Member State report / Art9 / 2018 / D6 / Mediterranean

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 D6 Sea-floor integrity/D1 Benthic habitats
Region/subregion Mediterranean
Reported by Member state
Member state
United Kingdom
Spain
France
Italy
Malta
Slovenia
Croatia
Greece
Cyprus
Member state report
Marine reporting units MRUs used
  • MWE-ES-SD-ESAL
  • MWE-ES-SD-LEV
  • MWE-FR-MS-MO
  • IT-AS-0001
  • IT-ISCMS-0001
  • IT-WMS-0001
  • MIC-MT-MS-02
  • MAD-SI-MRU-1
  • MAD-HR-MRU_1
  • MAL-CY-MS
Structure, functions and processes of marine ecosystems: Habitats Benthic habitats
  • D6C1 (2)
  • D6C2 (2)
  • D6C3 (2)
  • D6C4 (2)
  • D6C5 (2)
Structure, functions and processes of marine ecosystems: Habitats Benthic broad habitats
  • D6C3 (1)
  • D6C3 (1)
  • D6C4 (1)
  • D6C5 (1)
  • D6/D1 (2)
  • D6/D1 (1)
Structure, functions and processes of marine ecosystems: Habitats Lower bathyal rock and biogenic reef
  • D6/D1 (3)
Structure, functions and processes of marine ecosystems: Habitats Upper bathyal rock and biogenic reef
  • D6/D1 (3)
  • D6C3 (1)
  • D6C4 (1)
  • D6C5 (1)
Structure, functions and processes of marine ecosystems: Habitats Circalittoral coarse sediment
  • D6/D1 (3)
  • D6/D1 (1)
Structure, functions and processes of marine ecosystems: Habitats Circalittoral mud
  • D6/D1 (1)
Structure, functions and processes of marine ecosystems: Habitats Circalittoral mixed sediment
  • D6/D1 (1)
Structure, functions and processes of marine ecosystems: Habitats Circalittoral rock and biogenic reef
  • D6/D1 (3)
  • D6C3 (1)
  • D6C4 (1)
  • D6C5 (1)
  • D6/D1 (1)
Structure, functions and processes of marine ecosystems: Habitats Circalittoral sand
  • D6/D1 (1)
Structure, functions and processes of marine ecosystems: Habitats Infralittoral coarse sediment
  • D6/D1 (3)
  • D6/D1 (1)
Structure, functions and processes of marine ecosystems: Habitats Infralittoral mud
  • D6/D1 (1)
Structure, functions and processes of marine ecosystems: Habitats Infralittoral mixed sediment
  • D6C3 (1)
  • D6C4 (1)
  • D6C5 (1)
  • D6/D1 (1)
Structure, functions and processes of marine ecosystems: Habitats Infralittoral rock and biogenic reef
  • D6/D1 (3)
  • D6C4 (1)
  • D6C5 (1)
  • D6/D1 (1)
Structure, functions and processes of marine ecosystems: Habitats Infralittoral sand
  • D6/D1 (1)
Structure, functions and processes of marine ecosystems: Habitats Littoral rock and biogenic reef
  • D6C3 (1)
  • D6C4 (1)
  • D6C5 (1)
  • D6C3 (1)
  • D6/D1 (1)
Structure, functions and processes of marine ecosystems: Habitats Littoral sediment
  • D6/D1 (1)
Structure, functions and processes of marine ecosystems: Habitats Offshore circalittoral coarse sediment
  • D6/D1 (1)
Structure, functions and processes of marine ecosystems: Habitats Offshore circalittoral mud
  • D6/D1 (1)
Structure, functions and processes of marine ecosystems: Habitats Offshore circalittoral mixed sediment
  • D6/D1 (1)
Structure, functions and processes of marine ecosystems: Habitats Offshore circalittoral rock and biogenic reef
  • D6/D1 (1)
Structure, functions and processes of marine ecosystems: Habitats Offshore circalittoral sand
  • D6/D1 (1)
Structure, functions and processes of marine ecosystems: Habitats Other benthic habitats
  • D6C4 (1)
Structure, functions and processes of marine ecosystems: Habitats Coastal
  • D6/D1 (1)
Structure, functions and processes of marine ecosystems: Habitats Shelf
  • D6/D1 (1)
Structure, functions and processes of marine ecosystems: Ecosystems, including food webs Current regime
  • D6/D1 (1)
Structure, functions and processes of marine ecosystems: Ecosystems, including food webs Mixing
  • D6/D1 (1)
Structure, functions and processes of marine ecosystems: Ecosystems, including food webs Organic carbon
  • D6/D1 (1)
Structure, functions and processes of marine ecosystems: Ecosystems, including food webs Turbidity (silt/sediment loads)
  • D6/D1 (1)
Structure, functions and processes of marine ecosystems: Ecosystems, including food webs Upwelling
  • D6/D1 (1)
Structure, functions and processes of marine ecosystems: Ecosystems, including food webs Wave regime
  • D6/D1 (1)
Structure, functions and processes of marine ecosystems: No theme All marine ecosystem elements
  • D6C5 (2)
Anthropogenic pressures on the marine environment: Biological Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • D6C3 (1)
Anthropogenic pressures on the marine environment: Physical Physical disturbance to seabed
  • D6C2 (1)
  • D6C2 (3)
  • D6C3 (3)
  • D6/D1 (1)
  • D6/D1 (1)
  • D6C2 (1)
Anthropogenic pressures on the marine environment: Physical Changes to hydrological conditions
  • D6/D1 (1)
Anthropogenic pressures on the marine environment: Physical Physical loss of the seabed
  • D6C1 (1)
  • D6C1 (3)
  • D6C3 (3)
  • D6/D1 (1)
  • D6/D1 (1)
  • D6C1 (1)
GES description D6 Sea-floor integrity/D1 Benthic habitats
G 1.2 Marine habitats listed in the Habitats Directive and referring to the SPA/BD protocol of the Barcelona Convention maintain or achieve a favourable conservation status.
G 6.1 Any significant pressure due to: (a) physical disturbances caused by anthropogenic activities
active on the seabed and b) physical loss on biogenic substrates related to activities
anthropogenic.
These GES G1.2 and G 6.1 includes primary criteria D6C4 and D6C5.
The good status of the marine environment in relation to the status of benthic habitat types is achieved when their quality, presence, distribution is in line with prevailing physiographic, geographic and climatic conditions.


