Member State report / Art8 / 2018 / D7 / 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 D7 Hydrographical changes
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

Nord SRM GdG L200 (ABI-FR-MS-GDG-NORD-L200)

GES component
D7
D7
D7
D7
D7
D7
D7
D7
D7
D7
D7
Feature
Hydrographical changes
Hydrographical changes
Hydrographical changes
Hydrographical changes
Hydrographical changes
Hydrographical changes
Hydrographical changes
Benthic broad habitats
Benthic broad habitats
Benthic broad habitats
Benthic broad habitats
Element
Changes in current regime
Changes in salinity regime
Changes in seabed substrate
Changes in thermal regime
Changes in tide regime
Changes in turbidity regime
Changes in waves regime
Offshore circalittoral coarse sediment
Offshore circalittoral mixed sediment
Offshore circalittoral mud
Offshore circalittoral sand
Element code
ExpPresCurrents
ExpPresSalinity
ExpPresSeabedNature
ExpPresTemperature
ExpPresTide
ExpPresTurbidity
ExpPresWaves
HabBenOffshCoarSed
HabBenOffshMxdSed
HabBenOffshMud
HabBenOffshSand
Element code source
Link to other vocabulary or code lists that may be relevant
Link to other vocabulary or code lists that may be relevant
Link to other vocabulary or code lists that may be relevant
Link to other vocabulary or code lists that may be relevant
Link to other vocabulary or code lists that may be relevant
Link to other vocabulary or code lists that may be relevant
Link to other vocabulary or code lists that may be relevant
Habitats (D1-D6) http://dd.eionet.europa.eu/vocabulary/msfd/broadHabitatTypes/view
Habitats (D1-D6) http://dd.eionet.europa.eu/vocabulary/msfd/broadHabitatTypes/view
Habitats (D1-D6) http://dd.eionet.europa.eu/vocabulary/msfd/broadHabitatTypes/view
Habitats (D1-D6) http://dd.eionet.europa.eu/vocabulary/msfd/broadHabitatTypes/view
Element 2
Element 2 code
Element 2 code source
Element source
National
National
National
National
National
National
National
EU
EU
EU
EU
Criterion
D7C1
D7C1
D7C1
D7C1
D7C1
D7C1
D7C1
D7C2
D7C2
D7C2
D7C2
Parameter
Extent
Extent
Extent
Extent
Extent
Extent
Extent
Extent
Extent
Extent
Extent
Parameter other
Threshold value upper
Threshold value lower
Threshold qualitative
Not available yet
Not available yet
Not available yet
Not available yet
Not available yet
Not available yet
Not available yet
Not available yet
Not available yet
Not available yet
Not available yet
Threshold value source
Threshold value source other
Value achieved upper
Value achieved lower
Value unit
Value unit other
Proportion threshold value
Proportion value achieved
11385.0
10.0
11385.0
120.0
45.0
306.0
395.0
Proportion threshold value unit
extent in km2 of pressure
extent in km2 of pressure
extent in km2 of pressure
extent in km2 of pressure
extent in km2 of pressure
extent in km2 of pressure
extent in km2 of pressure
extent in km2 of habitat adversely affected
extent in km2 of habitat adversely affected
extent in km2 of habitat adversely affected
extent in km2 of habitat adversely affected
Trend
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Parameter achieved
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Description parameter
The metric considered for this parameter is the area of exposure for each pressure considered (overall or as a function of the level of the exposure index). The areas potentially affected by a change in the current regime correspond to a total area of 0 km2 . The areas of exposure according to the four levels of the exposure index are No exposure: 51501 km² Low exposure index: 0 km² Medium exposure index: 0 km² High exposure index: 0 km² Note that no threshold is currently available to assess whether or not the parameter has been reached.
The metric considered for this parameter is the area of exposure for each pressure considered (overall or as a function of the level of the exposure index). The areas potentially affected by a change in salinity regime correspond to a total surface area of 0 km2 . The areas of exposure according to the four levels of the exposure index are No exposure: 51501 km² Low exposure index: 0 km² Medium exposure index: 0 km² High exposure index: 0 km² Note that no threshold is currently available to assess whether or not the parameter has been reached.
The metric considered for this parameter is the area of exposure for each pressure considered (overall or as a function of the level of the exposure index). The areas potentially affected by a change in the background nature correspond to a total area of 11385 km2 . The areas of exposure according to the four levels of exposure index are: No exposure: 40116 km² Low exposure index: 11385 km² Medium exposure index: 0 km² High exposure index: 0 km² Note that no threshold is currently available to assess whether or not the parameter has been reached.
The metric considered for this parameter is the area of exposure for each pressure considered (overall or as a function of the level of the exposure index). The areas potentially affected by a change in the thermal regime correspond to a total surface area of <10 km2 . The areas of exposure according to the four levels of the exposure index are No exposure: 51501 km² Low exposure index: <10 km² Medium exposure index: 0 km² High exposure index: 0 km² Note that no threshold is currently available to assess whether or not the parameter has been reached.
The metric considered for this parameter is the area of exposure for each pressure considered (overall or as a function of the level of the exposure index). The areas potentially affected by a change in the tidal regime correspond to a total area of 0 km2 , based on the four levels of exposure index: No exposure: 51501 km² Low exposure index: 0 km² Medium exposure index: 0 km² High exposure index: 0 km² Note that no threshold is currently available to assess whether or not the parameter has been reached.
The metric considered for this parameter is the area of exposure for each pressure considered (overall or as a function of the level of the exposure index). The areas potentially affected by a change in the turbidity regime correspond to a total area of 11385 km2 . The areas of exposure according to the four levels of exposure index are: No exposure: 40116 km² Low exposure index: 11385 km² Medium exposure index: 0 km² High exposure index: 0 km² Note that no threshold is currently available to assess whether or not the parameter has been reached.
The metric considered for this parameter is the area of exposure for each pressure considered (overall or as a function of the level of the exposure index). The areas potentially affected by a change in the wave regime correspond to a total area of 0 km2 . The areas of exposure according to the four levels of the exposure index are No Exposure: 51501 km² Low Exposure Index: 0 km² Medium Exposure Index: 0 km² High Exposure Index: 0 km² Note that no threshold is currently available to assess whether or not the parameter has been reached.
The metric considered for this parameter is the area of habitat potentially at risk (overall or based on the level of risk). The spatial extent of potential habitat alteration related to permanent changes in hydrographic conditions in this MRU is 120 km2 (i.e., 100% of the assessed habitat). In addition, the indicator makes it possible to assess the intensity of the risk of modification: negligible or nil risk of modification: 0 km², low risk of modification: 58 km², medium risk of modification: 62 km², high risk of modification: 0 km², it should be noted that no threshold is currently available to assess whether or not the parameter has been reached.
The metric considered for this parameter is the area of habitat potentially at risk (overall or based on the level of risk). The spatial extent of potential habitat alteration associated with permanent changes in hydrographic conditions in this MRU is 45 km2 (i.e., 100% of the assessed habitat). In addition, the indicator makes it possible to assess the intensity of the risk of modification: negligible or nil risk of modification: 0 km², low risk of modification: 21 km², medium risk of modification: 24 km², high risk of modification: 0 km², it should be noted that no threshold is currently available to assess whether or not the parameter has been reached.
The metric considered for this parameter is the area of habitat potentially at risk (overall or based on the level of risk). The spatial extent of potential habitat alteration associated with permanent changes in hydrographic conditions in this MRU is 306 km2 (i.e., 100% of the assessed habitat). In addition, the indicator makes it possible to assess the intensity of the risk of modification: negligible or no risk of modification: 0 km².low risk of modification: 110 km².medium risk of modification: 196 km².high risk of modification: 0 km².It should be noted that no threshold is currently available to assess whether or not the parameter has been reached.
The metric considered for this parameter is the area of habitat potentially at risk (overall or based on the level of risk). The spatial extent of potential habitat alteration associated with permanent changes in hydrographic conditions in this MRU is 395 km2 (i.e., 100% of the assessed habitat). In addition, the indicator makes it possible to assess the intensity of the risk of modification: negligible or nil risk of modification: 0 km², low risk of modification: 127 km², medium risk of modification: 268 km², high risk of modification: 0 km², it should be noted that no threshold is currently available to assess whether or not the parameter has been reached.
Related indicator
Criteria status
Contributes to assessment of another criterion/ele
Contributes to assessment of another criterion/ele
Contributes to assessment of another criterion/ele
Contributes to assessment of another criterion/ele
Contributes to assessment of another criterion/ele
Contributes to assessment of another criterion/ele
Contributes to assessment of another criterion/ele
Unknown
Unknown
Unknown
Unknown
Description criteria
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017) no threshold is to be specified for D7C1: the status of the D7C1 criterion is therefore not reported. However, the assessment of the D7C1 criterion has provided a first estimate of the exposure indices for spatial areas potentially affected by a change in the current, tidal, wave, bottom nature, turbidity, salinity and thermal regime. Indeed, the results show that the pressures related to a change in the current, tidal and wave regime are relatively low (< 1% of the northern subdivision of the Bay of Biscay marine sub-region). They do not affect the wide area and therefore represent 0% of the area of this MRU. Pressures related to a change in bottom nature and turbidity regime potentially affect a relatively small area (22% of the MRU), so the offshore area is the least affected. The exposure indices calculated for these pressures are mostly low (78% of the area of the MRU is subject to a low exposure index). Finally, pressures related to a change in the thermal and salinity regime affect less than 1% of the MRU.
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017) no threshold is to be specified for D7C1: the status of the D7C1 criterion is therefore not reported. However, the assessment of the D7C1 criterion has provided a first estimate of the exposure indices for spatial areas potentially affected by a change in the current, tidal, wave, bottom nature, turbidity, salinity and thermal regime. Indeed, the results show that the pressures related to a change in the current, tidal and wave regime are relatively low (< 1% of the northern subdivision of the Bay of Biscay marine sub-region). They do not affect the wide area and therefore represent 0% of the area of this MRU. Pressures related to a change in bottom nature and turbidity regime potentially affect a relatively small area (22% of the MRU), so the offshore area is the least affected. The exposure indices calculated for these pressures are mostly low (78% of the area of the MRU is subject to a low exposure index). Finally, pressures related to a change in the thermal and salinity regime affect less than 1% of the MRU.
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017) no threshold is to be specified for D7C1: the status of the D7C1 criterion is therefore not reported. However, the assessment of the D7C1 criterion has provided a first estimate of the exposure indices for spatial areas potentially affected by a change in the current, tidal, wave, bottom nature, turbidity, salinity and thermal regime. Indeed, the results show that the pressures related to a change in the current, tidal and wave regime are relatively low (< 1% of the northern subdivision of the Bay of Biscay marine sub-region). They do not affect the wide area and therefore represent 0% of the area of this MRU. Pressures related to a change in bottom nature and turbidity regime potentially affect a relatively small area (22% of the MRU), so the offshore area is the least affected. The exposure indices calculated for these pressures are mostly low (78% of the area of the MRU is subject to a low exposure index). Finally, pressures related to a change in the thermal and salinity regime affect less than 1% of the MRU.
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017) no threshold is to be specified for D7C1: the status of the D7C1 criterion is therefore not reported. However, the assessment of the D7C1 criterion has provided a first estimate of the exposure indices for spatial areas potentially affected by a change in the current, tidal, wave, bottom nature, turbidity, salinity and thermal regime. Indeed, the results show that the pressures related to a change in the current, tidal and wave regime are relatively low (< 1% of the northern subdivision of the Bay of Biscay marine sub-region). They do not affect the wide area and therefore represent 0% of the area of this MRU. Pressures related to a change in bottom nature and turbidity regime potentially affect a relatively small area (22% of the MRU), so the offshore area is the least affected. The exposure indices calculated for these pressures are mostly low (78% of the area of the MRU is subject to a low exposure index). Finally, pressures related to a change in the thermal and salinity regime affect less than 1% of the MRU.
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017) no threshold is to be specified for D7C1: the status of the D7C1 criterion is therefore not reported. However, the assessment of the D7C1 criterion has provided a first estimate of the exposure indices for spatial areas potentially affected by a change in the current, tidal, wave, bottom nature, turbidity, salinity and thermal regime. Indeed, the results show that the pressures related to a change in the current, tidal and wave regime are relatively low (< 1% of the northern subdivision of the Bay of Biscay marine sub-region). They do not affect the wide area and therefore represent 0% of the area of this MRU. Pressures related to a change in bottom nature and turbidity regime potentially affect a relatively small area (22% of the MRU), so the offshore area is the least affected. The exposure indices calculated for these pressures are mostly low (78% of the area of the MRU is subject to a low exposure index). Finally, pressures related to a change in the thermal and salinity regime affect less than 1% of the MRU.
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017) no threshold is to be specified for D7C1: the status of the D7C1 criterion is therefore not reported. However, the assessment of the D7C1 criterion has provided a first estimate of the exposure indices for spatial areas potentially affected by a change in the current, tidal, wave, bottom nature, turbidity, salinity and thermal regime. Indeed, the results show that the pressures related to a change in the current, tidal and wave regime are relatively low (< 1% of the northern subdivision of the Bay of Biscay marine sub-region). They do not affect the wide area and therefore represent 0% of the area of this MRU. Pressures related to a change in bottom nature and turbidity regime potentially affect a relatively small area (22% of the MRU), so the offshore area is the least affected. The exposure indices calculated for these pressures are mostly low (78% of the area of the MRU is subject to a low exposure index). Finally, pressures related to a change in the thermal and salinity regime affect less than 1% of the MRU.
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017) no threshold is to be specified for D7C1: the status of the D7C1 criterion is therefore not reported. However, the assessment of the D7C1 criterion has provided a first estimate of the exposure indices for spatial areas potentially affected by a change in the current, tidal, wave, bottom nature, turbidity, salinity and thermal regime. Indeed, the results show that the pressures related to a change in the current, tidal and wave regime are relatively low (< 1% of the northern subdivision of the Bay of Biscay marine sub-region). They do not affect the wide area and therefore represent 0% of the area of this MRU. Pressures related to a change in bottom nature and turbidity regime potentially affect a relatively small area (22% of the MRU), so the offshore area is the least affected. The exposure indices calculated for these pressures are mostly low (78% of the area of the MRU is subject to a low exposure index). Finally, pressures related to a change in the thermal and salinity regime affect less than 1% of the MRU.
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017), the D7C2 assessment must be carried out for each habitat type that is affected by changing hydrographic conditions and the D7C2 results are not integrated. On the other hand, no threshold has been defined so far for the parameter "Extent" and therefore the status of D7C2 is not reported, but the assessment of D7C2 has provided a first estimate of the spatial extent of benthic habitats potentially subject to cumulative risks of alteration, based on the indices of exposure to hydrographic pressures generated by human activities. For example, 51% of the area of offshore circalittoral coarse sediment habitat appears to be at medium risk.
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017), the D7C2 assessment must be carried out for each habitat type that is affected by changing hydrographic conditions and the D7C2 results are not integrated. On the other hand, no threshold has been defined so far for the parameter "Extent" and therefore the status of D7C2 is not reported, but the assessment of D7C2 has provided a first estimate of the spatial extent of benthic habitats potentially subject to cumulative risks of alteration, based on the indices of exposure to hydrographic pressures generated by human activities. Thus, 54% of the area of "Heterogeneous offshore circalittoral sediment" habitat appears to be at medium risk.
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017), the D7C2 assessment must be carried out for each habitat type that is affected by changing hydrographic conditions and the D7C2 results are not integrated. On the other hand, no threshold has been defined so far for the parameter "Extent" and therefore the status of D7C2 is not reported, but the assessment of D7C2 has provided a first estimate of the spatial extent of benthic habitats potentially subject to cumulative risks of alteration, based on the indices of exposure to hydrographic pressures generated by human activities. Thus, 64% of the area of "offshore circalittoral mud flats" habitat appears to be at medium risk.
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017), the D7C2 assessment must be carried out for each habitat type that is affected by changing hydrographic conditions and the D7C2 results are not integrated. On the other hand, no threshold has been defined so far for the parameter "Extent" and therefore the status of D7C2 is not reported, but the assessment of D7C2 has provided a first estimate of the spatial extent of benthic habitats potentially subject to cumulative risks of alteration, based on the indices of exposure to hydrographic pressures generated by human activities. Thus, 68% of the area of offshore circalittoral sands habitat appears to be at medium risk.
Element status
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Description element
The assessment of criterion D7C1 contributes to the assessment of criterion D7C2. Thus, the accumulation of quantified pressures (i.e., exposure indices) under D7C1 is incorporated into the calculation of the risk of modification of each habitat for the D7C2 assessment.
The assessment of criterion D7C1 contributes to the assessment of criterion D7C2. Thus, the accumulation of quantified pressures (i.e., exposure indices) under D7C1 is incorporated into the calculation of the risk of modification of each habitat for the D7C2 assessment.
The assessment of criterion D7C1 contributes to the assessment of criterion D7C2. Thus, the accumulation of quantified pressures (i.e., exposure indices) under D7C1 is incorporated into the calculation of the risk of modification of each habitat for the D7C2 assessment.
The assessment of criterion D7C1 contributes to the assessment of criterion D7C2. Thus, the accumulation of quantified pressures (i.e., exposure indices) under D7C1 is incorporated into the calculation of the risk of modification of each habitat for the D7C2 assessment.
The assessment of criterion D7C1 contributes to the assessment of criterion D7C2. Thus, the accumulation of quantified pressures (i.e., exposure indices) under D7C1 is incorporated into the calculation of the risk of modification of each habitat for the D7C2 assessment.
The assessment of criterion D7C1 contributes to the assessment of criterion D7C2. Thus, the accumulation of quantified pressures (i.e., exposure indices) under D7C1 is incorporated into the calculation of the risk of modification of each habitat for the D7C2 assessment.
The assessment of criterion D7C1 contributes to the assessment of criterion D7C2. Thus, the accumulation of quantified pressures (i.e., exposure indices) under D7C1 is incorporated into the calculation of the risk of modification of each habitat for the D7C2 assessment.
