Member State report / Art8 / 2018 / D5 / North East Atlantic
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 |
Region/subregion | North East Atlantic |
Reported by | Member state |
Member state | Sweden |
Denmark |
Germany |
Netherlands |
Belgium |
France |
United Kingdom |
Ireland |
Spain |
Portugal |
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Member state report | |||||||||||
Marine reporting units | MRUs used |
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Features | Chemical |
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Element | Transparency |
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Element | Nutrients (N, P) |
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Element | Dissolved oxygen |
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Element | Angiosperms |
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Element | Benthic habitats - macrobenthic communities |
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Element | Benthic habitats - macrophyte communities |
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Element | Benthic habitats - opportunistic macroalgae |
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Element | Benthic invertebrates |
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Element | Chlorophyll-a |
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Element | Cyanobacterial bloom index: Cyanobacterial biomass+cyanobacteria surface accumulations |
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Element | DIN |
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Element | DIN Celtic Sea |
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Element | DIN Coastal & Transitional waters |
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Element | DIN Irish Sea |
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Element | DIP |
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Element | DIP Celtic Sea |
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Element | DIP Coastal & Transitional waters |
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Element | DIP Irish Sea |
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Element | Macrophyte communities |
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Element | Maximum concentration of blooming species |
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Element | Nutrients (integrated) |
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Element | Opportunistic macro-algae |
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Element | Phaeocystis spp. |
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Element | Photic limit |
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Element | Phytoplankton |
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Element | Phytoplankton tool combinings indices for Chlorophyll (90th percentile), elevated counts and seasonal succession |
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Element | Remote sensing (chlorophyll a) |
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Element | TN |
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Element | TP |
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Element | WFD nutrient conditions |
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Element2 |
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Element sources | No. of elements per level |
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Criteria and parameters used (number of parameters) | D5 Eutrophication | ||||||||||
Criteria and parameters used (number of parameters) | D5C1 Nutrient concentrations (5.1, 5.1.1) |
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Criteria and parameters used (number of parameters) | D5C2 Chlorophyll-a concentration (5.2.1) |
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Criteria and parameters used (number of parameters) | D5C3 Harmful algal blooms (5.2.4) |
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Criteria and parameters used (number of parameters) | D5C4 Photic limit (5.2.2) |
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Criteria and parameters used (number of parameters) | D5C5 Dissolved oxygen concentration (5.3.2) |
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Criteria and parameters used (number of parameters) | D5C6 Opportunistic macroalgae of benthic habitats (5.2.3) |
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Criteria and parameters used (number of parameters) | D5C7 Macrophyte communities of benthic habitats (5.3.1) |
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Criteria and parameters used (number of parameters) | D5C8 Macrofaunal communities of benthic habitats |
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Criteria and parameters used (number of parameters) | 5.1.2 Nutrient ratios (silica, nitrogen and phosphorus) | ||||||||||
Criteria and parameters used (number of parameters) | 5.2 Direct effects of nutrient enrichment | ||||||||||
Criteria and parameters used (number of parameters) | 5.3 Indirect effects of nutrient enrichment | ||||||||||
Threshold values | % of parameters with values (no. of parameters) | 90% (108) |
0% (0) |
75% (56) |
72% (8) |
100% (3) |
72% (39) |
100% (8) |
33% (10) |
83% (31) |
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Threshold value sources | D5 Eutrophication | ||||||||||
Threshold value sources | D5C1 Nutrient concentrations (5.1, 5.1.1) |
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Threshold value sources | D5C2 Chlorophyll-a concentration (5.2.1) |
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Threshold value sources | D5C3 Harmful algal blooms (5.2.4) |
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Threshold value sources | D5C4 Photic limit (5.2.2) |
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Threshold value sources | D5C5 Dissolved oxygen concentration (5.3.2) |
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Threshold value sources | D5C6 Opportunistic macroalgae of benthic habitats (5.2.3) |
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Threshold value sources | D5C7 Macrophyte communities of benthic habitats (5.3.1) |
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Threshold value sources | D5C8 Macrofaunal communities of benthic habitats |
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Threshold value sources | 5.1.2 Nutrient ratios (silica, nitrogen and phosphorus) | ||||||||||
Threshold value sources | 5.2 Direct effects of nutrient enrichment | ||||||||||
Threshold value sources | 5.3 Indirect effects of nutrient enrichment | ||||||||||
Value achieved upper | % of parameters with values (no. of parameters) | 87% (104) |
0% (0) |
74% (55) |
72% (8) |
100% (3) |
83% (45) |
100% (8) |
43% (13) |
43% (16) |
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Value achieved lower | % of parameters with values (no. of parameters) | 5% (7) |
0% (0) |
71% (53) |
0% (0) |
0% (0) |
83% (45) |
12% (1) |
0% (0) |
40% (15) |
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Value unit/Value unit other (count of use per criterion) | D5 Eutrophication | ||||||||||
Value unit/Value unit other (count of use per criterion) | D5C1 Nutrient concentrations (5.1, 5.1.1) |
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Value unit/Value unit other (count of use per criterion) | D5C2 Chlorophyll-a concentration (5.2.1) |