The good status of the marine environment, in view of the quality descriptor for the seabed (D6), is achieved when the state of the seabed is at a level that ensures the protection of the structure and functions of ecosystems and prevents adverse effects in particular on benthic ecosystems.
Sea-floor integrity is at a level that ensures that the structure and functions of the ecosystems are safeguarded and benthic ecosystems, in particular, are not adversely affected.
The marine environment of Cyprus is considered to be in good environmental status by the year 2020 if the structure and function of the ecosystem are safeguarded and not adversely affected. Specifically, diversity and productivity are maintained, and any pressures do not hinder the ecosystem components to recover and/or retain their natural diversity, productivity and dynamic ecological processes. Given the available data, the determination of the GES of this descriptor relies heavily on criterion 6.2, which in turn is based on indicator 6.2.2. Indicator 6.2.2 is calculated using the various multimetric indices that have been developed in the framework of the Water-Framework Directive (2000/60/EC) for angiosperms, macroalgae and macrobenthos (and presently assigned a value of 0.9875)..
GES description D6C1 Physical loss of the seabed (6.1)
The physical loss of sea bottoms produced by human activities does not reach a spatial extent that would jeopardise the maintenance of the benthic habitats.
Spatial extent and distribution of physical loss (permanent change) of the natural seabed (Decision 2017/848/EU).
G 6.1 There is no significant pressure due to: (a) physical disturbances caused by human activities active on the seabed and (b) physical loss on biogenic substrates linked to anthropogenic activities.
The length of permanently altered coastline and estimated 100 m wide coastal water band have increased by 44% and 8% between 2012 and 2019. However, the actual fraction of affected coastline remains relatively low. A value of 0.75 is ascribed to this criterion.
GES description D6C2 Physical disturbance to the seabed (6.1)
Seabed potentially affected by physical disturbance does not reach a spatial extent that would jeopardise the maintenance of benthic habitats.
Spatial extent and distribution of pressures from physical disturbance of the seabed (Decision 2017/848/EU).
G 6.1 There is no significant pressure due to: (a) physical disturbances caused by human activities active on the seabed and (b) physical loss on biogenic substrates linked to anthropogenic activities.
Percent change from 2012 to 2019. Based on the information compiled for this reporting, a conservative overall score of 0.75 is ascribed to this criterion.
GES description D6C3 Adverse effects from physical disturbance (6.1.2)
The extent of each benthic habitat type adversely affected by physical disturbances keeps negative or stable trends in a way that ensures their conservation.
Spatial extent of each habitat type adversely affected by changes in its biotic and abiotic structure and functions (e.g. change in species composition and relative abundance, absence of particularly sensitive or fragile species or species performing a key function, size structure of species) due to physical disturbance (Decision 2017/848/EU).
G 6.1 There is no significant pressure due to: (a) physical disturbances caused by human activities active on the seabed and (b) physical loss on biogenic substrates linked to anthropogenic activities.
The structure and functions of MSFD predominant habitat types do not deviate from normal conditions and are in high/good status on the basis of biotic indices used under Directive 2000/60/EC, where established.