In the absence of a threshold for the "Extent" parameter, the state of the habitat could not be provided. Furthermore, according to Decision 2017/848/EU, the results of the assessment of criterion D7C2 (estimated extent of adverse effects by habitat type in each assessment area) are used for the assessment of criterion D6C5. However, in the absence of an operational indicator at the level of Descriptor 6 - Benthic Habitats, these results could not be taken into account in the assessment of D6C5.
In the absence of a threshold for the "Extent" parameter, the state of the habitat could not be provided. Furthermore, according to Decision 2017/848/EU, the results of the assessment of criterion D7C2 (estimated extent of adverse effects by habitat type in each assessment area) are used for the assessment of criterion D6C5. However, in the absence of an operational indicator at the level of Descriptor 6 - Benthic Habitats, these results could not be taken into account in the assessment of D6C5.
In the absence of a threshold for the "Extent" parameter, the state of the habitat could not be provided. Furthermore, according to Decision 2017/848/EU, the results of the assessment of criterion D7C2 (estimated extent of adverse effects by habitat type in each assessment area) are used for the assessment of criterion D6C5. However, in the absence of an operational indicator at the level of Descriptor 6 - Benthic Habitats, these results could not be taken into account in the assessment of D6C5.
In the absence of a threshold for the "Extent" parameter, the state of the habitat could not be provided. Furthermore, according to Decision 2017/848/EU, the results of the assessment of criterion D7C2 (estimated extent of adverse effects by habitat type in each assessment area) are used for the assessment of criterion D6C5. However, in the absence of an operational indicator at the level of Descriptor 6 - Benthic Habitats, these results could not be taken into account in the assessment of D6C5.
Integration rule type parameter
Not relevant
Not relevant
Not relevant
Not relevant
Not relevant
Not relevant
Not relevant
Not relevant
Not relevant
Not relevant
Not relevant
Integration rule description parameter
Integration rule type criteria
Not relevant
Not relevant
Not relevant
Not relevant
Not relevant
Not relevant
Not relevant
Not relevant
Not relevant
Not relevant
Not relevant
Integration rule description criteria
GES extent threshold
GES extent achieved
GES extent unit
GES achieved
Not relevant
Not relevant
Not relevant
Not relevant
Not relevant
Not relevant
Not relevant
Not relevant
Not relevant
Not relevant
Not relevant
Description overall status
The D7 assessment, based on data on anthropogenic activities, highlighted significant variations in exposure to pressures:1/ The L200 zone is less subject than the coastal zone (MEC DCE) to exposure to the hydrographic pressures under consideration.2/ The modification pressures of "turbidity" and "bottom nature" present the largest areas of potential exposure (58% of the northern subdivision of the Bay of Biscay marine sub-region). However, the exposure index remains mostly low, and for 90% of the major benthic habitat types, the area of habitat potentially subject to medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
The D7 assessment, based on data on anthropogenic activities, highlighted significant variations in exposure to pressures:1/ The L200 zone is less subject than the coastal zone (MEC DCE) to exposure to the hydrographic pressures under consideration.2/ The modification pressures of "turbidity" and "bottom nature" present the largest areas of potential exposure (58% of the northern subdivision of the Bay of Biscay marine sub-region). However, the exposure index remains mostly low, and for 90% of the major benthic habitat types, the area of habitat potentially subject to medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
The D7 assessment, based on data on anthropogenic activities, highlighted significant variations in exposure to pressures:1/ The L200 zone is less subject than the coastal zone (MEC DCE) to exposure to the hydrographic pressures under consideration.2/ The modification pressures of "turbidity" and "bottom nature" present the largest areas of potential exposure (58% of the northern subdivision of the Bay of Biscay marine sub-region). However, the exposure index remains mostly low, and for 90% of the major benthic habitat types, the area of habitat potentially subject to medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
The D7 assessment, based on data on anthropogenic activities, highlighted significant variations in exposure to pressures:1/ The L200 zone is less subject than the coastal zone (MEC DCE) to exposure to the hydrographic pressures under consideration.2/ The modification pressures of "turbidity" and "bottom nature" present the largest areas of potential exposure (58% of the northern subdivision of the Bay of Biscay marine sub-region). However, the exposure index remains mostly low, and for 90% of the major benthic habitat types, the area of habitat potentially subject to medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
The D7 assessment, based on data on anthropogenic activities, highlighted significant variations in exposure to pressures:1/ The L200 zone is less subject than the coastal zone (MEC DCE) to exposure to the hydrographic pressures under consideration.2/ The modification pressures of "turbidity" and "bottom nature" present the largest areas of potential exposure (58% of the northern subdivision of the Bay of Biscay marine sub-region). However, the exposure index remains mostly low, and for 90% of the major benthic habitat types, the area of habitat potentially subject to medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
The D7 assessment, based on data on anthropogenic activities, highlighted significant variations in exposure to pressures:1/ The L200 zone is less subject than the coastal zone (MEC DCE) to exposure to the hydrographic pressures under consideration.2/ The modification pressures of "turbidity" and "bottom nature" present the largest areas of potential exposure (58% of the northern subdivision of the Bay of Biscay marine sub-region). However, the exposure index remains mostly low, and for 90% of the major benthic habitat types, the area of habitat potentially subject to medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
The D7 assessment, based on data on anthropogenic activities, highlighted significant variations in exposure to pressures:1/ The L200 zone is less subject than the coastal zone (MEC DCE) to exposure to the hydrographic pressures under consideration.2/ The modification pressures of "turbidity" and "bottom nature" present the largest areas of potential exposure (58% of the northern subdivision of the Bay of Biscay marine sub-region). However, the exposure index remains mostly low, and for 90% of the major benthic habitat types, the area of habitat potentially subject to medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
The D7 assessment, based on data on anthropogenic activities, highlighted significant variations in exposure to pressures:1/ The L200 zone is less subject than the coastal zone (MEC DCE) to exposure to the hydrographic pressures under consideration.2/ The modification pressures of "turbidity" and "bottom nature" present the largest areas of potential exposure (58% of the northern subdivision of the Bay of Biscay marine sub-region). However, the exposure index remains mostly low, and for 90% of the major benthic habitat types, the area of habitat potentially subject to medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
The D7 assessment, based on data on anthropogenic activities, highlighted significant variations in exposure to pressures:1/ The L200 zone is less subject than the coastal zone (MEC DCE) to exposure to the hydrographic pressures under consideration.2/ The modification pressures of "turbidity" and "bottom nature" present the largest areas of potential exposure (58% of the northern subdivision of the Bay of Biscay marine sub-region). However, the exposure index remains mostly low, and for 90% of the major benthic habitat types, the area of habitat potentially subject to medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
The D7 assessment, based on data on anthropogenic activities, highlighted significant variations in exposure to pressures:1/ The L200 zone is less subject than the coastal zone (MEC DCE) to exposure to the hydrographic pressures under consideration.2/ The modification pressures of "turbidity" and "bottom nature" present the largest areas of potential exposure (58% of the northern subdivision of the Bay of Biscay marine sub-region). However, the exposure index remains mostly low, and for 90% of the major benthic habitat types, the area of habitat potentially subject to medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
The D7 assessment, based on data on anthropogenic activities, highlighted significant variations in exposure to pressures:1/ The L200 zone is less subject than the coastal zone (MEC DCE) to exposure to the hydrographic pressures under consideration.2/ The modification pressures of "turbidity" and "bottom nature" present the largest areas of potential exposure (58% of the northern subdivision of the Bay of Biscay marine sub-region). However, the exposure index remains mostly low, and for 90% of the major benthic habitat types, the area of habitat potentially subject to medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
Assessments period
2012-2018
2012-2018
2012-2018
2012-2018
2012-2018
2012-2018
2012-2018
2012-2018
2012-2018
2012-2018
2012-2018
Related pressures
Related targets

Nord SRM GdG MEC DCE (ABI-FR-MS-GDG-NORD-MEC2010)

GES component
D7
D7
D7
D7
D7
D7
D7
D7
D7
D7
D7
D7
D7
D7
D7
D7
D7
D7
D7
D7
Feature
Hydrographical changes
Hydrographical changes
Hydrographical changes
Hydrographical changes
Hydrographical changes
Hydrographical changes
Hydrographical changes
Benthic broad habitats
Benthic broad habitats
Benthic broad habitats
Benthic broad habitats
Benthic broad habitats
Benthic broad habitats
Benthic broad habitats
Benthic broad habitats
Benthic broad habitats
Benthic broad habitats
Benthic broad habitats
Benthic broad habitats
Benthic broad habitats
Element
Changes in current regime
Changes in salinity regime
Changes in seabed substrate
Changes in thermal regime
Changes in tide regime
Changes in turbidity regime
Changes in waves regime
Circalittoral coarse sediment
Circalittoral mixed sediment
Circalittoral mud
Circalittoral rock and biogenic reef
Circalittoral sand
Infralittoral coarse sediment
Infralittoral mixed sediment
Infralittoral mud
Infralittoral rock and biogenic reef
Infralittoral sand
Offshore circalittoral coarse sediment
Offshore circalittoral mud
Offshore circalittoral rock and biogenic reef
Element code
ExpPresCurrents
ExpPresSalinity
ExpPresSeabedNature
ExpPresTemperature
ExpPresTide
ExpPresTurbidity
ExpPresWaves
HabBenCircalitCoarSed
HabBenCircalitMxdSed
HabBenCircalitMud
HabBenCircalitRock
HabBenCircalitSand
HabBenInfralitCoarSed
HabBenInfralitMxdSed
HabBenInfralitMud
HabBenInfralitRock
HabBenInfralitSand
HabBenOffshCoarSed
HabBenOffshMud
HabBenOffshRock
Element code source
Link to other vocabulary or code lists that may be relevant
Link to other vocabulary or code lists that may be relevant
Link to other vocabulary or code lists that may be relevant
Link to other vocabulary or code lists that may be relevant
Link to other vocabulary or code lists that may be relevant
Link to other vocabulary or code lists that may be relevant
Link to other vocabulary or code lists that may be relevant
Habitats (D1-D6) http://dd.eionet.europa.eu/vocabulary/msfd/broadHabitatTypes/view
Habitats (D1-D6) http://dd.eionet.europa.eu/vocabulary/msfd/broadHabitatTypes/view
Habitats (D1-D6) http://dd.eionet.europa.eu/vocabulary/msfd/broadHabitatTypes/view
Habitats (D1-D6) http://dd.eionet.europa.eu/vocabulary/msfd/broadHabitatTypes/view
Habitats (D1-D6) http://dd.eionet.europa.eu/vocabulary/msfd/broadHabitatTypes/view
Habitats (D1-D6) http://dd.eionet.europa.eu/vocabulary/msfd/broadHabitatTypes/view
Habitats (D1-D6) http://dd.eionet.europa.eu/vocabulary/msfd/broadHabitatTypes/view
Habitats (D1-D6) http://dd.eionet.europa.eu/vocabulary/msfd/broadHabitatTypes/view
Habitats (D1-D6) http://dd.eionet.europa.eu/vocabulary/msfd/broadHabitatTypes/view
Habitats (D1-D6) http://dd.eionet.europa.eu/vocabulary/msfd/broadHabitatTypes/view
Habitats (D1-D6) http://dd.eionet.europa.eu/vocabulary/msfd/broadHabitatTypes/view
Habitats (D1-D6) http://dd.eionet.europa.eu/vocabulary/msfd/broadHabitatTypes/view
Habitats (D1-D6) http://dd.eionet.europa.eu/vocabulary/msfd/broadHabitatTypes/view
Element 2
Element 2 code
Element 2 code source
Element source
National
National
National
National
National
National
National
EU
EU
EU
EU
EU
EU
EU
EU
EU
EU
EU
EU
EU
Criterion
D7C1
D7C1
D7C1
D7C1
D7C1
D7C1
D7C1
D7C2
D7C2
D7C2
D7C2
D7C2
D7C2
D7C2
D7C2
D7C2
D7C2
D7C2
D7C2
D7C2
Parameter
Extent
Extent
Extent
Extent
Extent
Extent
Extent
Extent
Extent
Extent
Extent
Extent
Extent
Extent
Extent
Extent
Extent
Extent
Extent
Extent
Parameter other
Threshold value upper
Threshold value lower
Threshold qualitative
Not available yet
Not available yet
Not available yet
Not available yet
Not available yet
Not available yet
Not available yet
Not available yet
Not available yet
Not available yet
Not available yet
Not available yet
Not available yet
Not available yet
Not available yet
Not available yet
Not available yet
Not available yet
Not available yet
Not available yet
Threshold value source
Threshold value source other
Value achieved upper
Value achieved lower
Value unit
Value unit other
Proportion threshold value
Proportion value achieved
690.0
10.0
5649.0
10.0
646.0
5608.0
646.0
969.0
107.0
941.0
1017.0
896.0
385.0
21.0
161.0
543.0
305.0
10.0
38.0
24.0
Proportion threshold value unit
extent in km2 of pressure
extent in km2 of pressure
extent in km2 of pressure
extent in km2 of pressure
extent in km2 of pressure
extent in km2 of pressure
extent in km2 of pressure
extent in km2 of habitat adversely affected
extent in km2 of habitat adversely affected
extent in km2 of habitat adversely affected
extent in km2 of habitat adversely affected
extent in km2 of habitat adversely affected
extent in km2 of habitat adversely affected
extent in km2 of habitat adversely affected
extent in km2 of habitat adversely affected
extent in km2 of habitat adversely affected
extent in km2 of habitat adversely affected
extent in km2 of habitat adversely affected
extent in km2 of habitat adversely affected
extent in km2 of habitat adversely affected
Trend
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Parameter achieved
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Description parameter
The metric considered for this parameter is the area of exposure for each pressure considered (overall or as a function of the level of the exposure index). The areas potentially affected by a change in the current regime correspond to a total area of 690 km2 , based on the four levels of exposure index: No exposure: 5121 km² Low exposure index: 608 km² Medium exposure index: 82 km² High exposure index: 0 km² Note that no threshold is currently available to assess whether or not the parameter has been reached.
The metric considered for this parameter is the area of exposure for each pressure considered (overall or as a function of the level of the exposure index). The areas potentially affected by a change in salinity regime correspond to a total surface area of <10 km2 . The areas of exposure according to the four levels of the exposure index are No exposure: 5753 km² Low exposure index: <10 km² Medium exposure index: 0 km² High exposure index: 0 km² Note that no threshold is currently available to assess whether or not the parameter has been reached.
The metric considered for this parameter is the area of exposure for each pressure considered (overall or as a function of the level of the exposure index). The areas potentially affected by a change in the background nature correspond to a total area of 5649 km2 , based on the four levels of exposure index: No exposure: 161 km² Low exposure index: 5591 km² Medium exposure index: 58 km² High exposure index: 0 km² Note that no threshold is currently available to assess whether or not the parameter has been reached.
The metric considered for this parameter is the area of exposure for each pressure considered (overall or as a function of the level of the exposure index). The areas potentially affected by a change in the thermal regime correspond to a total surface area of <10 km2 . The areas of exposure according to the four levels of the exposure index are No exposure: 5753 km² Low exposure index: <10 km² Medium exposure index: 0 km² High exposure index: 0 km² Note that no threshold is currently available to assess whether or not the parameter has been reached.
The metric considered for this parameter is the area of exposure for each pressure considered (overall or as a function of the level of the exposure index). The areas potentially affected by a change in the tidal regime correspond to a total area of 646 km2 , based on the four levels of exposure index: No exposure: 5165 km² Low exposure index: 508 km² Medium exposure index: 137 km² High exposure index: 0 km² Note that no threshold is currently available to assess whether or not the parameter has been reached.
The metric considered for this parameter is the area of exposure for each pressure considered (overall or as a function of the level of the exposure index). The areas potentially affected by a change in the turbidity regime correspond to a total area of 5608 km2 . The areas of exposure according to the four levels of exposure index are: No exposure: 203 km² Low exposure index: 4811 km² Medium exposure index: 793 km² High exposure index: 3 km² Note that no threshold is currently available to assess whether or not the parameter has been reached.
The metric considered for this parameter is the area of exposure for each pressure considered (overall or as a function of the level of the exposure index). The areas potentially affected by a change in the wave regime correspond to a total area of 646 km2 , based on the four levels of exposure index: No Exposure: 5165 km² Low Exposure Index: 639 km² Medium Exposure Index: 7 km² High Exposure Index: 0 km² Note that no threshold is currently available to assess whether or not the parameter has been reached.
The metric considered for this parameter is the area of habitat potentially at risk (overall or based on the level of risk). The spatial extent of potential habitat modification related to permanent changes in hydrographic conditions in this MRU is 969 km2 (i.e. 100% of the habitat assessed). Furthermore, the indicator makes it possible to assess the intensity of the risk of modification: negligible or no risk of modification: 0 km².low risk of modification: 158 km².medium risk of modification: 797 km².high risk of modification: 14 km².It should be noted that no threshold is currently available to assess whether or not the parameter has been reached.
The metric considered for this parameter is the area of habitat potentially at risk (overall or as a function of the level of risk). The spatial extent of potential habitat modification related to permanent changes in hydrographic conditions in this MRU is 107 km2 (i.e. 100% of the habitat assessed). Furthermore, the indicator makes it possible to assess the intensity of the risk of modification: negligible or no risk of modification: 0 km², low risk of modification: 14 km², medium risk of modification: 89 km², high risk of modification: 3 km², although no threshold is currently available to assess whether or not the parameter has been reached.
The metric considered for this parameter is the area of habitat potentially at risk (overall or based on the level of risk). The spatial extent of potential habitat modification related to permanent changes in hydrographic conditions in this MRU is 941 km2 (i.e. 99% of the habitat assessed). In addition, the indicator makes it possible to assess the intensity of the risk of modification: negligible or nil risk of modification: 14 km², low risk of modification: 203 km², medium risk of modification: 728 km², high risk of modification: 10 km², it should be noted that no threshold is currently available to assess whether or not the parameter has been reached.