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Value unit/Value unit other (count of use per criterion) | D5C3 Harmful algal blooms (5.2.4) |
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Value unit/Value unit other (count of use per criterion) | D5C4 Photic limit (5.2.2) |
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Value unit/Value unit other (count of use per criterion) | D5C5 Dissolved oxygen concentration (5.3.2) |
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Value unit/Value unit other (count of use per criterion) | D5C6 Opportunistic macroalgae of benthic habitats (5.2.3) |
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Value unit/Value unit other (count of use per criterion) | D5C7 Macrophyte communities of benthic habitats (5.3.1) |
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Value unit/Value unit other (count of use per criterion) | D5C8 Macrofaunal communities of benthic habitats |
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Value unit/Value unit other (count of use per criterion) | 5.1.2 Nutrient ratios (silica, nitrogen and phosphorus) | ||||||||||
Value unit/Value unit other (count of use per criterion) | 5.2 Direct effects of nutrient enrichment | ||||||||||
Value unit/Value unit other (count of use per criterion) | 5.3 Indirect effects of nutrient enrichment | ||||||||||
Proportion threshold values | Range of % values (no. of parameters) | Range: 100-100% (10 of 11 parameters) |
Range: 90-100% (24 of 37 parameters) |
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Proportion values achieved | Range of % values (no. of parameters) | Range: 15-49% (5 of 27 parameters) |
Range: 22-77% (5 of 74 parameters) |
Range: 97-100% (7 of 11 parameters) |
Range: 52-71% (3 of 3 parameters) |
Range: 4-100% (54 of 54 parameters) |
Range: 90-100% (24 of 37 parameters) |
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Proportion threshold value units | % 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 % of samples achieving threshold value |
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Trends | No. of trends per category |
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Parameters achieved | No. of parameters per category |
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Related indicators |
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Criteria status | No. of criteria per category |
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Element status | No. of elements per category |
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Integration rule type for parameters | NHIE_WEI (119 or 100.0%) |
OTH (8 or 100.0%) |
OTH (74 or 100.0%) |
OTH (11 or 100.0%) |
OOAO (3 or 100.0%) |
OTH (66 or 100.0%) |
THRES (66 or 100.0%) |
OTH (8 or 24.2%) THRES (25 or 75.8%) |
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Integration rule description for parameters | Integration rule applied to D5C1 and D5C2 when more than one parameter used, not relevant for other elements/criteria as only a single parameter is used per element/ criterion Integration rule applied to D5C1 and D5C2 when more than one parameter used, not relevant for other elements/criteria as only a single parameter is used per element/criterion |
As used in WFD |
According to the OSPAR Common Procedure, the first step is to evaluate the annual mean of each parameter against the area-specific threshold. In a second step, the evaluation results are evaluated over the entire evaluation period. The final result depends on which evaluation result outweighs the single years. If e.g. the DIN concentrations were rated five times as good and four times as bad over an evaluation period of 9 years, the overall evaluation result is good.
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No integration
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Based on whole BPNS |
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 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). |
For the rest of the assessment area (non-DMA), the baseline values defined in the previous Marine Strategy Framework Directive initial assessment were used as a threshold.
For criterion D5C5, it was considered to be BEPS when values higher than 5Â mg L-1 were reached in more than 90Â % of the records. |
Qualitative evaluation: No integration rules applied
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Integration rule type for criteria | OOAO_HIE (119 or 100.0%) |
Not relevant (19 or 70.4%) OTH (8 or 29.6%) |
OOAO (74 or 100.0%) |
OTH (11 or 100.0%) |
OTH (3 or 100.0%) |
HIE_WEI (66 or 100.0%) |
THRES (8 or 100.0%) |
OTH (66 or 100.0%) |
OTH (8 or 22.9%) THRES (27 or 77.1%) |
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Integration rule description for criteria | As used in WFD No integration rule has been applied. The integrated assessment cannot evaluate criteria against the GES decision, since no threshold values have been set in the OSPAR region. OSPAR's integrated assessment thus classifies assessment units as 'problem area' vs. 'Non-problem area' rather than whether or not GES has been achieved. The Final classification is based on the one out – all out principle, meaning that a single “+” in an assessment unit result in a classification as Eutrophication Problem Area. |
According to the OSPAR Common Procedure, the one-out principle has been applied between criteria D5C1, D5C2, D5C3, D5C6, D5C7, D5C8.
According to the OSPAR Common Procedure, the one-out principle is applied between D5C1, D5C2, D5C3, D5C4, D5C5. |
No integration
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OSPAR comp & OOAO WFD coastal waters |
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 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. |
Decision 2017/848/EC does not propose any method for integrating the evaluation of each of the criteria. Therefore, the integration criterion used in the first initial assessment based on the OSPAR Joint Procedure, which was also applied in the first cycle of the Member States, will be adopted. According to this scheme, the assessment area could be classified as âwithout eutrophication problemsâ if all the indicators (criteria) are in BEA. where the nutrient concentrations are not found in BEA but the rest of criteria are found, the zone is classified as âwith potential eutrophication problemsâ. if the criteria of direct effect (chlorophyll) or indirect (oxygen concentration) are not found in BEA, the area would be classified as âWith eutrophication problemsâ.
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Qualitative evaluation: No integration rules applied
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GES extent threshold |
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GES extent achieved |
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GES extent unit |
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GES achieved | Eutrophication |
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Assessment period | 2006-2014 (119 or 100.0%) |
1990-2014 (19 or 70.4%) 2010-2016 (8 or 29.6%) |
2006-2014 (74 or 100.0%) |
2006-2014 (8 or 72.7%) 2009-2015 (3 or 27.3%) |
2011-2016 (3 or 100.0%) |
2010-2015 (24 or 36.4%) 2010-2016 (42 or 63.6%) |
2006-2018 (8 or 100.0%) |
2011-2016 (66 or 100.0%) |
2012-2018 (8 or 20.5%) 2013-2018 (27 or 69.2%) 2014-2018 (4 or 10.3%) |
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Related pressures |
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Related targets | 1 |
2 |
4 |
2 |
5 |
3 |
32 |
5 |