The structure and functions of benthic habitats listed in Directive 92/43/EEC, in terms of species composition and relative abundance (as relevant), are in high/good status on the basis of biotic indices used under Directive 2000/60/EC for more than 75% of the area covered by the habitat.
Spatial extent of each habitat type which is adversely affected, through change in its biotic and abiotic structure and its functions (e.g. through changes in species composition and their relative abundance, absence of particularly sensitive or fragile species or species providing a key function, size structure of species), by physical disturbance.
Assuming that the above indicators contribute equally to criterion D6C3, an average value of 0.8 can be ascribed to the criterion itself.
GES description D6C4 Benthic habitat extent (1.4, 1.4.1, 1.4.2, 1.5, 1.5.1, 6.1.1)
The proportion of the loss surface of each benthic habitat type due to anthropogenic pressures does not threaten the maintenance of the habitat type.
The area covered by MSFD broad benthic habitats is stable and is representative of all its natural distributional range.


The area covered by benthic habitats listed in Directive 92/43/EEC is stable and is not smaller than the Favourable Reference Area values where established under Directive 92/43/EEC.
The extent of loss of the habitat type, resulting from anthropogenic pressures, does not exceed a specified proportion of the natural extent of the habitat type in the assessment area.
GES description D6C5 Benthic habitat condition (1.6, 1.6.1, 1.6.2, 1.6.3, 6.2, 6.2.1, 6.2.2, 6.2.3, 6.2.4)
The extent of each habitat type in which benthic communities are kept within values to ensure their durability and performance is maintained or presented with increasing trends.
The structure and functions of MSFD predominant habitat types do not deviate from normal conditions and are in high/good status on the basis of biotic indices used under Directive 2000/60/EC, where established.


The structure and functions of benthic habitats listed in Directive 92/43/EEC, in terms of species composition and relative abundance (as relevant), are in high/good status on the basis of biotic indices used under Directive 2000/60/EC for more than 75% of the area covered by the habitat.
The extent of adverse effects from anthropogenic pressures on the condition of the habitat type, including alteration to its biotic and abiotic structure and its functions (e.g. its typical species composition and their relative abundance, absence of particularly sensitive or fragile species or species providing a key function, size structure of species), does not exceed a specified proportion of the natural extent of the habitat type in the assessment area.
Determination date
  • 2019-06 (D6C4, D6C2, D6C3, D6C1, D6C5)
  • 2019-10 (D6C2, D6C3, D6C1)
  • 2018-12 (D6C2, D6/D1, D6C3, D6C1)
  • 2019-12 (D6C4, D6C3, D6C5)
  • 2020-01 (D6/D1)
  • 2019-05 (D6C4, D6/D1, D6C3, D6C5)
  • 2013-04 (D6C2, D6/D1, D6C3, D6C1)
Update type
  • New determination (D6C4, D6C2, D6C3, D6C1, D6C5)
  • New determination (D6C2, D6C3, D6C1)
  • Modified from reported determination (D6C2, D6C3, D6C1)
  • Same as last reported determination (D6/D1)
  • Modified from reported determination (D6C4, D6C3, D6C5)
  • Modified from reported determination (D6/D1)
  • New determination (D6/D1)
  • New determination (D6C4, D6/D1, D6C3, D6C5)
  • Same as last reported determination (D6C2, D6/D1, D6C3, D6C1)
Justification for non-use of criterion
D6C1: D6C1 is considered to be covered through the following GES: “The area covered by benthic habitats listed in Directive 92/43/EEC is stable and is not smaller than the Favourable Reference Area values where established under Directive 92/43/EEC”.