The metric considered for this parameter is the area of habitat potentially at risk (overall or based on the level of risk). The spatial extent of potential habitat alteration associated with permanent changes in hydrographic conditions in this MRU is 1017 km2 (i.e. >99% of the assessed habitat). Furthermore, the indicator makes it possible to assess the intensity of the risk of modification: negligible or nil risk of modification: 3 km², low risk of modification: 248 km², medium risk of modification: 745 km², high risk of modification: 24 km², although no threshold is currently available to assess whether or not the parameter has been reached.
The metric considered for this parameter is the area of habitat potentially at risk (overall or based on the level of risk). The spatial extent of potential habitat modification related to permanent changes in hydrographic conditions in this MRU is 896 km2 (i.e. 100% of the habitat assessed). In addition, the indicator makes it possible to assess the intensity of the risk of modification: negligible or nil risk of modification: 0 km², low risk of modification: 182 km², medium risk of modification: 704 km², high risk of modification: 10 km², although no threshold is currently available to assess whether or not the parameter has been reached.
The metric considered for this parameter is the area of habitat potentially at risk (overall or as a function of the level of risk). The spatial extent of potential habitat modification related to permanent changes in hydrographic conditions in this MRU is 385 km2 (i.e. 100% of the habitat assessed). Furthermore, the indicator makes it possible to assess the intensity of the risk of modification: negligible or nil risk of modification: 0 km², low risk of modification: 124 km², medium risk of modification: 234 km², high risk of modification: 28 km², although no threshold is currently available to assess whether or not the parameter has been reached.
The metric considered for this parameter is the area of habitat potentially at risk (overall or as a function of the level of risk). The spatial extent of potential habitat modification related to permanent changes in hydrographic conditions in this MRU is 21 km2 (i.e. 100% of the habitat assessed). Furthermore, the indicator makes it possible to assess the intensity of the risk of modification: negligible or no risk of modification: 0 km², low risk of modification: 7 km², medium risk of modification: 7 km², high risk of modification: 7 km², etc. It should be noted that no threshold is currently available to assess whether or not the parameter has been reached.
The metric considered for this parameter is the area of habitat potentially at risk (overall or as a function of the level of risk). The spatial extent of potential habitat modification related to permanent changes in hydrographic conditions in this MRU is 161 km2 (87% of the assessed habitat). In addition, the indicator makes it possible to assess the intensity of the risk of modification: negligible or nil risk of modification: 24 km², low risk of modification: 48 km², medium risk of modification: 31 km², high risk of modification: 82 km², it should be noted that no threshold is currently available to assess whether or not the parameter has been reached.
The metric considered for this parameter is the area of habitat potentially at risk (overall or by level of risk). The spatial extent of potential habitat alteration due to permanent changes in hydrographic conditions in this MRU is 543 km2 (>99% of the assessed habitat). In addition, the indicator makes it possible to assess the intensity of the risk of modification: negligible or nil risk of modification: 3 km², low risk of modification: 144 km², medium risk of modification: 295 km², high risk of modification: 103 km², it should be noted that no threshold is currently available to assess whether or not the parameter has been reached.
The metric considered for this parameter is the area of habitat potentially at risk (overall or based on the level of risk). The spatial extent of potential habitat modification related to permanent changes in hydrographic conditions in this MRU is 305 km2 (92% of the habitat assessed). In addition, the indicator makes it possible to assess the intensity of the risk of modification: negligible or nil risk of modification: 28 km², low risk of modification: 96 km², medium risk of modification: 179 km², high risk of modification: 31 km², although no threshold is currently available to assess whether or not the parameter has been reached.
The metric considered for this parameter is the area of habitat potentially at risk (overall or as a function of the level of risk). The spatial extent of potential habitat modification related to permanent changes in hydrographic conditions in this MRU is 10 km2 (i.e. 100% of the habitat assessed). Furthermore, the indicator makes it possible to assess the intensity of the risk of modification: negligible or nil risk of modification: 0 km², low risk of modification: 0 km², medium risk of modification: 10 km², high risk of modification: 0 km², although no threshold is currently available to assess whether or not the parameter has been reached.
The metric considered for this parameter is the area of habitat potentially at risk (overall or as a function of the level of risk). The spatial extent of potential habitat modification related to permanent changes in hydrographic conditions in this MRU is 38 km2 (i.e. 100% of the habitat assessed). Furthermore, the indicator makes it possible to assess the intensity of the risk of modification: negligible or no risk of modification: 0 km², low risk of modification: 3 km², medium risk of modification: 31 km², high risk of modification: 3 km², although no threshold is currently available to assess whether or not the parameter has been reached.
The metric considered for this parameter is the area of habitat potentially at risk (overall or as a function of the level of risk). The spatial extent of potential habitat modification related to permanent changes in hydrographic conditions in this MRU is 24 km2 (i.e. 100% of the habitat assessed). In addition, the indicator makes it possible to assess the intensity of the risk of modification: negligible or nil risk of modification: 14 km², low risk of modification: 7 km², medium risk of modification: 17 km², high risk of modification: 0 km², although no threshold is currently available to assess whether or not the parameter has been reached.
Related indicator
Criteria status
Contributes to assessment of another criterion/ele
Contributes to assessment of another criterion/ele
Contributes to assessment of another criterion/ele
Contributes to assessment of another criterion/ele
Contributes to assessment of another criterion/ele
Contributes to assessment of another criterion/ele
Contributes to assessment of another criterion/ele
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Description criteria
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017) no threshold is to be specified for D7C1: the status of the D7C1 criterion is therefore not reported. However, the assessment of the D7C1 criterion has provided a first estimate of the exposure indices for spatial areas potentially affected by a change in the current, tidal, wave, bottom nature, turbidity, salinity and thermal regime. Indeed, the results show that the pressures related to a change in the current, tidal and wave regime are relatively low (< 1% of the northern subdivision of the Gulf of Gas marine sub-region) and fairly localised since they mainly affect coastal waters. They each represent less than 12% of the area of this MRU. It should also be noted that the exposure indices calculated for these pressures are mostly low. Pressures related to a change in the nature of the bottom and turbidity regime potentially affect a very large area (97% of the MRU). The exposure indices calculated for the change in background are mostly low (>96% of the MRU), and higher for the change in turbidity regime in the coastal MRU (14% of the area of the MRU is subject to an average exposure index). Finally, pressures related to a change in the thermal and salinity regime affect less than 1% of the MRU.
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017) no threshold is to be specified for D7C1: the status of the D7C1 criterion is therefore not reported. However, the assessment of the D7C1 criterion has provided a first estimate of the exposure indices for spatial areas potentially affected by a change in the current, tidal, wave, bottom nature, turbidity, salinity and thermal regime. Indeed, the results show that the pressures related to a change in the current, tidal and wave regime are relatively low (< 1% of the northern subdivision of the Gulf of Gas marine sub-region) and fairly localised since they mainly affect coastal waters. They each represent less than 12% of the area of this MRU. It should also be noted that the exposure indices calculated for these pressures are mostly low. Pressures related to a change in the nature of the bottom and turbidity regime potentially affect a very large area (97% of the MRU). The exposure indices calculated for the change in background are mostly low (>96% of the MRU), and higher for the change in turbidity regime in the coastal MRU (14% of the area of the MRU is subject to an average exposure index). Finally, pressures related to a change in the thermal and salinity regime affect less than 1% of the MRU.
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017) no threshold is to be specified for D7C1: the status of the D7C1 criterion is therefore not reported. However, the assessment of the D7C1 criterion has provided a first estimate of the exposure indices for spatial areas potentially affected by a change in the current, tidal, wave, bottom nature, turbidity, salinity and thermal regime. Indeed, the results show that the pressures related to a change in the current, tidal and wave regime are relatively low (< 1% of the northern subdivision of the Gulf of Gas marine sub-region) and fairly localised since they mainly affect coastal waters. They each represent less than 12% of the area of this MRU. It should also be noted that the exposure indices calculated for these pressures are mostly low. Pressures related to a change in the nature of the bottom and turbidity regime potentially affect a very large area (97% of the MRU). The exposure indices calculated for the change in background are mostly low (>96% of the MRU), and higher for the change in turbidity regime in the coastal MRU (14% of the area of the MRU is subject to an average exposure index). Finally, pressures related to a change in the thermal and salinity regime affect less than 1% of the MRU.
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017) no threshold is to be specified for D7C1: the status of the D7C1 criterion is therefore not reported. However, the assessment of the D7C1 criterion has provided a first estimate of the exposure indices for spatial areas potentially affected by a change in the current, tidal, wave, bottom nature, turbidity, salinity and thermal regime. Indeed, the results show that the pressures related to a change in the current, tidal and wave regime are relatively low (< 1% of the northern subdivision of the Gulf of Gas marine sub-region) and fairly localised since they mainly affect coastal waters. They each represent less than 12% of the area of this MRU. It should also be noted that the exposure indices calculated for these pressures are mostly low. Pressures related to a change in the nature of the bottom and turbidity regime potentially affect a very large area (97% of the MRU). The exposure indices calculated for the change in background are mostly low (>96% of the MRU), and higher for the change in turbidity regime in the coastal MRU (14% of the area of the MRU is subject to an average exposure index). Finally, pressures related to a change in the thermal and salinity regime affect less than 1% of the MRU.
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017) no threshold is to be specified for D7C1: the status of the D7C1 criterion is therefore not reported. However, the assessment of the D7C1 criterion has provided a first estimate of the exposure indices for spatial areas potentially affected by a change in the current, tidal, wave, bottom nature, turbidity, salinity and thermal regime. Indeed, the results show that the pressures related to a change in the current, tidal and wave regime are relatively low (< 1% of the northern subdivision of the Gulf of Gas marine sub-region) and fairly localised since they mainly affect coastal waters. They each represent less than 12% of the area of this MRU. It should also be noted that the exposure indices calculated for these pressures are mostly low. Pressures related to a change in the nature of the bottom and turbidity regime potentially affect a very large area (97% of the MRU). The exposure indices calculated for the change in background are mostly low (>96% of the MRU), and higher for the change in turbidity regime in the coastal MRU (14% of the area of the MRU is subject to an average exposure index). Finally, pressures related to a change in the thermal and salinity regime affect less than 1% of the MRU.
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017) no threshold is to be specified for D7C1: the status of the D7C1 criterion is therefore not reported. However, the assessment of the D7C1 criterion has provided a first estimate of the exposure indices for spatial areas potentially affected by a change in the current, tidal, wave, bottom nature, turbidity, salinity and thermal regime. Indeed, the results show that the pressures related to a change in the current, tidal and wave regime are relatively low (< 1% of the northern subdivision of the Gulf of Gas marine sub-region) and fairly localised since they mainly affect coastal waters. They each represent less than 12% of the area of this MRU. It should also be noted that the exposure indices calculated for these pressures are mostly low. Pressures related to a change in the nature of the bottom and turbidity regime potentially affect a very large area (97% of the MRU). The exposure indices calculated for the change in background are mostly low (>96% of the MRU), and higher for the change in turbidity regime in the coastal MRU (14% of the area of the MRU is subject to an average exposure index). Finally, pressures related to a change in the thermal and salinity regime affect less than 1% of the MRU.
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017) no threshold is to be specified for D7C1: the status of the D7C1 criterion is therefore not reported. However, the assessment of the D7C1 criterion has provided a first estimate of the exposure indices for spatial areas potentially affected by a change in the current, tidal, wave, bottom nature, turbidity, salinity and thermal regime. Indeed, the results show that the pressures related to a change in the current, tidal and wave regime are relatively low (< 1% of the northern subdivision of the Gulf of Gas marine sub-region) and fairly localised since they mainly affect coastal waters. They each represent less than 12% of the area of this MRU. It should also be noted that the exposure indices calculated for these pressures are mostly low. Pressures related to a change in the nature of the bottom and turbidity regime potentially affect a very large area (97% of the MRU). The exposure indices calculated for the change in background are mostly low (>96% of the MRU), and higher for the change in turbidity regime in the coastal MRU (14% of the area of the MRU is subject to an average exposure index). Finally, pressures related to a change in the thermal and salinity regime affect less than 1% of the MRU.
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017), the D7C2 assessment must be carried out for each habitat type that is affected by changing hydrographic conditions and the D7C2 results are not integrated. On the other hand, no threshold has been defined so far for the parameter "Extent" and therefore the status of D7C2 is not reported, but the assessment of D7C2 has provided a first estimate of the spatial extent of benthic habitats potentially subject to cumulative risks of alteration, based on the indices of exposure to hydrographic pressures generated by human activities. Thus, the "Coastal Circumpolar Coarse Sediment" habitat presents a large area (82% of the MRU) subject to a medium risk and 2% to a high risk.
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017), the D7C2 assessment must be carried out for each habitat type that is affected by changing hydrographic conditions and the D7C2 results are not integrated. On the other hand, no threshold has been defined so far for the parameter "Extent" and therefore the status of D7C2 is not reported, but the assessment of D7C2 has provided a first estimate of the spatial extent of benthic habitats potentially subject to cumulative risks of alteration, based on the indices of exposure to hydrographic pressures generated by human activities. Thus, 84% of the surface area of the "Coastal Circumferential Heterogeneous Sediment" habitat appears to be subject to a medium risk and 3% to a high risk.
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017), the D7C2 assessment must be carried out for each habitat type that is affected by changing hydrographic conditions and the D7C2 results are not integrated. On the other hand, no threshold has been defined so far for the parameter "Extent" and therefore the status of D7C2 is not reported, but the assessment of D7C2 has provided a first estimate of the spatial extent of benthic habitats potentially subject to cumulative risks of alteration, based on the indices of exposure to hydrographic pressures generated by human activities. Thus, 76% of the "Coastal Circumvalittoral Mudflats" habitat area appears to be subject to a medium risk and 1% to a high risk.
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017), the D7C2 assessment must be carried out for each habitat type that is affected by changing hydrographic conditions and the D7C2 results are not integrated. On the other hand, no threshold has been defined so far for the parameter "Extent" and therefore the status of D7C2 is not reported, but the assessment of D7C2 has provided a first estimate of the spatial extent of benthic habitats potentially subject to cumulative risks of alteration, based on the indices of exposure to hydrographic pressures generated by human activities. Thus, 73% of the surface area of the "Coastal Circumpolar Biogenic Rocks and Reefs" habitat appears to be at medium risk and 2% at high risk.
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017), the D7C2 assessment must be carried out for each habitat type that is affected by changing hydrographic conditions and the D7C2 results are not integrated. On the other hand, no threshold has been defined so far for the parameter "Extent" and therefore the status of D7C2 is not reported, but the assessment of D7C2 has provided a first estimate of the spatial extent of benthic habitats potentially subject to cumulative risks of alteration, based on the indices of exposure to hydrographic pressures generated by human activities. Thus, 79% of the area of "Coastal Circalittoral Sand" habitat appears to be at medium risk and 1% at high risk.
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017), the D7C2 assessment must be carried out for each habitat type that is affected by changing hydrographic conditions and the D7C2 results are not integrated. On the other hand, no threshold has been defined so far for the parameter "Extent" and therefore the status of D7C2 is not reported, but the assessment of D7C2 has provided a first estimate of the spatial extent of benthic habitats potentially subject to cumulative risks of alteration, based on the indices of exposure to hydrographic pressures generated by human activities. Thus, the " infralittoral coarse sediment " habitat presents a high risk area of 7% of the total habitat area.
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017), the D7C2 assessment must be carried out for each habitat type that is affected by changing hydrographic conditions and the D7C2 results are not integrated. On the other hand, no threshold has been defined so far for the parameter "Extent" and therefore the status of D7C2 is not reported, but the assessment of D7C2 has provided a first estimate of the spatial extent of benthic habitats potentially subject to cumulative risks of alteration, based on the indices of exposure to hydrographic pressures generated by human activities. Thus, the "mixed infralittoral sediment" habitat presents one of the largest areas at high risk, with 33% of the total habitat area at high risk, and 33% at medium risk.
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017), the D7C2 assessment must be carried out for each habitat type that is affected by changing hydrographic conditions and the D7C2 results are not integrated. On the other hand, no threshold has been defined so far for the parameter "Extent" and therefore the status of D7C2 is not reported, but the assessment of D7C2 has provided a first estimate of the spatial extent of benthic habitats potentially subject to cumulative risks of alteration, based on the indices of exposure to hydrographic pressures generated by human activities. Thus, the " infralittoral mud " habitat presents the largest area at high risk, with 44% of the total area of habitat subject to a high risk, and 17% subject to a medium risk.
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017), the D7C2 assessment must be carried out for each habitat type that is affected by changing hydrographic conditions and the D7C2 results are not integrated. On the other hand, no threshold has been defined so far for the parameter "Extent" and therefore the status of D7C2 is not reported, but the assessment of D7C2 has provided a first estimate of the spatial extent of benthic habitats potentially subject to cumulative risks of alteration, based on the indices of exposure to hydrographic pressures generated by human activities. Thus, the "Infralittoral rock and biogenic reef" habitat presents a large area at high risk (19% of the total habitat area), and a larger area at medium risk (54% of the MRU).
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017), the D7C2 assessment must be carried out for each habitat type that is affected by changing hydrographic conditions and the D7C2 results are not integrated. On the other hand, no threshold has been defined so far for the parameter "Extent" and therefore the status of D7C2 is not reported, but the assessment of D7C2 has provided a first estimate of the spatial extent of benthic habitats potentially subject to cumulative risks of alteration, based on the indices of exposure to hydrographic pressures generated by human activities. Thus, " infralittoral sands " habitat presents a high-risk area of 9% of the total habitat area, and a medium-risk area of 54% of the MRU.
