyll-a, and/or turbidity. 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 evaluation methodology compared to the 2012 Initial Evaluation, including the use of products from satellite imagery 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 Bay of Biscay marine sub-region, the results of the integration of all the criteria show that 98% (i.e. 13844 km2 ) of the area is in good condition. On the other hand, 2% (or 287 km2 ) of the MRU's surface area is not in good condition. It should be noted that 100 % of the surface area of this MRU has been assessed. On reading the results by criterion, it appears that the eutrophication problems in this MRU are located at the mouths of the Loire and Gironde rivers and are associated with the combined action of high concentrations of nutrients, chlorophyll-a, and/or turbidity. 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 evaluation methodology compared to the 2012 Initial Evaluation, including the use of products from satellite imagery 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