D6C2: D6C2 is considered to be covered through the following GES: “The structure and functions of benthic habitats listed in Directive 92/43/EEC, in terms of species composition and relative abundance (as relevant), are in high/good status on the basis of biotic indices used under Directive 2000/60/EC for more than 75% of the area covered by the habitat” and “The structure and functions of MSFD predominant habitat types do not deviate from normal conditions and are in high/good status on the basis of biotic indices used under Directive 2000/60/EC, where established”.
D6/D1: The GES definition is set at the descriptor level according to the data currently available for condition assessment. One GES definition is set for D6, and another GES definition is set for criteria D6C4 and D6C5.
D6C1: Assessment methodology not developed. Threshold values should be defined. No data avaliable at the moment, GES not assessed.


D6C2: Assessment methodology not developed. Threshold values should be defined. No data avaliable at the moment, GES not assessed.
Justification for delay in setting EU/regional requirements
D6C1: It is necessary to establish the GES to meet the new criteria for D6. However, the definitions should be quite general as threshold and/or reference values have not yet been established.


D6C2: It is necessary to establish the GES to meet the new criteria for D6. However, the definitions should be quite general as threshold and/or reference values have not yet been established.


D6C3: It is necessary to establish the GES to meet the new criteria for D6. However, the definitions should be quite general as threshold and/or reference values have not yet been established.


D6C4: It is necessary to establish the GES to meet the new criteria for D6. However, the definitions should be quite general as threshold and/or reference values have not yet been established.


D6C5: It is necessary to establish the GES to meet the new criteria for D6. However, the definitions should be quite general as threshold and/or reference values have not yet been established.
D6C1: Criterion D6C1 does not have a threshold required in Decision 2017/848/EU.



D6C2: Criterion D6C2 does not have a threshold required in Decision 2017/848/EU.



D6C3: Criterion D6C3 requires the establishment, through cooperation between Member States at regional or sub-regional level, of threshold values for adverse effects of physical disturbance. Such thresholds have not yet been defined for the French marine sub-regions, but work in this direction is under way at the European level, particularly within the framework of the International Council for the Exploration of the Sea (ICES). The methodological standards associated with this criterion will be specified following further studies, as provided for in Ministerial Order 2019 on the definition of good environmental status of marine waters.



D6C4: No indicators are available for the assessment of criterion D6C4. The methodological standards associated with criterion D6C4 will be further developed following additional studies, as provided for in the Ministerial Order 2019 on the definition of good environmental status of marine waters. The evaluation is available at: https://doi.org/10.13155/60192



D6C5: The assessment of the D6C5 criterion is informed by the calculation of the BenthoVal indicator (Labrune et al., in preparation) selected at the national level. Due to the absence of a defined threshold, criterion D6C5 is not assessed. It should be noted that for this assessment, the BenthoVal indicator could not be calculated for rocky habitats, despite the acquisition of data, because the applicability of BenthoVal to these types of habitats requires further testing. The methodological standards associated with criterion D6C5 will be specified following further studies, as provided for in Ministerial Order 2019 on the definition of good ecological status of marine waters. The evaluation is available at: https://doi.org/10.13155/60192
D6C1: Assessment methodology not developed. Threshold values should be defined. No data avaliable at the moment, GES not assessed.


D6C2: Assessment methodology not developed. Threshold values should be defined. No data avaliable at the moment, GES not assessed.
D6/D1: Sufficient data is available for Descriptor to be assessed.


D6C4: Not assessed


D6C5: Not assessed