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017), the D7C2 assessment must be carried out for each habitat type that is affected by changing hydrographic conditions and the D7C2 results are not integrated. On the other hand, no threshold has been defined so far for the parameter "Extent" and therefore the status of D7C2 is not reported, but the assessment of D7C2 has provided a first estimate of the spatial extent of benthic habitats potentially subject to cumulative risks of alteration, based on the indices of exposure to hydrographic pressures generated by human activities. Thus, all of the "offshore circalittoral coarse sediment" habitat appears to be at medium risk (100% of the total area of habitat in the MRU).
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017), the D7C2 assessment must be carried out for each habitat type that is affected by changing hydrographic conditions and the D7C2 results are not integrated. On the other hand, no threshold has been defined so far for the parameter "Extent" and therefore the status of D7C2 is not reported, but the assessment of D7C2 has provided a first estimate of the spatial extent of benthic habitats potentially subject to cumulative risks of alteration, based on the indices of exposure to hydrographic pressures generated by human activities. Thus, 82% of the area of "offshore circalittoral mud flats" habitat appears to be at medium risk and 9% at high risk.
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017), the D7C2 assessment must be carried out for each habitat type that is affected by changing hydrographic conditions and the D7C2 results are not integrated. On the other hand, no threshold has been defined so far for the parameter "Extent" and therefore the status of D7C2 is not reported, but the assessment of D7C2 has provided a first estimate of the spatial extent of benthic habitats potentially subject to cumulative risks of alteration, based on the indices of exposure to hydrographic pressures generated by human activities. For example, the "Offshore Circumpolar Biogenic Rocks and Reefs" habitat presents a large area at medium risk with 71% of the total habitat area at medium risk.
Element status
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Description element
The assessment of criterion D7C1 contributes to the assessment of criterion D7C2. Thus, the accumulation of quantified pressures (i.e., exposure indices) under D7C1 is incorporated into the calculation of the risk of modification of each habitat for the D7C2 assessment.
The assessment of criterion D7C1 contributes to the assessment of criterion D7C2. Thus, the accumulation of quantified pressures (i.e., exposure indices) under D7C1 is incorporated into the calculation of the risk of modification of each habitat for the D7C2 assessment.
The assessment of criterion D7C1 contributes to the assessment of criterion D7C2. Thus, the accumulation of quantified pressures (i.e., exposure indices) under D7C1 is incorporated into the calculation of the risk of modification of each habitat for the D7C2 assessment.
The assessment of criterion D7C1 contributes to the assessment of criterion D7C2. Thus, the accumulation of quantified pressures (i.e., exposure indices) under D7C1 is incorporated into the calculation of the risk of modification of each habitat for the D7C2 assessment.
The assessment of criterion D7C1 contributes to the assessment of criterion D7C2. Thus, the accumulation of quantified pressures (i.e., exposure indices) under D7C1 is incorporated into the calculation of the risk of modification of each habitat for the D7C2 assessment.
The assessment of criterion D7C1 contributes to the assessment of criterion D7C2. Thus, the accumulation of quantified pressures (i.e., exposure indices) under D7C1 is incorporated into the calculation of the risk of modification of each habitat for the D7C2 assessment.
The assessment of criterion D7C1 contributes to the assessment of criterion D7C2. Thus, the accumulation of quantified pressures (i.e., exposure indices) under D7C1 is incorporated into the calculation of the risk of modification of each habitat for the D7C2 assessment.
In the absence of a threshold for the "Extent" parameter, the state of the habitat could not be provided. Furthermore, according to Decision 2017/848/EU, the results of the assessment of criterion D7C2 (estimated extent of adverse effects by habitat type in each assessment area) are used for the assessment of criterion D6C5. However, in the absence of an operational indicator at the level of Descriptor 6 - Benthic Habitats, these results could not be taken into account in the assessment of D6C5.
In the absence of a threshold for the "Extent" parameter, the state of the habitat could not be provided. Furthermore, according to Decision 2017/848/EU, the results of the assessment of criterion D7C2 (estimated extent of adverse effects by habitat type in each assessment area) are used for the assessment of criterion D6C5. However, in the absence of an operational indicator at the level of Descriptor 6 - Benthic Habitats, these results could not be taken into account in the assessment of D6C5.
In the absence of a threshold for the "Extent" parameter, the state of the habitat could not be provided. Furthermore, according to Decision 2017/848/EU, the results of the assessment of criterion D7C2 (estimated extent of adverse effects by habitat type in each assessment area) are used for the assessment of criterion D6C5. However, in the absence of an operational indicator at the level of Descriptor 6 - Benthic Habitats, these results could not be taken into account in the assessment of D6C5.
In the absence of a threshold for the "Extent" parameter, the state of the habitat could not be provided. Furthermore, according to Decision 2017/848/EU, the results of the assessment of criterion D7C2 (estimated extent of adverse effects by habitat type in each assessment area) are used for the assessment of criterion D6C5. However, in the absence of an operational indicator at the level of Descriptor 6 - Benthic Habitats, these results could not be taken into account in the assessment of D6C5.
In the absence of a threshold for the "Extent" parameter, the state of the habitat could not be provided. Furthermore, according to Decision 2017/848/EU, the results of the assessment of criterion D7C2 (estimated extent of adverse effects by habitat type in each assessment area) are used for the assessment of criterion D6C5. However, in the absence of an operational indicator at the level of Descriptor 6 - Benthic Habitats, these results could not be taken into account in the assessment of D6C5.
In the absence of a threshold for the "Extent" parameter, the state of the habitat could not be provided. Furthermore, according to Decision 2017/848/EU, the results of the assessment of criterion D7C2 (estimated extent of adverse effects by habitat type in each assessment area) are used for the assessment of criterion D6C5. However, in the absence of an operational indicator at the level of Descriptor 6 - Benthic Habitats, these results could not be taken into account in the assessment of D6C5.
In the absence of a threshold for the "Extent" parameter, the state of the habitat could not be provided. Furthermore, according to Decision 2017/848/EU, the results of the assessment of criterion D7C2 (estimated extent of adverse effects by habitat type in each assessment area) are used for the assessment of criterion D6C5. However, in the absence of an operational indicator at the level of Descriptor 6 - Benthic Habitats, these results could not be taken into account in the assessment of D6C5.
In the absence of a threshold for the "Extent" parameter, the state of the habitat could not be provided. Furthermore, according to Decision 2017/848/EU, the results of the assessment of criterion D7C2 (estimated extent of adverse effects by habitat type in each assessment area) are used for the assessment of criterion D6C5. However, in the absence of an operational indicator at the level of Descriptor 6 - Benthic Habitats, these results could not be taken into account in the assessment of D6C5.
In the absence of a threshold for the "Extent" parameter, the state of the habitat could not be provided. Furthermore, according to Decision 2017/848/EU, the results of the assessment of criterion D7C2 (estimated extent of adverse effects by habitat type in each assessment area) are used for the assessment of criterion D6C5. However, in the absence of an operational indicator at the level of Descriptor 6 - Benthic Habitats, these results could not be taken into account in the assessment of D6C5.
In the absence of a threshold for the "Extent" parameter, the state of the habitat could not be provided. Furthermore, according to Decision 2017/848/EU, the results of the assessment of criterion D7C2 (estimated extent of adverse effects by habitat type in each assessment area) are used for the assessment of criterion D6C5. However, in the absence of an operational indicator at the level of Descriptor 6 - Benthic Habitats, these results could not be taken into account in the assessment of D6C5.
In the absence of a threshold for the "Extent" parameter, the state of the habitat could not be provided. Furthermore, according to Decision 2017/848/EU, the results of the assessment of criterion D7C2 (estimated extent of adverse effects by habitat type in each assessment area) are used for the assessment of criterion D6C5. However, in the absence of an operational indicator at the level of Descriptor 6 - Benthic Habitats, these results could not be taken into account in the assessment of D6C5.
In the absence of a threshold for the "Extent" parameter, the state of the habitat could not be provided. Furthermore, according to Decision 2017/848/EU, the results of the assessment of criterion D7C2 (estimated extent of adverse effects by habitat type in each assessment area) are used for the assessment of criterion D6C5. However, in the absence of an operational indicator at the level of Descriptor 6 - Benthic Habitats, these results could not be taken into account in the assessment of D6C5.
In the absence of a threshold for the "Extent" parameter, the state of the habitat could not be provided. Furthermore, according to Decision 2017/848/EU, the results of the assessment of criterion D7C2 (estimated extent of adverse effects by habitat type in each assessment area) are used for the assessment of criterion D6C5. However, in the absence of an operational indicator at the level of Descriptor 6 - Benthic Habitats, these results could not be taken into account in the assessment of D6C5.
Integration rule type parameter
Not relevant
Not relevant
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Integration rule description parameter
Integration rule type criteria
Not relevant
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Integration rule description criteria
GES extent threshold
GES extent achieved
GES extent unit
GES achieved
Not relevant
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Description overall status
The D7 assessment, based on data on anthropogenic activities, highlighted significant variations in pressure exposures:1/ The coastal zone is the most subject to exposure to the hydrographic pressures considered.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (58% of the northern subdivision of the Bay of Biscay marine sub-region). However, the exposure index remains mostly low, and for 90% of the major benthic habitat types, the area of habitat potentially subject to medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
The D7 assessment, based on data on anthropogenic activities, highlighted significant variations in pressure exposures:1/ The coastal zone is the most subject to exposure to the hydrographic pressures considered.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (58% of the northern subdivision of the Bay of Biscay marine sub-region). However, the exposure index remains mostly low, and for 90% of the major benthic habitat types, the area of habitat potentially subject to medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
The D7 assessment, based on data on anthropogenic activities, highlighted significant variations in pressure exposures:1/ The coastal zone is the most subject to exposure to the hydrographic pressures considered.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (58% of the northern subdivision of the Bay of Biscay marine sub-region). However, the exposure index remains mostly low, and for 90% of the major benthic habitat types, the area of habitat potentially subject to medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
The D7 assessment, based on data on anthropogenic activities, highlighted significant variations in pressure exposures:1/ The coastal zone is the most subject to exposure to the hydrographic pressures considered.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (58% of the northern subdivision of the Bay of Biscay marine sub-region). However, the exposure index remains mostly low, and for 90% of the major benthic habitat types, the area of habitat potentially subject to medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
The D7 assessment, based on data on anthropogenic activities, highlighted significant variations in pressure exposures:1/ The coastal zone is the most subject to exposure to the hydrographic pressures considered.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (58% of the northern subdivision of the Bay of Biscay marine sub-region). However, the exposure index remains mostly low, and for 90% of the major benthic habitat types, the area of habitat potentially subject to medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
The D7 assessment, based on data on anthropogenic activities, highlighted significant variations in pressure exposures:1/ The coastal zone is the most subject to exposure to the hydrographic pressures considered.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (58% of the northern subdivision of the Bay of Biscay marine sub-region). However, the exposure index remains mostly low, and for 90% of the major benthic habitat types, the area of habitat potentially subject to medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
The D7 assessment, based on data on anthropogenic activities, highlighted significant variations in pressure exposures:1/ The coastal zone is the most subject to exposure to the hydrographic pressures considered.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (58% of the northern subdivision of the Bay of Biscay marine sub-region). However, the exposure index remains mostly low, and for 90% of the major benthic habitat types, the area of habitat potentially subject to medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
The D7 assessment, based on data on anthropogenic activities, highlighted significant variations in pressure exposures:1/ The coastal zone is the most subject to exposure to the hydrographic pressures considered.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (58% of the northern subdivision of the Bay of Biscay marine sub-region). However, the exposure index remains mostly low, and for 90% of the major benthic habitat types, the area of habitat potentially subject to medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
The D7 assessment, based on data on anthropogenic activities, highlighted significant variations in pressure exposures:1/ The coastal zone is the most subject to exposure to the hydrographic pressures considered.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (58% of the northern subdivision of the Bay of Biscay marine sub-region). However, the exposure index remains mostly low, and for 90% of the major benthic habitat types, the area of habitat potentially subject to medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
The D7 assessment, based on data on anthropogenic activities, highlighted significant variations in pressure exposures:1/ The coastal zone is the most subject to exposure to the hydrographic pressures considered.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (58% of the northern subdivision of the Bay of Biscay marine sub-region). However, the exposure index remains mostly low, and for 90% of the major benthic habitat types, the area of habitat potentially subject to medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
The D7 assessment, based on data on anthropogenic activities, highlighted significant variations in pressure exposures:1/ The coastal zone is the most subject to exposure to the hydrographic pressures considered.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (58% of the northern subdivision of the Bay of Biscay marine sub-region). However, the exposure index remains mostly low, and for 90% of the major benthic habitat types, the area of habitat potentially subject to medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
The D7 assessment, based on data on anthropogenic activities, highlighted significant variations in pressure exposures:1/ The coastal zone is the most subject to exposure to the hydrographic pressures considered.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (58% of the northern subdivision of the Bay of Biscay marine sub-region). However, the exposure index remains mostly low, and for 90% of the major benthic habitat types, the area of habitat potentially subject to medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
The D7 assessment, based on data on anthropogenic activities, highlighted significant variations in pressure exposures:1/ The coastal zone is the most subject to exposure to the hydrographic pressures considered.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (58% of the northern subdivision of the Bay of Biscay marine sub-region). However, the exposure index remains mostly low, and for 90% of the major benthic habitat types, the area of habitat potentially subject to medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
The D7 assessment, based on data on anthropogenic activities, highlighted significant variations in pressure exposures:1/ The coastal zone is the most subject to exposure to the hydrographic pressures considered.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (58% of the northern subdivision of the Bay of Biscay marine sub-region). However, the exposure index remains mostly low, and for 90% of the major benthic habitat types, the area of habitat potentially subject to medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
The D7 assessment, based on data on anthropogenic activities, highlighted significant variations in pressure exposures:1/ The coastal zone is the most subject to exposure to the hydrographic pressures considered.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (58% of the northern subdivision of the Bay of Biscay marine sub-region). However, the exposure index remains mostly low, and for 90% of the major benthic habitat types, the area of habitat potentially subject to medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
The D7 assessment, based on data on anthropogenic activities, highlighted significant variations in pressure exposures:1/ The coastal zone is the most subject to exposure to the hydrographic pressures considered.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (58% of the northern subdivision of the Bay of Biscay marine sub-region). However, the exposure index remains mostly low, and for 90% of the major benthic habitat types, the area of habitat potentially subject to medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
The D7 assessment, based on data on anthropogenic activities, highlighted significant variations in pressure exposures:1/ The coastal zone is the most subject to exposure to the hydrographic pressures considered.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (58% of the northern subdivision of the Bay of Biscay marine sub-region). However, the exposure index remains mostly low, and for 90% of the major benthic habitat types, the area of habitat potentially subject to medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
The D7 assessment, based on data on anthropogenic activities, highlighted significant variations in pressure exposures:1/ The coastal zone is the most subject to exposure to the hydrographic pressures considered.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (58% of the northern subdivision of the Bay of Biscay marine sub-region). However, the exposure index remains mostly low, and for 90% of the major benthic habitat types, the area of habitat potentially subject to medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
The D7 assessment, based on data on anthropogenic activities, highlighted significant variations in pressure exposures:1/ The coastal zone is the most subject to exposure to the hydrographic pressures considered.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (58% of the northern subdivision of the Bay of Biscay marine sub-region). However, the exposure index remains mostly low, and for 90% of the major benthic habitat types, the area of habitat potentially subject to medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
The D7 assessment, based on data on anthropogenic activities, highlighted significant variations in pressure exposures:1/ The coastal zone is the most subject to exposure to the hydrographic pressures considered.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (58% of the northern subdivision of the Bay of Biscay marine sub-region). However, the exposure index remains mostly low, and for 90% of the major benthic habitat types, the area of habitat potentially subject to medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
Assessments period
2012-2018
2012-2018
2012-2018
2012-2018
2012-2018
2012-2018
2012-2018
2012-2018
2012-2018
2012-2018
2012-2018
2012-2018
2012-2018
2012-2018
2012-2018
2012-2018
2012-2018
2012-2018
2012-2018
2012-2018
Related pressures
Related targets

Nord SRM GdG Z200 (ABI-FR-MS-GDG-NORD-Z200)

GES component
D7
D7
D7
D7
D7
D7
D7
D7
D7
D7
D7
D7
D7
D7
D7
D7
D7
D7
D7
Feature
Hydrographical changes
Hydrographical changes
Hydrographical changes
Hydrographical changes
Hydrographical changes
Hydrographical changes
Hydrographical changes
Benthic broad habitats
Benthic broad habitats
Benthic broad habitats
Benthic broad habitats
Benthic broad habitats
Benthic broad habitats
Benthic broad habitats
Benthic broad habitats
Benthic broad habitats
Benthic broad habitats
Benthic broad habitats
Benthic broad habitats
Element
Changes in current regime
Changes in salinity regime
Changes in seabed substrate
Changes in thermal regime
Changes in tide regime
Changes in turbidity regime
Changes in waves regime
Circalittoral coarse sediment
Circalittoral mixed sediment
Circalittoral mud
Circalittoral rock and biogenic reef
Circalittoral sand
Infralittoral mixed sediment
Infralittoral rock and biogenic reef
Offshore circalittoral coarse sediment
Offshore circalittoral mixed sediment
Offshore circalittoral mud
Offshore circalittoral rock and biogenic reef
Offshore circalittoral sand
Element code
ExpPresCurrents
ExpPresSalinity
ExpPresSeabedNature
ExpPresTemperature
ExpPresTide
ExpPresTurbidity
ExpPresWaves
HabBenCircalitCoarSed
HabBenCircalitMxdSed
HabBenCircalitMud
HabBenCircalitRock
HabBenCircalitSand
HabBenInfralitMxdSed
HabBenInfralitRock
HabBenOffshCoarSed
HabBenOffshMxdSed
HabBenOffshMud
HabBenOffshRock
HabBenOffshSand
Element code source
Link to other vocabulary or code lists that may be relevant
Link to other vocabulary or code lists that may be relevant
Link to other vocabulary or code lists that may be relevant
Link to other vocabulary or code lists that may be relevant
Link to other vocabulary or code lists that may be relevant
Link to other vocabulary or code lists that may be relevant
Link to other vocabulary or code lists that may be relevant
Habitats (D1-D6) http://dd.eionet.europa.eu/vocabulary/msfd/broadHabitatTypes/view
Habitats (D1-D6) http://dd.eionet.europa.eu/vocabulary/msfd/broadHabitatTypes/view
Habitats (D1-D6) http://dd.eionet.europa.eu/vocabulary/msfd/broadHabitatTypes/view
Habitats (D1-D6) http://dd.eionet.europa.eu/vocabulary/msfd/broadHabitatTypes/view
Habitats (D1-D6) http://dd.eionet.europa.eu/vocabulary/msfd/broadHabitatTypes/view
Habitats (D1-D6) http://dd.eionet.europa.eu/vocabulary/msfd/broadHabitatTypes/view
Habitats (D1-D6) http://dd.eionet.europa.eu/vocabulary/msfd/broadHabitatTypes/view
Habitats (D1-D6) http://dd.eionet.europa.eu/vocabulary/msfd/broadHabitatTypes/view
Habitats (D1-D6) http://dd.eionet.europa.eu/vocabulary/msfd/broadHabitatTypes/view
Habitats (D1-D6) http://dd.eionet.europa.eu/vocabulary/msfd/broadHabitatTypes/view
Habitats (D1-D6) http://dd.eionet.europa.eu/vocabulary/msfd/broadHabitatTypes/view
Habitats (D1-D6) http://dd.eionet.europa.eu/vocabulary/msfd/broadHabitatTypes/view
Element 2
Element 2 code
Element 2 code source
Element source
National
National
National
National
National
National
National
EU
EU
EU
EU
EU
EU
EU
EU
EU
EU
EU
EU
Criterion
D7C1
D7C1
D7C1
D7C1
D7C1
D7C1
D7C1
D7C2
D7C2
D7C2
D7C2
D7C2
D7C2
D7C2
D7C2
D7C2
D7C2
D7C2
D7C2
Parameter
Extent
Extent
Extent
Extent
Extent
Extent
Extent
Extent
Extent
Extent
Extent
Extent
Extent
Extent
Extent
Extent
Extent
Extent
Extent
Parameter other
Threshold value upper
Threshold value lower
Threshold qualitative
Not available yet
Not available yet
Not available yet
Not available yet
Not available yet
Not available yet
Not available yet
Not available yet
Not available yet
Not available yet
Not available yet
Not available yet
Not available yet
Not available yet
Not available yet
Not available yet
Not available yet
Not available yet
Not available yet
Threshold value source
Threshold value source other
Value achieved upper
Value achieved lower
Value unit
Value unit other
Proportion threshold value
Proportion value achieved
10.0
38461.0
10.0
10.0
38461.0
10.0
2061.0
1491.0
254.0
1157.0
910.0
3.4
3.4
2686.0
2960.0
15190.0
1171.0
10560.0
Proportion threshold value unit
extent in km2 of pressure
extent in km2 of pressure
extent in km2 of pressure
extent in km2 of pressure
extent in km2 of pressure
extent in km2 of pressure
extent in km2 of pressure
extent in km2 of habitat adversely affected
extent in km2 of habitat adversely affected
extent in km2 of habitat adversely affected
extent in km2 of habitat adversely affected
extent in km2 of habitat adversely affected
extent in km2 of habitat adversely affected
extent in km2 of habitat adversely affected
extent in km2 of habitat adversely affected
extent in km2 of habitat adversely affected
extent in km2 of habitat adversely affected
extent in km2 of habitat adversely affected
extent in km2 of habitat adversely affected
Trend
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Parameter achieved
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Description parameter
The metric considered for this parameter is the area of exposure for each pressure considered (overall or as a function of the level of the exposure index). The areas potentially affected by a change in the current regime correspond to a total area of 10 km2 , based on the four levels of exposure index: No exposure: 38450 km² Low exposure index: 3 km² Medium exposure index: 7 km² High exposure index: 0 km² Note that no threshold is currently available to assess whether or not the parameter has been reached.
