Member State report / Art9 / 2018 / D5 / France / NE Atlantic: Celtic Seas
Report type | Member State report to Commission |
MSFD Article | Art. 9 Determination of GES (and Art. 17 updates) |
Report due | 2018-10-15 |
GES Descriptor | D5 Eutrophication |
Member State | France |
Region/subregion | NE Atlantic: Celtic Seas |
Reported by | Ministère de la transition Ecologique et Solidaire |
Report date | 2020-02-19 |
Report access | ART9_GES_FR_2019-12-12.xml |
GES component |
D5
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D5C1
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D5C1
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D5C2
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D5C3
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D5C4
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D5C5
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D5C6
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D5C7
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D5C8
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5.1.2
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5.2
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5.3
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Marine reporting units |
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Features |
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GES description |
Human-induced eutrophication, in particular with regard to its adverse effects, such as loss of biodiversity, ecosystem degradation, toxic algal blooms and deoxygenation of bottom waters, is minimised (Directive 2008/56/EC).
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Nutrient concentrations are not at levels indicating adverse effects related to eutrophication (Decision 2017/848/EU).
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Concentrations of chlorophyll a are not at levels indicating adverse effects (Decision 2017/848/EU).
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The photic limit of the water column is not reduced by an increase in the amount of suspended algae to a level indicating adverse effects (Decision 2017/848/EU).
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The concentration of dissolved oxygen is not reduced to levels indicating adverse effects on benthic habitats (Decision 2017/848/EU).
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The abundance of opportunistic macroscopic algae is not at a level indicating adverse effects (Decision 2017/848/EU).
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The species composition and relative abundance or depth distribution of macrophyte communities reach values indicating absence of adverse effects (Decision 2017/848/EU).
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Determination date |
201910 |
201910 |
201910 |
201910 |
201910 |
201910 |
201910 |
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Update type |
New determination |
New determination |
New determination |
New determination |
New determination |
New determination |
New determination |
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Justification for non-use of criterion |
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Justification for delay in setting EU/regional requirements |
For descriptor D5, no criteria could be evaluated due to the absence of an aggregation rule (threshold) at the level of each parameter evaluated. Indeed, the assessment of the status of each parameter is carried out at the level of the basic unit of assessment, i.e. the WFD water body or the grid box according to the MRU considered, without aggregation at the scale of the MRU. However, the assessment allows the identification of criteria and problem areas to guide the actions that must be implemented for a return to or maintenance of good status. The methodological standards relating to the criteria of Descriptor 5 will be specified following additional studies, as provided for in Ministerial Order 2019 on the definition of good environmental status of marine waters.
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Criterion D5C1 could not be filled in for this assessment in the coastal zone of the Western Mediterranean Marine Sub-Region. Indeed, the lack of data (collection effort being mainly concentrated in lagoon areas more prone to eutrophication problems) and of consensus to define a threshold in this MRU did not allow a relevant evaluation of this criterion. The methodological standards relating to criterion D5C1 will be specified following further studies, as provided for in Ministerial Order 2019 on the definition of good environmental status of marine waters.
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For descriptor D5, no criteria could be evaluated due to the absence of an aggregation rule (threshold) at the level of each parameter evaluated. Indeed, the assessment of the status of each parameter is carried out at the level of the basic unit of assessment, i.e. the WFD water body or the grid box according to the MRU considered, without aggregation at the scale of the MRU. However, the assessment allows the identification of criteria and problem areas to guide the actions that must be implemented for a return to or maintenance of good status. The methodological standards relating to the criteria of Descriptor 5 will be specified following additional studies, as provided for in Ministerial Order 2019 on the definition of good environmental status of marine waters.
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For descriptor D5, no criteria could be evaluated due to the absence of an aggregation rule (threshold) at the level of each parameter evaluated. Indeed, the assessment of the status of each parameter is carried out at the level of the basic unit of assessment, i.e. the WFD water body or the grid box according to the MRU considered, without aggregation at the scale of the MRU. However, the assessment allows the identification of criteria and problem areas to guide the actions that must be implemented for a return to or maintenance of good status. The methodological standards relating to the criteria of Descriptor 5 will be specified following additional studies, as provided for in Ministerial Order 2019 on the definition of good environmental status of marine waters.
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For descriptor D5, no criteria could be evaluated due to the absence of an aggregation rule (threshold) at the level of each parameter evaluated. Indeed, the assessment of the status of each parameter is carried out at the level of the basic unit of assessment, i.e. the WFD water body or the grid box according to the MRU considered, without aggregation at the scale of the MRU. However, the assessment allows the identification of criteria and problem areas to guide the actions that must be implemented for a return to or maintenance of good status. The methodological standards relating to the criteria of Descriptor 5 will be specified following additional studies, as provided for in Ministerial Order 2019 on the definition of good environmental status of marine waters.
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For descriptor D5, no criteria could be evaluated due to the absence of an aggregation rule (threshold) at the level of each parameter evaluated. Indeed, the assessment of the status of each parameter is carried out at the level of the basic unit of assessment, i.e. the WFD water body or the grid box according to the MRU considered, without aggregation at the scale of the MRU. However, the assessment allows the identification of criteria and problem areas to guide the actions that must be implemented for a return to or maintenance of good status. The methodological standards relating to the criteria of Descriptor 5 will be specified following additional studies, as provided for in Ministerial Order 2019 on the definition of good environmental status of marine waters.
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For descriptor D5, no criteria could be evaluated due to the absence of an aggregation rule (threshold) at the level of each parameter evaluated. Indeed, the assessment of the status of each parameter is carried out at the level of the basic unit of assessment, i.e. the WFD water body or the grid box according to the MRU considered, without aggregation at the scale of the MRU. However, the assessment allows the identification of criteria and problem areas to guide the actions that must be implemented for a return to or maintenance of good status. The methodological standards relating to the criteria of Descriptor 5 will be specified following additional studies, as provided for in Ministerial Order 2019 on the definition of good environmental status of marine waters.
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For descriptor D5, no criteria could be evaluated due to the absence of an aggregation rule (threshold) at the level of each parameter evaluated. Indeed, the assessment of the status of each parameter is carried out at the level of the basic unit of assessment, i.e. the WFD water body or the grid box according to the MRU considered, without aggregation at the scale of the MRU. However, the assessment allows the identification of criteria and problem areas to guide the actions that must be implemented for a return to or maintenance of good status. The methodological standards relating to the criteria of Descriptor 5 will be specified following additional studies, as provided for in Ministerial Order 2019 on the definition of good environmental status of marine waters.
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