The metric considered for this parameter is the area of exposure for each pressure considered (overall or as a function of the level of the exposure index). The areas potentially affected by a change in the salinity regime correspond to a total area of 0 km2 . The areas of exposure according to the four levels of the exposure index are No exposure: 38461 km² Low exposure index: 0 km² Medium exposure index: 0 km² High exposure index: 0 km² Note that no threshold is currently available to assess whether or not the parameter has been reached.
The metric considered for this parameter is the area of exposure for each pressure considered (overall or as a function of the level of the exposure index). The areas potentially affected by a change in the background nature correspond to a total area of 38461 km2 . The areas of exposure according to the four levels of exposure index are: No Exposure: 0 km² Low Exposure Index: 38457 km² Medium Exposure Index: 3 km² High Exposure Index: 0 km² Note that no threshold is currently available to assess whether or not the parameter has been reached.
The metric considered for this parameter is the area of exposure for each pressure considered (overall or as a function of the level of the exposure index). The areas potentially affected by a change in the thermal regime correspond to a total surface area of <10 km2 . The areas of exposure according to the four levels of the exposure index are No exposure: 38461 km².Low exposure index: <10 km².Medium exposure index: 0 km².High exposure index: 0 km².Note that no threshold is currently available to assess whether or not the parameter has been reached.
The metric considered for this parameter is the area of exposure for each pressure considered (overall or as a function of the level of the exposure index). The areas potentially affected by a change in the tidal regime correspond to a total area of 10 km2 , based on the four levels of exposure index: No exposure: 38450 km².Low exposure index: 0km².Medium exposure index: 10 km².High exposure index: 0 km².Note that no threshold is currently available to assess whether or not the parameter has been reached.
The metric considered for this parameter is the area of exposure for each pressure considered (overall or as a function of the level of the exposure index). The areas potentially affected by a change in the turbidity regime correspond to a total area of 38461 km2 . The areas of exposure according to the four levels of exposure index are: No exposure: 0 km².Low exposure index: 38392 km².Medium exposure index: 69 km².High exposure index: 0 km².It should be noted that no threshold is currently available to assess whether or not the parameter has been reached.
The metric considered for this parameter is the area of exposure for each pressure considered (overall or as a function of the level of the exposure index). The areas potentially affected by a change in the wave regime correspond to a total area of 10 km2 . The areas of exposure according to the four levels of exposure index are: No Exposure: 38450 km².Low Exposure Index: 10 km².Medium Exposure Index: 0 km².High Exposure Index: 0 km².Note that no threshold is currently available to assess whether or not the parameter is reached.
The metric considered for this parameter is the area of habitat potentially at risk (overall or based on the level of risk). The spatial extent of potential habitat modification related to permanent changes in hydrographic conditions in this MRU is 2061 km2 (i.e. 100% of the assessed habitat). Furthermore, the indicator makes it possible to assess the intensity of the risk of modification: negligible or nil risk of modification: 0 km², low risk of modification: 137 km², medium risk of modification: 1923 km², high risk of modification: 0 km², it should be noted that no threshold is currently available to assess whether or not the parameter has been reached.
The metric considered for this parameter is the area of habitat potentially at risk (overall or based on the level of risk). The spatial extent of potential habitat modification related to permanent changes in hydrographic conditions in this MRU is 1491 km2 (i.e. 100% of the habitat assessed). Furthermore, the indicator makes it possible to assess the intensity of the risk of modification: negligible or nil risk of modification: 0 km², low risk of modification: 196 km², medium risk of modification: 1295 km², high risk of modification: 0 km², it should be noted that no threshold is currently available to assess whether or not the parameter has been reached.
The metric considered for this parameter is the area of habitat potentially at risk (overall or as a function of the level of risk). The spatial extent of potential habitat modification related to permanent changes in hydrographic conditions in this MRU is 254 km2 (i.e. 100% of the habitat assessed). Furthermore, the indicator makes it possible to assess the intensity of the risk of modification: negligible or no risk of modification: 0 km², low risk of modification: 10 km², medium risk of modification: 244 km², high risk of modification: 0 km², it should be noted that no threshold is currently available to assess whether or not the parameter has been reached.
The metric considered for this parameter is the area of habitat potentially at risk (overall or based on the level of risk). The spatial extent of potential habitat modification related to permanent changes in hydrographic conditions in this MRU is 1157 km2 (i.e. 100% of the assessed habitat). Furthermore, the indicator makes it possible to assess the intensity of the risk of modification: negligible or no risk of modification: 0 km², low risk of modification: 343 km², medium risk of modification: 814 km², high risk of modification: 0 km², it should be noted that no threshold is currently available to assess whether or not the parameter has been reached.
The metric considered for this parameter is the area of habitat potentially at risk (overall or as a function of the level of risk). The spatial extent of potential habitat modification related to permanent changes in hydrographic conditions in this MRU is 910 km2 (i.e. 100% of the habitat assessed). Furthermore, the indicator makes it possible to assess the intensity of the risk of modification: negligible or nil risk of modification: 0 km², low risk of modification: 70 km², medium risk of modification: 841 km², high risk of modification: 0 km², it should be noted that no threshold is currently available to assess whether or not the parameter has been reached.
The metric considered for this parameter is the area of habitat potentially at risk (overall or based on the level of risk). The spatial extent of potential habitat modification related to permanent changes in hydrographic conditions in this MRU is 3.4 km2 (i.e. 100% of the habitat assessed). Furthermore, the indicator makes it possible to assess the intensity of the risk of modification: negligible or nil risk of modification: 0 km², low risk of modification: 0 km², medium risk of modification: 0 km², high risk of modification: 3.4 km², although no threshold is currently available to assess whether or not the parameter has been reached.
The metric considered for this parameter is the area of habitat potentially at risk (overall or based on the level of risk). The spatial extent of potential habitat alteration related to permanent changes in hydrographic conditions in this MRU is 3.4 km2 (i.e., 100% of the assessed habitat). In addition, the indicator makes it possible to assess the intensity of the risk of modification: negligible or no risk of modification: 0km², low risk of modification: 0 km², medium risk of modification: 3.4 km², high risk of modification: 0 km², it should be noted that no threshold is currently available to assess whether or not the parameter has been reached.
The metric considered for this parameter is the area of habitat potentially at risk (overall or as a function of the level of risk). The spatial extent of potential habitat modification related to permanent changes in hydrographic conditions in this MRU is 2686 km2 (i.e., 100% of the habitat assessed). Furthermore, the indicator makes it possible to assess the intensity of the risk of modification: negligible or nil risk of modification: 0 km², low risk of modification: 567 km², medium risk of modification: 2119 km², high risk of modification: 0 km², it should be noted that no threshold is currently available to assess whether or not the parameter has been reached.
The metric considered for this parameter is the area of habitat potentially at risk (overall or as a function of the level of risk). The spatial extent of potential habitat modification related to permanent changes in hydrographic conditions in this MRU is 2960 km2 (i.e. 100% of the habitat assessed). Furthermore, the indicator makes it possible to assess the intensity of the risk of modification: negligible or nil risk of modification: 0 km², low risk of modification: 292 km², medium risk of modification: 2668 km², high risk of modification: 0 km², it should be noted that no threshold is currently available to assess whether or not the parameter has been reached.
The metric considered for this parameter is the area of habitat potentially at risk (overall or as a function of the level of risk). The spatial extent of potential habitat modification related to permanent changes in hydrographic conditions in this MRU is 15190 km2 (i.e. 100% of the habitat assessed). Furthermore, the indicator makes it possible to assess the intensity of the risk of modification: negligible or nil risk of modification: 0 km², low risk of modification: 2583 km², medium risk of modification: 12607 km², high risk of modification: 0 km², it should be noted that no threshold is currently available to assess whether or not the parameter has been reached.
The metric considered for this parameter is the area of habitat potentially at risk (overall or as a function of the level of risk). The spatial extent of potential habitat modification related to permanent changes in hydrographic conditions in this MRU is 1171 km2 (i.e. 100% of the habitat assessed). Furthermore, the indicator makes it possible to assess the intensity of the risk of modification: negligible or no risk of modification: 0 km², low risk of modification: 773 km², medium risk of modification: 399 km², high risk of modification: 0 km², it should be noted that no threshold is currently available to assess whether or not the parameter has been reached.
The metric considered for this parameter is the area of habitat potentially at risk (overall or as a function of the level of risk). The spatial extent of potential habitat modification related to permanent changes in hydrographic conditions in this MRU is 10560 km2 (i.e. 100% of the assessed habitat). Furthermore, the indicator makes it possible to assess the intensity of the risk of modification: negligible or no risk of modification: 0 km², low risk of modification: 1339 km², medium risk of modification: 9221 km², high risk of modification: 0 km², it should be noted that no threshold is currently available to assess whether or not the parameter has been reached.
Related indicator
Criteria status
Contributes to assessment of another criterion/ele
Contributes to assessment of another criterion/ele
Contributes to assessment of another criterion/ele
Contributes to assessment of another criterion/ele
Contributes to assessment of another criterion/ele
Contributes to assessment of another criterion/ele
Contributes to assessment of another criterion/ele
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Description criteria
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017) no threshold is to be specified for D7C1: the status of the D7C1 criterion is therefore not reported. However, the assessment of the D7C1 criterion has provided a first estimate of the exposure indices for spatial areas potentially affected by a change in the current, tidal, wave, bottom nature, turbidity, salinity and thermal regime. Indeed, the results show that the pressures linked to a change in the current, tidal and wave regime are relatively low (< 1% of the northern subdivision of the Bay of Biscay marine sub-region) and fairly localised since they mainly affect coastal waters. They represent less than 1% of the area of this MRU. It should also be noted that the exposure indices calculated for these pressures are mostly low. Pressures linked to a change in the nature of the bottom and the turbidity regime potentially affect a very large area (100% of the MRU). The exposure indices calculated for these pressures are mostly low (>99% of the area of the MRU is subject to a low exposure index). Finally, pressures related to a change in the thermal and salinity regime affect less than 1% of the MRU.
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017) no threshold is to be specified for D7C1: the status of the D7C1 criterion is therefore not reported. However, the assessment of the D7C1 criterion has provided a first estimate of the exposure indices for spatial areas potentially affected by a change in the current, tidal, wave, bottom nature, turbidity, salinity and thermal regime. Indeed, the results show that the pressures linked to a change in the current, tidal and wave regime are relatively low (< 1% of the northern subdivision of the Bay of Biscay marine sub-region) and fairly localised since they mainly affect coastal waters. They represent less than 1% of the area of this MRU. It should also be noted that the exposure indices calculated for these pressures are mostly low. Pressures linked to a change in the nature of the bottom and the turbidity regime potentially affect a very large area (100% of the MRU). The exposure indices calculated for these pressures are mostly low (>99% of the area of the MRU is subject to a low exposure index). Finally, pressures related to a change in the thermal and salinity regime affect less than 1% of the MRU.
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017) no threshold is to be specified for D7C1: the status of the D7C1 criterion is therefore not reported. However, the assessment of the D7C1 criterion has provided a first estimate of the exposure indices for spatial areas potentially affected by a change in the current, tidal, wave, bottom nature, turbidity, salinity and thermal regime. Indeed, the results show that the pressures linked to a change in the current, tidal and wave regime are relatively low (< 1% of the northern subdivision of the Bay of Biscay marine sub-region) and fairly localised since they mainly affect coastal waters. They represent less than 1% of the area of this MRU. It should also be noted that the exposure indices calculated for these pressures are mostly low. Pressures linked to a change in the nature of the bottom and the turbidity regime potentially affect a very large area (100% of the MRU). The exposure indices calculated for these pressures are mostly low (>99% of the area of the MRU is subject to a low exposure index). Finally, pressures related to a change in the thermal and salinity regime affect less than 1% of the MRU.
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017) no threshold is to be specified for D7C1: the status of the D7C1 criterion is therefore not reported. However, the assessment of the D7C1 criterion has provided a first estimate of the exposure indices for spatial areas potentially affected by a change in the current, tidal, wave, bottom nature, turbidity, salinity and thermal regime. Indeed, the results show that the pressures linked to a change in the current, tidal and wave regime are relatively low (< 1% of the northern subdivision of the Bay of Biscay marine sub-region) and fairly localised since they mainly affect coastal waters. They represent less than 1% of the area of this MRU. It should also be noted that the exposure indices calculated for these pressures are mostly low. Pressures linked to a change in the nature of the bottom and the turbidity regime potentially affect a very large area (100% of the MRU). The exposure indices calculated for these pressures are mostly low (>99% of the area of the MRU is subject to a low exposure index). Finally, pressures related to a change in the thermal and salinity regime affect less than 1% of the MRU.
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017) no threshold is to be specified for D7C1: the status of the D7C1 criterion is therefore not reported. However, the assessment of the D7C1 criterion has provided a first estimate of the exposure indices for spatial areas potentially affected by a change in the current, tidal, wave, bottom nature, turbidity, salinity and thermal regime. Indeed, the results show that the pressures linked to a change in the current, tidal and wave regime are relatively low (< 1% of the northern subdivision of the Bay of Biscay marine sub-region) and fairly localised since they mainly affect coastal waters. They represent less than 1% of the area of this MRU. It should also be noted that the exposure indices calculated for these pressures are mostly low. Pressures linked to a change in the nature of the bottom and the turbidity regime potentially affect a very large area (100% of the MRU). The exposure indices calculated for these pressures are mostly low (>99% of the area of the MRU is subject to a low exposure index). Finally, pressures related to a change in the thermal and salinity regime affect less than 1% of the MRU.
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017) no threshold is to be specified for D7C1: the status of the D7C1 criterion is therefore not reported. However, the assessment of the D7C1 criterion has provided a first estimate of the exposure indices for spatial areas potentially affected by a change in the current, tidal, wave, bottom nature, turbidity, salinity and thermal regime. Indeed, the results show that the pressures linked to a change in the current, tidal and wave regime are relatively low (< 1% of the northern subdivision of the Bay of Biscay marine sub-region) and fairly localised since they mainly affect coastal waters. They represent less than 1% of the area of this MRU. It should also be noted that the exposure indices calculated for these pressures are mostly low. Pressures linked to a change in the nature of the bottom and the turbidity regime potentially affect a very large area (100% of the MRU). The exposure indices calculated for these pressures are mostly low (>99% of the area of the MRU is subject to a low exposure index). Finally, pressures related to a change in the thermal and salinity regime affect less than 1% of the MRU.
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017) no threshold is to be specified for D7C1: the status of the D7C1 criterion is therefore not reported. However, the assessment of the D7C1 criterion has provided a first estimate of the exposure indices for spatial areas potentially affected by a change in the current, tidal, wave, bottom nature, turbidity, salinity and thermal regime. Indeed, the results show that the pressures linked to a change in the current, tidal and wave regime are relatively low (< 1% of the northern subdivision of the Bay of Biscay marine sub-region) and fairly localised since they mainly affect coastal waters. They represent less than 1% of the area of this MRU. It should also be noted that the exposure indices calculated for these pressures are mostly low. Pressures linked to a change in the nature of the bottom and the turbidity regime potentially affect a very large area (100% of the MRU). The exposure indices calculated for these pressures are mostly low (>99% of the area of the MRU is subject to a low exposure index). Finally, pressures related to a change in the thermal and salinity regime affect less than 1% of the MRU.
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017), the D7C2 assessment must be carried out for each habitat type that is affected by changing hydrographic conditions and the D7C2 results are not integrated. On the other hand, no threshold has been defined so far for the parameter "Extent" and therefore the status of D7C2 is not reported, but the assessment of D7C2 has provided a first estimate of the spatial extent of benthic habitats potentially subject to cumulative risks of alteration, based on the indices of exposure to hydrographic pressures generated by human activities. Thus, 93% of the area of "Coastal circalittoral coarse sediment" habitat appears to be at medium risk.
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017), the D7C2 assessment must be carried out for each habitat type that is affected by changing hydrographic conditions and the D7C2 results are not integrated. On the other hand, no threshold has been defined so far for the parameter "Extent" and therefore the status of D7C2 is not reported, but the assessment of D7C2 has provided a first estimate of the spatial extent of benthic habitats potentially subject to cumulative risks of alteration, based on the indices of exposure to hydrographic pressures generated by human activities. Thus, 87% of the surface area of the "Coastal circalittoral mixed sediment" habitat appears to be subject to a medium risk.
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017), the D7C2 assessment must be carried out for each habitat type that is affected by changing hydrographic conditions and the D7C2 results are not integrated. On the other hand, no threshold has been defined so far for the parameter "Extent" and therefore the status of D7C2 is not reported, but the assessment of D7C2 has provided a first estimate of the spatial extent of benthic habitats potentially subject to cumulative risks of alteration, based on the indices of exposure to hydrographic pressures generated by human activities. Thus, 96% of the surface area of the "Coastal circalittoral mud flats" habitat appears to be at medium risk.
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017), the D7C2 assessment must be carried out for each habitat type that is affected by changing hydrographic conditions and the D7C2 results are not integrated. On the other hand, no threshold has been defined so far for the parameter "Extent" and therefore the status of D7C2 is not reported, but the assessment of D7C2 has provided a first estimate of the spatial extent of benthic habitats potentially subject to cumulative risks of alteration, based on the indices of exposure to hydrographic pressures generated by human activities. Thus, 70% of the surface area of the "Coastal circalittoral biogenic rocks and reefs" habitat appears to be at medium risk.
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017), the D7C2 assessment must be carried out for each habitat type that is affected by changing hydrographic conditions and the D7C2 results are not integrated. On the other hand, no threshold has been defined so far for the parameter "Extent" and therefore the status of D7C2 is not reported, but the assessment of D7C2 has provided a first estimate of the spatial extent of benthic habitats potentially subject to cumulative risks of alteration, based on the indices of exposure to hydrographic pressures generated by human activities. Ninety-two percent of the area of "Coastal circalittoral sands" habitat appears to be at medium risk.
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017), the D7C2 assessment must be carried out for each habitat type that is affected by changing hydrographic conditions and the D7C2 results are not integrated. On the other hand, no threshold has been defined so far for the parameter "Extent" and therefore the status of D7C2 is not reported, but the assessment of D7C2 has provided a first estimate of the spatial extent of benthic habitats potentially subject to cumulative risks of alteration, based on the indices of exposure to hydrographic pressures generated by human activities. Thus, the "Heterogeneous subtidal sediment" habitat presents the largest area affected with the totality subject to a high risk, i.e. 100% of the MRU.
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017), the D7C2 assessment must be carried out for each habitat type that is affected by changing hydrographic conditions and the D7C2 results are not integrated. On the other hand, no threshold has been defined so far for the parameter "Extent" and therefore the status of D7C2 is not reported, but the assessment of D7C2 has provided a first estimate of the spatial extent of benthic habitats potentially subject to cumulative risks of alteration, based on the indices of exposure to hydrographic pressures generated by human activities. Thus, the " infralittoral biogenic rocks and reefs " habitat appears to be entirely at medium risk (100% of the total habitat area).
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017), the D7C2 assessment must be carried out for each habitat type that is affected by changing hydrographic conditions and the D7C2 results are not integrated. On the other hand, no threshold has been defined so far for the parameter "Extent" and therefore the status of D7C2 is not reported, but the assessment of D7C2 has provided a first estimate of the spatial extent of benthic habitats potentially subject to cumulative risks of alteration, based on the indices of exposure to hydrographic pressures generated by human activities. For example, 79% of the area of offshore circalittoral coarse sediment habitat appears to be at medium risk.
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017), the D7C2 assessment must be carried out for each habitat type that is affected by changing hydrographic conditions and the D7C2 results are not integrated. On the other hand, no threshold has been defined so far for the parameter "Extent" and therefore the status of D7C2 is not reported, but the assessment of D7C2 has provided a first estimate of the spatial extent of benthic habitats potentially subject to cumulative risks of alteration, based on the indices of exposure to hydrographic pressures generated by human activities. Thus, 90% of the area of "mixed offshore circalittoral sediment" habitat appears to be at medium risk.
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017), the D7C2 assessment must be carried out for each habitat type that is affected by changing hydrographic conditions and the D7C2 results are not integrated. On the other hand, no threshold has been defined so far for the parameter "Extent" and therefore the status of D7C2 is not reported, but the assessment of D7C2 has provided a first estimate of the spatial extent of benthic habitats potentially subject to cumulative risks of alteration, based on the indices of exposure to hydrographic pressures generated by human activities. Thus, 83% of the area of "offshore circalittoral mud flats" habitat appears to be at medium risk.
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017), the D7C2 assessment must be carried out for each habitat type that is affected by changing hydrographic conditions and the D7C2 results are not integrated. On the other hand, no threshold has been defined so far for the parameter "Extent" and therefore the status of D7C2 is not reported, but the assessment of D7C2 has provided a first estimate of the spatial extent of benthic habitats potentially subject to cumulative risks of alteration, based on the indices of exposure to hydrographic pressures generated by human activities. Thus, 34% of the area of "offshore circalittoral biogenic rocks and reefs" habitat appears to be at medium risk and 66% at low risk.
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017), the D7C2 assessment must be carried out for each habitat type that is affected by changing hydrographic conditions and the D7C2 results are not integrated. On the other hand, no threshold has been defined so far for the parameter "Extent" and therefore the status of D7C2 is not reported, but the assessment of D7C2 has provided a first estimate of the spatial extent of benthic habitats potentially subject to cumulative risks of alteration, based on the indices of exposure to hydrographic pressures generated by human activities. Thus, 87% of the area of offshore circalittoral sands habitat appears to be at medium risk.
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Description element
The assessment of criterion D7C1 contributes to the assessment of criterion D7C2. Thus, the accumulation of quantified pressures (i.e., exposure indices) under D7C1 is incorporated into the calculation of the risk of modification of each habitat for the D7C2 assessment.
The assessment of criterion D7C1 contributes to the assessment of criterion D7C2. Thus, the accumulation of quantified pressures (i.e., exposure indices) under D7C1 is incorporated into the calculation of the risk of modification of each habitat for the D7C2 assessment.
The assessment of criterion D7C1 contributes to the assessment of criterion D7C2. Thus, the accumulation of quantified pressures (i.e., exposure indices) under D7C1 is incorporated into the calculation of the risk of modification of each habitat for the D7C2 assessment.
The assessment of criterion D7C1 contributes to the assessment of criterion D7C2. Thus, the accumulation of quantified pressures (i.e., exposure indices) under D7C1 is incorporated into the calculation of the risk of modification of each habitat for the D7C2 assessment.
The assessment of criterion D7C1 contributes to the assessment of criterion D7C2. Thus, the accumulation of quantified pressures (i.e., exposure indices) under D7C1 is incorporated into the calculation of the risk of modification of each habitat for the D7C2 assessment.
The assessment of criterion D7C1 contributes to the assessment of criterion D7C2. Thus, the accumulation of quantified pressures (i.e., exposure indices) under D7C1 is incorporated into the calculation of the risk of modification of each habitat for the D7C2 assessment.
The assessment of criterion D7C1 contributes to the assessment of criterion D7C2. Thus, the accumulation of quantified pressures (i.e., exposure indices) under D7C1 is incorporated into the calculation of the risk of modification of each habitat for the D7C2 assessment.
In the absence of a threshold for the "Extent" parameter, the state of the habitat could not be provided. Furthermore, according to Decision 2017/848/EU, the results of the assessment of criterion D7C2 (estimated extent of adverse effects by habitat type in each assessment area) are used for the assessment of criterion D6C5. However, in the absence of an operational indicator at the level of Descriptor 6 - Benthic Habitats, these results could not be taken into account in the assessment of D6C5.
In the absence of a threshold for the "Extent" parameter, the state of the habitat could not be provided. Furthermore, according to Decision 2017/848/EU, the results of the assessment of criterion D7C2 (estimated extent of adverse effects by habitat type in each assessment area) are used for the assessment of criterion D6C5. However, in the absence of an operational indicator at the level of Descriptor 6 - Benthic Habitats, these results could not be taken into account in the assessment of D6C5.
In the absence of a threshold for the "Extent" parameter, the state of the habitat could not be provided. Furthermore, according to Decision 2017/848/EU, the results of the assessment of criterion D7C2 (estimated extent of adverse effects by habitat type in each assessment area) are used for the assessment of criterion D6C5. However, in the absence of an operational indicator at the level of Descriptor 6 - Benthic Habitats, these results could not be taken into account in the assessment of D6C5.
In the absence of a threshold for the "Extent" parameter, the state of the habitat could not be provided. Furthermore, according to Decision 2017/848/EU, the results of the assessment of criterion D7C2 (estimated extent of adverse effects by habitat type in each assessment area) are used for the assessment of criterion D6C5. However, in the absence of an operational indicator at the level of Descriptor 6 - Benthic Habitats, these results could not be taken into account in the assessment of D6C5.
In the absence of a threshold for the "Extent" parameter, the state of the habitat could not be provided. Furthermore, according to Decision 2017/848/EU, the results of the assessment of criterion D7C2 (estimated extent of adverse effects by habitat type in each assessment area) are used for the assessment of criterion D6C5. However, in the absence of an operational indicator at the level of Descriptor 6 - Benthic Habitats, these results could not be taken into account in the assessment of D6C5.
In the absence of a threshold for the "Extent" parameter, the state of the habitat could not be provided. Furthermore, according to Decision 2017/848/EU, the results of the assessment of criterion D7C2 (estimated extent of adverse effects by habitat type in each assessment area) are used for the assessment of criterion D6C5. However, in the absence of an operational indicator at the level of Descriptor 6 - Benthic Habitats, these results could not be taken into account in the assessment of D6C5.
In the absence of a threshold for the "Extent" parameter, the state of the habitat could not be provided. Furthermore, according to Decision 2017/848/EU, the results of the assessment of criterion D7C2 (estimated extent of adverse effects by habitat type in each assessment area) are used for the assessment of criterion D6C5. However, in the absence of an operational indicator at the level of Descriptor 6 - Benthic Habitats, these results could not be taken into account in the assessment of D6C5.
In the absence of a threshold for the "Extent" parameter, the state of the habitat could not be provided. Furthermore, according to Decision 2017/848/EU, the results of the assessment of criterion D7C2 (estimated extent of adverse effects by habitat type in each assessment area) are used for the assessment of criterion D6C5. However, in the absence of an operational indicator at the level of Descriptor 6 - Benthic Habitats, these results could not be taken into account in the assessment of D6C5.
In the absence of a threshold for the "Extent" parameter, the state of the habitat could not be provided. Furthermore, according to Decision 2017/848/EU, the results of the assessment of criterion D7C2 (estimated extent of adverse effects by habitat type in each assessment area) are used for the assessment of criterion D6C5. However, in the absence of an operational indicator at the level of Descriptor 6 - Benthic Habitats, these results could not be taken into account in the assessment of D6C5.
In the absence of a threshold for the "Extent" parameter, the state of the habitat could not be provided. Furthermore, according to Decision 2017/848/EU, the results of the assessment of criterion D7C2 (estimated extent of adverse effects by habitat type in each assessment area) are used for the assessment of criterion D6C5. However, in the absence of an operational indicator at the level of Descriptor 6 - Benthic Habitats, these results could not be taken into account in the assessment of D6C5.
In the absence of a threshold for the "Extent" parameter, the state of the habitat could not be provided. Furthermore, according to Decision 2017/848/EU, the results of the assessment of criterion D7C2 (estimated extent of adverse effects by habitat type in each assessment area) are used for the assessment of criterion D6C5. However, in the absence of an operational indicator at the level of Descriptor 6 - Benthic Habitats, these results could not be taken into account in the assessment of D6C5.
In the absence of a threshold for the "Extent" parameter, the state of the habitat could not be provided. Furthermore, according to Decision 2017/848/EU, the results of the assessment of criterion D7C2 (estimated extent of adverse effects by habitat type in each assessment area) are used for the assessment of criterion D6C5. However, in the absence of an operational indicator at the level of Descriptor 6 - Benthic Habitats, these results could not be taken into account in the assessment of D6C5.
Integration rule type parameter
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Integration rule description parameter
Integration rule type criteria
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Integration rule description criteria
GES extent threshold
GES extent achieved
GES extent unit
GES achieved
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Description overall status
The D7 assessment, based on data on anthropogenic activities, highlighted significant variations in exposure to pressures:1/ The Z200 zone is less subject than the coastal zone (MEC DCE) to exposure to the hydrographic pressures under consideration.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (58% of the northern subdivision of the Bay of Biscay marine sub-region). However, the exposure index remains mostly low, and for 90% of the major benthic habitat types, the area of habitat potentially subject to medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
The D7 assessment, based on data on anthropogenic activities, highlighted significant variations in exposure to pressures:1/ The Z200 zone is less subject than the coastal zone (MEC DCE) to exposure to the hydrographic pressures under consideration.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (58% of the northern subdivision of the Bay of Biscay marine sub-region). However, the exposure index remains mostly low, and for 90% of the major benthic habitat types, the area of habitat potentially subject to medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
The D7 assessment, based on data on anthropogenic activities, highlighted significant variations in exposure to pressures:1/ The Z200 zone is less subject than the coastal zone (MEC DCE) to exposure to the hydrographic pressures under consideration.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (58% of the northern subdivision of the Bay of Biscay marine sub-region). However, the exposure index remains mostly low, and for 90% of the major benthic habitat types, the area of habitat potentially subject to medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
The D7 assessment, based on data on anthropogenic activities, highlighted significant variations in exposure to pressures:1/ The Z200 zone is less subject than the coastal zone (MEC DCE) to exposure to the hydrographic pressures under consideration.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (58% of the northern subdivision of the Bay of Biscay marine sub-region). However, the exposure index remains mostly low, and for 90% of the major benthic habitat types, the area of habitat potentially subject to medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
The D7 assessment, based on data on anthropogenic activities, highlighted significant variations in exposure to pressures:1/ The Z200 zone is less subject than the coastal zone (MEC DCE) to exposure to the hydrographic pressures under consideration.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (58% of the northern subdivision of the Bay of Biscay marine sub-region). However, the exposure index remains mostly low, and for 90% of the major benthic habitat types, the area of habitat potentially subject to medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
The D7 assessment, based on data on anthropogenic activities, highlighted significant variations in exposure to pressures:1/ The Z200 zone is less subject than the coastal zone (MEC DCE) to exposure to the hydrographic pressures under consideration.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (58% of the northern subdivision of the Bay of Biscay marine sub-region). However, the exposure index remains mostly low, and for 90% of the major benthic habitat types, the area of habitat potentially subject to medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
The D7 assessment, based on data on anthropogenic activities, highlighted significant variations in exposure to pressures:1/ The Z200 zone is less subject than the coastal zone (MEC DCE) to exposure to the hydrographic pressures under consideration.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (58% of the northern subdivision of the Bay of Biscay marine sub-region). However, the exposure index remains mostly low, and for 90% of the major benthic habitat types, the area of habitat potentially subject to medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
The D7 assessment, based on data on anthropogenic activities, highlighted significant variations in exposure to pressures:1/ The Z200 zone is less subject than the coastal zone (MEC DCE) to exposure to the hydrographic pressures under consideration.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (58% of the northern subdivision of the Bay of Biscay marine sub-region). However, the exposure index remains mostly low, and for 90% of the major benthic habitat types, the area of habitat potentially subject to medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
The D7 assessment, based on data on anthropogenic activities, highlighted significant variations in exposure to pressures:1/ The Z200 zone is less subject than the coastal zone (MEC DCE) to exposure to the hydrographic pressures under consideration.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (58% of the northern subdivision of the Bay of Biscay marine sub-region). However, the exposure index remains mostly low, and for 90% of the major benthic habitat types, the area of habitat potentially subject to medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
The D7 assessment, based on data on anthropogenic activities, highlighted significant variations in exposure to pressures:1/ The Z200 zone is less subject than the coastal zone (MEC DCE) to exposure to the hydrographic pressures under consideration.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (58% of the northern subdivision of the Bay of Biscay marine sub-region). However, the exposure index remains mostly low, and for 90% of the major benthic habitat types, the area of habitat potentially subject to medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
The D7 assessment, based on data on anthropogenic activities, highlighted significant variations in exposure to pressures:1/ The Z200 zone is less subject than the coastal zone (MEC DCE) to exposure to the hydrographic pressures under consideration.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (58% of the northern subdivision of the Bay of Biscay marine sub-region). However, the exposure index remains mostly low, and for 90% of the major benthic habitat types, the area of habitat potentially subject to medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
The D7 assessment, based on data on anthropogenic activities, highlighted significant variations in exposure to pressures:1/ The Z200 zone is less subject than the coastal zone (MEC DCE) to exposure to the hydrographic pressures under consideration.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (58% of the northern subdivision of the Bay of Biscay marine sub-region). However, the exposure index remains mostly low, and for 90% of the major benthic habitat types, the area of habitat potentially subject to medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
The D7 assessment, based on data on anthropogenic activities, highlighted significant variations in exposure to pressures:1/ The Z200 zone is less subject than the coastal zone (MEC DCE) to exposure to the hydrographic pressures under consideration.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (58% of the northern subdivision of the Bay of Biscay marine sub-region). However, the exposure index remains mostly low, and for 90% of the major benthic habitat types, the area of habitat potentially subject to medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
The D7 assessment, based on data on anthropogenic activities, highlighted significant variations in exposure to pressures:1/ The Z200 zone is less subject than the coastal zone (MEC DCE) to exposure to the hydrographic pressures under consideration.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (58% of the northern subdivision of the Bay of Biscay marine sub-region). However, the exposure index remains mostly low, and for 90% of the major benthic habitat types, the area of habitat potentially subject to medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
The D7 assessment, based on data on anthropogenic activities, highlighted significant variations in exposure to pressures:1/ The Z200 zone is less subject than the coastal zone (MEC DCE) to exposure to the hydrographic pressures under consideration.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (58% of the northern subdivision of the Bay of Biscay marine sub-region). However, the exposure index remains mostly low, and for 90% of the major benthic habitat types, the area of habitat potentially subject to medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
The D7 assessment, based on data on anthropogenic activities, highlighted significant variations in exposure to pressures:1/ The Z200 zone is less subject than the coastal zone (MEC DCE) to exposure to the hydrographic pressures under consideration.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (58% of the northern subdivision of the Bay of Biscay marine sub-region). However, the exposure index remains mostly low, and for 90% of the major benthic habitat types, the area of habitat potentially subject to medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
The D7 assessment, based on data on anthropogenic activities, highlighted significant variations in exposure to pressures:1/ The Z200 zone is less subject than the coastal zone (MEC DCE) to exposure to the hydrographic pressures under consideration.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (58% of the northern subdivision of the Bay of Biscay marine sub-region). However, the exposure index remains mostly low, and for 90% of the major benthic habitat types, the area of habitat potentially subject to medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
The D7 assessment, based on data on anthropogenic activities, highlighted significant variations in exposure to pressures:1/ The Z200 zone is less subject than the coastal zone (MEC DCE) to exposure to the hydrographic pressures under consideration.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (58% of the northern subdivision of the Bay of Biscay marine sub-region). However, the exposure index remains mostly low, and for 90% of the major benthic habitat types, the area of habitat potentially subject to medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
The D7 assessment, based on data on anthropogenic activities, highlighted significant variations in exposure to pressures:1/ The Z200 zone is less subject than the coastal zone (MEC DCE) to exposure to the hydrographic pressures under consideration.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (58% of the northern subdivision of the Bay of Biscay marine sub-region). However, the exposure index remains mostly low, and for 90% of the major benthic habitat types, the area of habitat potentially subject to medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
Assessments period
2012-2018
2012-2018
2012-2018
2012-2018
2012-2018
2012-2018
2012-2018
2012-2018
2012-2018
2012-2018
2012-2018
2012-2018
2012-2018
2012-2018
2012-2018
2012-2018
2012-2018
2012-2018
2012-2018
Related pressures
Related targets

Sud SRM GdG L200 (ABI-FR-MS-GDG-SUD-L200)

GES component
D7
D7
D7
D7
D7
D7
D7
D7
D7
D7
D7
Feature
Hydrographical changes
Hydrographical changes
Hydrographical changes
Hydrographical changes
Hydrographical changes
Hydrographical changes
Hydrographical changes
Benthic broad habitats
Benthic broad habitats
Benthic broad habitats
Benthic broad habitats
Element
Changes in current regime
Changes in salinity regime
Changes in seabed substrate
Changes in thermal regime
Changes in tide regime
Changes in turbidity regime
Changes in waves regime
Circalittoral sand
Offshore circalittoral coarse sediment
Offshore circalittoral mud
Offshore circalittoral sand
Element code
ExpPresCurrents
ExpPresSalinity
ExpPresSeabedNature
ExpPresTemperature
ExpPresTide
ExpPresTurbidity
ExpPresWaves
HabBenCircalitSand
HabBenOffshCoarSed
HabBenOffshMud
HabBenOffshSand
Element code source
Link to other vocabulary or code lists that may be relevant
Link to other vocabulary or code lists that may be relevant
Link to other vocabulary or code lists that may be relevant
Link to other vocabulary or code lists that may be relevant
Link to other vocabulary or code lists that may be relevant
Link to other vocabulary or code lists that may be relevant
Link to other vocabulary or code lists that may be relevant
Habitats (D1-D6) http://dd.eionet.europa.eu/vocabulary/msfd/broadHabitatTypes/view
Habitats (D1-D6) http://dd.eionet.europa.eu/vocabulary/msfd/broadHabitatTypes/view
Habitats (D1-D6) http://dd.eionet.europa.eu/vocabulary/msfd/broadHabitatTypes/view
Habitats (D1-D6) http://dd.eionet.europa.eu/vocabulary/msfd/broadHabitatTypes/view
Element 2
Element 2 code
Element 2 code source
Element source
National
National
National
National
National
National
National
EU
EU
EU
EU
Criterion
D7C1
D7C1
D7C1
D7C1
D7C1
D7C1
D7C1
D7C2
D7C2
D7C2
D7C2
Parameter
Extent
Extent
Extent
Extent
Extent
Extent
Extent
Extent
Extent
Extent
Extent
Parameter other
Threshold value upper
Threshold value lower
Threshold qualitative
Not available yet
Not available yet
Not available yet
Not available yet
Not available yet
Not available yet
Not available yet
Not available yet
Not available yet
Not available yet
Not available yet
Threshold value source
Threshold value source other
Value achieved upper
Value achieved lower
Value unit
Value unit other
Proportion threshold value
Proportion value achieved
9911.0
9911.0
3.4
34.0
148.0
646.0
Proportion threshold value unit
extent in km2 of pressure
extent in km2 of pressure
extent in km2 of pressure
extent in km2 of pressure
extent in km2 of pressure
extent in km2 of pressure
extent in km2 of pressure
extent in km2 of habitat adversely affected
extent in km2 of habitat adversely affected
extent in km2 of habitat adversely affected
extent in km2 of habitat adversely affected
Trend
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Parameter achieved
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Description parameter
The metric considered for this parameter is the area of exposure for each pressure considered (overall or as a function of the level of the exposure index). The areas potentially affected by a change in the current regime correspond to a total area of 0 km2 . The areas of exposure according to the four levels of the exposure index are No exposure: 482630 km² Low exposure index: 0 km² Medium exposure index: 0 km² High exposure index: 0 km² Note that no threshold is currently available to assess whether or not the parameter has been reached.
The metric considered for this parameter is the area of exposure for each pressure considered (overall or as a function of the level of the exposure index). The areas potentially affected by a change in salinity regime correspond to a total surface area of 0 km2 . The areas of exposure according to the four levels of the exposure index are No exposure: 48630 km² Low exposure index: 0 km² Medium exposure index: 0 km² High exposure index: 0 km² Note that no threshold is currently available to assess whether or not the parameter has been reached.
The metric considered for this parameter is the area of exposure for each pressure considered (overall or as a function of the level of the exposure index). The areas potentially affected by a change in the background nature correspond to a total area of 9911 km2 . The areas of exposure according to the four levels of exposure index are: No exposure: 38718 km² Low exposure index: 9911 km² Medium exposure index: 0 km² High exposure index: 0 km² Note that no threshold is currently available to assess whether or not the parameter has been reached.
The metric considered for this parameter is the area of exposure for each pressure considered (overall or as a function of the level of the exposure index). The areas potentially affected by a change in the thermal regime correspond to a total area of 0 km2 . The areas of exposure according to the four levels of exposure index are: No exposure: 48630 km² Low exposure index: 0 km² Medium exposure index: 0 km² High exposure index: 0 km² Note that no threshold is currently available to assess whether or not the parameter has been reached.
The metric considered for this parameter is the area of exposure for each pressure considered (overall or as a function of the level of the exposure index). The areas potentially affected by a change in the tidal regime correspond to a total area of 0 km2 , based on the four levels of exposure index: No exposure: 48630 km² Low exposure index: 0 km² Medium exposure index: 0 km² High exposure index: 0 km² Note that no threshold is currently available to assess whether or not the parameter has been reached.
The metric considered for this parameter is the area of exposure for each pressure considered (overall or as a function of the level of the exposure index). The areas potentially affected by a change in the turbidity regime correspond to a total area of 9911 km2 . The areas of exposure according to the four levels of exposure index are: No exposure: 38718 km² Low exposure index: 9911 km² Medium exposure index: 0 km² High exposure index: 0 km² Note that no threshold is currently available to assess whether or not the parameter has been reached.
The metric considered for this parameter is the area of exposure for each pressure considered (overall or as a function of the level of the exposure index). The areas potentially affected by a change in the wave regime correspond to a total area of 0 km2 . The areas of exposure according to the four levels of the exposure index are No Exposure: 48630 km² Low Exposure Index: 0 km² Medium Exposure Index: 0 km² High Exposure Index: 0 km² Note that no threshold is currently available to assess whether or not the parameter has been reached.
The metric considered for this parameter is the area of habitat potentially at risk (overall or based on the level of risk). The spatial extent of potential habitat alteration associated with permanent changes in hydrographic conditions in this MRU is 3 km2 (i.e., 100% of the assessed habitat). In addition, the indicator makes it possible to assess the intensity of the risk of modification: negligible or nil risk of modification: 0 km², low risk of modification: 3 km², medium risk of modification: 0 km², high risk of modification: 0 km², and no threshold is currently available to assess whether or not the parameter has been reached.
The metric considered for this parameter is the area of habitat potentially at risk (overall or based on the level of risk). The spatial extent of potential habitat alteration associated with permanent changes in hydrographic conditions in this MRU is 34 km2 (i.e., 100% of the assessed habitat). In addition, the indicator makes it possible to assess the intensity of the risk of modification: negligible or nil risk of modification: 0 km², low risk of modification: 10 km², medium risk of modification: 24 km², high risk of modification: 0 km², it should be noted that no threshold is currently available to assess whether or not the parameter has been reached.
The metric considered for this parameter is the area of habitat potentially at risk (overall or based on the level of risk). The spatial extent of potential habitat alteration related to permanent changes in hydrographic conditions in this MRU is 148 km2 (i.e., 100% of the assessed habitat). In addition, the indicator makes it possible to assess the intensity of the risk of modification: negligible or nil risk of modification: 0 km², low risk of modification: 34 km², medium risk of modification: 113 km², high risk of modification: 0 km², it should be noted that no threshold is currently available to assess whether or not the parameter has been reached.
The metric considered for this parameter is the area of habitat potentially at risk (overall or based on the level of risk). The spatial extent of potential habitat alteration associated with permanent changes in hydrographic conditions in this MRU is 646 km2 (i.e., 100% of the assessed habitat). In addition, the indicator makes it possible to assess the intensity of the risk of modification: negligible or nil risk of modification: 0 km², low risk of modification: 302 km², medium risk of modification: 343 km², high risk of modification: 0 km², it should be noted that no threshold is currently available to assess whether or not the parameter has been reached.
Related indicator
Criteria status
Contributes to assessment of another criterion/ele
Contributes to assessment of another criterion/ele
Contributes to assessment of another criterion/ele
Contributes to assessment of another criterion/ele
Contributes to assessment of another criterion/ele
Contributes to assessment of another criterion/ele
Contributes to assessment of another criterion/ele
Unknown
Unknown
Unknown
Unknown
Description criteria
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017) no threshold is to be specified for D7C1: the status of the D7C1 criterion is therefore not reported. However, the assessment of the D7C1 criterion has provided a first estimate of the exposure indices for spatial areas potentially affected by a change in current, tidal, wave, bottom nature, turbidity, thermal and salinity regimes. Indeed, the results show that the pressures linked to a change in the current, tidal and wave regime are relatively low (< 1% of the southern subdivision of the Bay of Biscay marine sub-region). They do not affect the wide area and therefore represent 0% of the area of this MRU. Pressures related to a change in bottom nature and turbidity regime potentially affect a relatively small area (20% of the MRU), so the offshore area is the least affected. The exposure indices calculated for these pressures are mostly low. Finally, pressures related to a change in thermal and salinity regime affect less than 1% of the MRU.
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017) no threshold is to be specified for D7C1: the status of the D7C1 criterion is therefore not reported. However, the assessment of the D7C1 criterion has provided a first estimate of the exposure indices for spatial areas potentially affected by a change in current, tidal, wave, bottom nature, turbidity, thermal and salinity regimes. Indeed, the results show that the pressures linked to a change in the current, tidal and wave regime are relatively low (< 1% of the southern subdivision of the Bay of Biscay marine sub-region). They do not affect the wide area and therefore represent 0% of the area of this MRU. Pressures related to a change in bottom nature and turbidity regime potentially affect a relatively small area (20% of the MRU), so the offshore area is the least affected. The exposure indices calculated for these pressures are mostly low. Finally, pressures related to a change in thermal and salinity regime affect less than 1% of the MRU.
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017) no threshold is to be specified for D7C1: the status of the D7C1 criterion is therefore not reported. However, the assessment of the D7C1 criterion has provided a first estimate of the exposure indices for spatial areas potentially affected by a change in current, tidal, wave, bottom nature, turbidity, thermal and salinity regimes. Indeed, the results show that the pressures linked to a change in the current, tidal and wave regime are relatively low (< 1% of the southern subdivision of the Bay of Biscay marine sub-region). They do not affect the wide area and therefore represent 0% of the area of this MRU. Pressures related to a change in bottom nature and turbidity regime potentially affect a relatively small area (20% of the MRU), so the offshore area is the least affected. The exposure indices calculated for these pressures are mostly low. Finally, pressures related to a change in thermal and salinity regime affect less than 1% of the MRU.
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017) no threshold is to be specified for D7C1: the status of the D7C1 criterion is therefore not reported. However, the assessment of the D7C1 criterion has provided a first estimate of the exposure indices for spatial areas potentially affected by a change in current, tidal, wave, bottom nature, turbidity, thermal and salinity regimes. Indeed, the results show that the pressures linked to a change in the current, tidal and wave regime are relatively low (< 1% of the southern subdivision of the Bay of Biscay marine sub-region). They do not affect the wide area and therefore represent 0% of the area of this MRU. Pressures related to a change in bottom nature and turbidity regime potentially affect a relatively small area (20% of the MRU), so the offshore area is the least affected. The exposure indices calculated for these pressures are mostly low. Finally, pressures related to a change in thermal and salinity regime affect less than 1% of the MRU.
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017) no threshold is to be specified for D7C1: the status of the D7C1 criterion is therefore not reported. However, the assessment of the D7C1 criterion has provided a first estimate of the exposure indices for spatial areas potentially affected by a change in current, tidal, wave, bottom nature, turbidity, thermal and salinity regimes. Indeed, the results show that the pressures linked to a change in the current, tidal and wave regime are relatively low (< 1% of the southern subdivision of the Bay of Biscay marine sub-region). They do not affect the wide area and therefore represent 0% of the area of this MRU. Pressures related to a change in bottom nature and turbidity regime potentially affect a relatively small area (20% of the MRU), so the offshore area is the least affected. The exposure indices calculated for these pressures are mostly low. Finally, pressures related to a change in thermal and salinity regime affect less than 1% of the MRU.
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017) no threshold is to be specified for D7C1: the status of the D7C1 criterion is therefore not reported. However, the assessment of the D7C1 criterion has provided a first estimate of the exposure indices for spatial areas potentially affected by a change in current, tidal, wave, bottom nature, turbidity, thermal and salinity regimes. Indeed, the results show that the pressures linked to a change in the current, tidal and wave regime are relatively low (< 1% of the southern subdivision of the Bay of Biscay marine sub-region). They do not affect the wide area and therefore represent 0% of the area of this MRU. Pressures related to a change in bottom nature and turbidity regime potentially affect a relatively small area (20% of the MRU), so the offshore area is the least affected. The exposure indices calculated for these pressures are mostly low. Finally, pressures related to a change in thermal and salinity regime affect less than 1% of the MRU.
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017) no threshold is to be specified for D7C1: the status of the D7C1 criterion is therefore not reported. However, the assessment of the D7C1 criterion has provided a first estimate of the exposure indices for spatial areas potentially affected by a change in current, tidal, wave, bottom nature, turbidity, thermal and salinity regimes. Indeed, the results show that the pressures linked to a change in the current, tidal and wave regime are relatively low (< 1% of the southern subdivision of the Bay of Biscay marine sub-region). They do not affect the wide area and therefore represent 0% of the area of this MRU. Pressures related to a change in bottom nature and turbidity regime potentially affect a relatively small area (20% of the MRU), so the offshore area is the least affected. The exposure indices calculated for these pressures are mostly low. Finally, pressures related to a change in thermal and salinity regime affect less than 1% of the MRU.
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017), the D7C2 assessment must be carried out for each habitat type that is affected by changing hydrographic conditions and the D7C2 results are not integrated. On the other hand, no threshold has been defined so far for the parameter "Extent" and therefore the status of D7C2 is not reported, but the assessment of D7C2 has provided a first estimate of the spatial extent of benthic habitats potentially subject to cumulative risks of alteration, based on the indices of exposure to hydrographic pressures generated by human activities. Thus, the coastal circalittoral sands habitat is entirely at low risk (100% of the total habitat area).
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017), the D7C2 assessment must be carried out for each habitat type that is affected by changing hydrographic conditions and the D7C2 results are not integrated. On the other hand, no threshold has been defined so far for the parameter "Extent" and therefore the status of D7C2 is not reported, but the assessment of D7C2 has provided a first estimate of the spatial extent of benthic habitats potentially subject to cumulative risks of alteration, based on the indices of exposure to hydrographic pressures generated by human activities. For example, 70% of the area of offshore circalittoral coarse sediment habitat appears to be at medium risk and 30% at low risk.
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017), the D7C2 assessment must be carried out for each habitat type that is affected by changing hydrographic conditions and the D7C2 results are not integrated. On the other hand, no threshold has been defined so far for the parameter "Extent" and therefore the status of D7C2 is not reported, but the assessment of D7C2 has provided a first estimate of the spatial extent of benthic habitats potentially subject to cumulative risks of alteration, based on the indices of exposure to hydrographic pressures generated by human activities. Thus, 77% of the area of "offshore circalittoral mud flats" habitat appears to be at medium risk and 23% at low risk.
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017), the D7C2 assessment must be carried out for each habitat type that is affected by changing hydrographic conditions and the D7C2 results are not integrated. On the other hand, no threshold has been defined so far for the parameter "Extent" and therefore the status of D7C2 is not reported, but the assessment of D7C2 has provided a first estimate of the spatial extent of benthic habitats potentially subject to cumulative risks of alteration, based on the indices of exposure to hydrographic pressures generated by human activities. Thus, 53% of the area of offshore circalittoral sands habitat appears to be at medium risk and 47% at low risk.
Element status
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Description element
The assessment of criterion D7C1 contributes to the assessment of criterion D7C2. Thus, the accumulation of quantified pressures (i.e., exposure indices) under D7C1 is incorporated into the calculation of the risk of modification of each habitat for the D7C2 assessment.
The assessment of criterion D7C1 contributes to the assessment of criterion D7C2. Thus, the accumulation of quantified pressures (i.e., exposure indices) under D7C1 is incorporated into the calculation of the risk of modification of each habitat for the D7C2 assessment.
The assessment of criterion D7C1 contributes to the assessment of criterion D7C2. Thus, the accumulation of quantified pressures (i.e., exposure indices) under D7C1 is incorporated into the calculation of the risk of modification of each habitat for the D7C2 assessment.
The assessment of criterion D7C1 contributes to the assessment of criterion D7C2. Thus, the accumulation of quantified pressures (i.e., exposure indices) under D7C1 is incorporated into the calculation of the risk of modification of each habitat for the D7C2 assessment.
The assessment of criterion D7C1 contributes to the assessment of criterion D7C2. Thus, the accumulation of quantified pressures (i.e., exposure indices) under D7C1 is incorporated into the calculation of the risk of modification of each habitat for the D7C2 assessment.
The assessment of criterion D7C1 contributes to the assessment of criterion D7C2. Thus, the accumulation of quantified pressures (i.e., exposure indices) under D7C1 is incorporated into the calculation of the risk of modification of each habitat for the D7C2 assessment.
The assessment of criterion D7C1 contributes to the assessment of criterion D7C2. Thus, the accumulation of quantified pressures (i.e., exposure indices) under D7C1 is incorporated into the calculation of the risk of modification of each habitat for the D7C2 assessment.
In the absence of a threshold for the "Extent" parameter, the state of the habitat could not be provided. Furthermore, according to Decision 2017/848/EU, the results of the assessment of criterion D7C2 (estimated extent of adverse effects by habitat type in each assessment area) are used for the assessment of criterion D6C5. However, in the absence of an operational indicator at the level of Descriptor 6 - Benthic Habitats, these results could not be taken into account in the assessment of D6C5.
In the absence of a threshold for the "Extent" parameter, the state of the habitat could not be provided. Furthermore, according to Decision 2017/848/EU, the results of the assessment of criterion D7C2 (estimated extent of adverse effects by habitat type in each assessment area) are used for the assessment of criterion D6C5. However, in the absence of an operational indicator at the level of Descriptor 6 - Benthic Habitats, these results could not be taken into account in the assessment of D6C5.
In the absence of a threshold for the "Extent" parameter, the state of the habitat could not be provided. Furthermore, according to Decision 2017/848/EU, the results of the assessment of criterion D7C2 (estimated extent of adverse effects by habitat type in each assessment area) are used for the assessment of criterion D6C5. However, in the absence of an operational indicator at the level of Descriptor 6 - Benthic Habitats, these results could not be taken into account in the assessment of D6C5.
In the absence of a threshold for the "Extent" parameter, the state of the habitat could not be provided. Furthermore, according to Decision 2017/848/EU, the results of the assessment of criterion D7C2 (estimated extent of adverse effects by habitat type in each assessment area) are used for the assessment of criterion D6C5. However, in the absence of an operational indicator at the level of Descriptor 6 - Benthic Habitats, these results could not be taken into account in the assessment of D6C5.
Integration rule type parameter
Not relevant
Not relevant
Not relevant
Not relevant
Not relevant
Not relevant
Not relevant
Not relevant
Not relevant
Not relevant
Not relevant
Integration rule description parameter
Integration rule type criteria
Not relevant
Not relevant
Not relevant
Not relevant
Not relevant
Not relevant
Not relevant
Not relevant
Not relevant
Not relevant
Not relevant
Integration rule description criteria
GES extent threshold
GES extent achieved
GES extent unit
GES achieved
Not relevant
Not relevant
Not relevant
Not relevant
Not relevant
Not relevant
Not relevant
Not relevant
Not relevant
Not relevant
Not relevant
Description overall status
The assessment of D7, based on data on anthropogenic activities, highlighted significant variations in exposure to pressures:1/ The L200 zone is less subject than the coastal zone (MEC DCE) to exposure to the hydrographic pressures considered.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (53% of the southern subdivision of the Bay of Biscay marine sub-region). However, the exposure index remains mostly low, and for 90% of the major benthic habitat types, the area of habitat potentially at risk of moderate to high modification is greater than 30% of the total habitat area, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
The assessment of D7, based on data on anthropogenic activities, highlighted significant variations in exposure to pressures:1/ The L200 zone is less subject than the coastal zone (MEC DCE) to exposure to the hydrographic pressures considered.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (53% of the southern subdivision of the Bay of Biscay marine sub-region). However, the exposure index remains mostly low, and for 90% of the major benthic habitat types, the area of habitat potentially at risk of moderate to high modification is greater than 30% of the total habitat area, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
The assessment of D7, based on data on anthropogenic activities, highlighted significant variations in exposure to pressures:1/ The L200 zone is less subject than the coastal zone (MEC DCE) to exposure to the hydrographic pressures considered.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (53% of the southern subdivision of the Bay of Biscay marine sub-region). However, the exposure index remains mostly low, and for 90% of the major benthic habitat types, the area of habitat potentially at risk of moderate to high modification is greater than 30% of the total habitat area, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
The assessment of D7, based on data on anthropogenic activities, highlighted significant variations in exposure to pressures:1/ The L200 zone is less subject than the coastal zone (MEC DCE) to exposure to the hydrographic pressures considered.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (53% of the southern subdivision of the Bay of Biscay marine sub-region). However, the exposure index remains mostly low, and for 90% of the major benthic habitat types, the area of habitat potentially at risk of moderate to high modification is greater than 30% of the total habitat area, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
The assessment of D7, based on data on anthropogenic activities, highlighted significant variations in exposure to pressures:1/ The L200 zone is less subject than the coastal zone (MEC DCE) to exposure to the hydrographic pressures considered.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (53% of the southern subdivision of the Bay of Biscay marine sub-region). However, the exposure index remains mostly low, and for 90% of the major benthic habitat types, the area of habitat potentially at risk of moderate to high modification is greater than 30% of the total habitat area, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
The assessment of D7, based on data on anthropogenic activities, highlighted significant variations in exposure to pressures:1/ The L200 zone is less subject than the coastal zone (MEC DCE) to exposure to the hydrographic pressures considered.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (53% of the southern subdivision of the Bay of Biscay marine sub-region). However, the exposure index remains mostly low, and for 90% of the major benthic habitat types, the area of habitat potentially at risk of moderate to high modification is greater than 30% of the total habitat area, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
The assessment of D7, based on data on anthropogenic activities, highlighted significant variations in exposure to pressures:1/ The L200 zone is less subject than the coastal zone (MEC DCE) to exposure to the hydrographic pressures considered.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (53% of the southern subdivision of the Bay of Biscay marine sub-region). However, the exposure index remains mostly low, and for 90% of the major benthic habitat types, the area of habitat potentially at risk of moderate to high modification is greater than 30% of the total habitat area, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
The assessment of D7, based on data on anthropogenic activities, highlighted significant variations in exposure to pressures:1/ The L200 zone is less subject than the coastal zone (MEC DCE) to exposure to the hydrographic pressures considered.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (53% of the southern subdivision of the Bay of Biscay marine sub-region). However, the exposure index remains mostly low, and for 90% of the major benthic habitat types, the area of habitat potentially at risk of moderate to high modification is greater than 30% of the total habitat area, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
The assessment of D7, based on data on anthropogenic activities, highlighted significant variations in exposure to pressures:1/ The L200 zone is less subject than the coastal zone (MEC DCE) to exposure to the hydrographic pressures considered.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (53% of the southern subdivision of the Bay of Biscay marine sub-region). However, the exposure index remains mostly low, and for 90% of the major benthic habitat types, the area of habitat potentially at risk of moderate to high modification is greater than 30% of the total habitat area, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
The assessment of D7, based on data on anthropogenic activities, highlighted significant variations in exposure to pressures:1/ The L200 zone is less subject than the coastal zone (MEC DCE) to exposure to the hydrographic pressures considered.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (53% of the southern subdivision of the Bay of Biscay marine sub-region). However, the exposure index remains mostly low, and for 90% of the major benthic habitat types, the area of habitat potentially at risk of moderate to high modification is greater than 30% of the total habitat area, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
The assessment of D7, based on data on anthropogenic activities, highlighted significant variations in exposure to pressures:1/ The L200 zone is less subject than the coastal zone (MEC DCE) to exposure to the hydrographic pressures considered.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (53% of the southern subdivision of the Bay of Biscay marine sub-region). However, the exposure index remains mostly low, and for 90% of the major benthic habitat types, the area of habitat potentially at risk of moderate to high modification is greater than 30% of the total habitat area, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
Assessments period
2012-2018
2012-2018
2012-2018
2012-2018
2012-2018
2012-2018
2012-2018
2012-2018
2012-2018
2012-2018
2012-2018
Related pressures
Related targets

Sud SRM GdG MEC DCE (ABI-FR-MS-GDG-SUD-MEC2010)

GES component
D7
D7
D7
D7
D7
D7
D7
D7
D7
D7
D7
D7
D7
D7
D7
D7
Feature
Hydrographical changes
Hydrographical changes
Hydrographical changes
Hydrographical changes
Hydrographical changes
Hydrographical changes
Hydrographical changes
Benthic broad habitats
Benthic broad habitats
Benthic broad habitats
Benthic broad habitats
Benthic broad habitats
Benthic broad habitats
Benthic broad habitats
Benthic broad habitats
Benthic broad habitats
Element
Changes in current regime
Changes in salinity regime
Changes in seabed substrate
Changes in thermal regime
Changes in tide regime
Changes in turbidity regime
Changes in waves regime
Circalittoral coarse sediment
Circalittoral mud
Circalittoral rock and biogenic reef
Circalittoral sand
Infralittoral coarse sediment
Infralittoral mud
Infralittoral rock and biogenic reef
Infralittoral sand
Offshore circalittoral mud
Element code
ExpPresCurrents
ExpPresSalinity
ExpPresSeabedNature
ExpPresTemperature
ExpPresTide
ExpPresTurbidity
ExpPresWaves
HabBenCircalitCoarSed
HabBenCircalitMud
HabBenCircalitRock
HabBenCircalitSand
HabBenInfralitCoarSed
HabBenInfralitMud
HabBenInfralitRock
HabBenInfralitSand
HabBenOffshMud
Element code source
Link to other vocabulary or code lists that may be relevant
Link to other vocabulary or code lists that may be relevant
Link to other vocabulary or code lists that may be relevant
Link to other vocabulary or code lists that may be relevant
Link to other vocabulary or code lists that may be relevant
Link to other vocabulary or code lists that may be relevant
Link to other vocabulary or code lists that may be relevant
Habitats (D1-D6) http://dd.eionet.europa.eu/vocabulary/msfd/broadHabitatTypes/view
Habitats (D1-D6) http://dd.eionet.europa.eu/vocabulary/msfd/broadHabitatTypes/view
Habitats (D1-D6) http://dd.eionet.europa.eu/vocabulary/msfd/broadHabitatTypes/view
Habitats (D1-D6) http://dd.eionet.europa.eu/vocabulary/msfd/broadHabitatTypes/view
Habitats (D1-D6) http://dd.eionet.europa.eu/vocabulary/msfd/broadHabitatTypes/view
Habitats (D1-D6) http://dd.eionet.europa.eu/vocabulary/msfd/broadHabitatTypes/view
Habitats (D1-D6) http://dd.eionet.europa.eu/vocabulary/msfd/broadHabitatTypes/view
Habitats (D1-D6) http://dd.eionet.europa.eu/vocabulary/msfd/broadHabitatTypes/view
Habitats (D1-D6) http://dd.eionet.europa.eu/vocabulary/msfd/broadHabitatTypes/view
Element 2
Element 2 code
Element 2 code source
Element source
National
National
National
National
National
National
National
EU
EU
EU
EU
EU
EU
EU
EU
EU
Criterion
D7C1
D7C1
D7C1
D7C1
D7C1
D7C1
D7C1
D7C2
D7C2
D7C2
D7C2
D7C2
D7C2
D7C2
D7C2
D7C2
Parameter
Extent
Extent
Extent
Extent
Extent
Extent
Extent
Extent
Extent
Extent
Extent
Extent
Extent
Extent
Extent
Extent
Parameter other
Threshold value upper
Threshold value lower
Threshold qualitative
Not available yet
Not available yet
Not available yet
Not available yet
Not available yet
Not available yet
Not available yet
Not available yet
Not available yet
Not available yet
Not available yet
Not available yet
Not available yet
Not available yet
Not available yet
Not available yet
Threshold value source
Threshold value source other
Value achieved upper
Value achieved lower
Value unit
Value unit other
Proportion threshold value
Proportion value achieved
543.0
10.0
1882.0
10.0
536.0
1889.0
536.0
100.0
182.0
151.0
395.0
24.0
182.0
165.0
285.0
21.0
Proportion threshold value unit
extent in km2 of pressure
extent in km2 of pressure
extent in km2 of pressure
extent in km2 of pressure
extent in km2 of pressure
extent in km2 of pressure
extent in km2 of pressure
extent in km2 of habitat adversely affected
extent in km2 of habitat adversely affected
extent in km2 of habitat adversely affected
extent in km2 of habitat adversely affected
extent in km2 of habitat adversely affected
extent in km2 of habitat adversely affected
extent in km2 of habitat adversely affected
extent in km2 of habitat adversely affected
extent in km2 of habitat adversely affected
Trend
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Parameter achieved
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Description parameter
The metric considered for this parameter is the area of exposure for each pressure considered (overall or as a function of the level of the exposure index). The areas potentially affected by a change in the current regime correspond to a total area of 543 km2 , based on the four levels of exposure index: No exposure: 1,367 km² Low exposure index: 460 km² Medium exposure index: 82 km² High exposure index: 0 km² Note that no threshold is currently available to assess whether or not the parameter has been reached.
The metric considered for this parameter is the area of exposure for each pressure considered (overall or as a function of the level of the exposure index). The areas potentially affected by a change in salinity regime correspond to a total surface area of <10 km2 . The areas of exposure according to the four levels of the exposure index are No exposure: 1890 km² Low exposure index: <10 km² Medium exposure index: 0 km² High exposure index: 0 km² Note that no threshold is currently available to assess whether or not the parameter has been reached.
The metric considered for this parameter is the area of exposure for each pressure considered (overall or as a function of the level of the exposure index). The areas potentially affected by a change in background nature correspond to a total surface area of 1882 km2 , based on the four levels of exposure index: No exposure: 10 km² Low exposure index: 1724 km² Medium exposure index: 158 km² High exposure index: 0 km² Note that no threshold is currently available to assess whether or not the parameter has been reached.
The metric considered for this parameter is the area of exposure for each pressure considered (overall or as a function of the level of the exposure index). The areas potentially affected by a change in the thermal regime correspond to a total surface area of <10 km2 . The areas of exposure according to the four levels of the exposure index are No exposure: 1890 km².Low exposure index: <10 km².Medium exposure index: 0 km².High exposure index: 0 km².Note that no threshold is currently available to assess whether or not the parameter has been reached.
The metric considered for this parameter is the area of exposure for each pressure considered (overall or as a function of the level of the exposure index). The areas potentially affected by a change in the tidal regime correspond to a total area of 536 km2 , based on the four levels of exposure index: No exposure: 1374 km² Low exposure index: 422 km² Medium exposure index: 113 km² High exposure index: 0 km² Note that no threshold is currently available to assess whether or not the parameter has been reached.
The metric considered for this parameter is the area of exposure for each pressure considered (overall or as a function of the level of the exposure index). The areas potentially affected by a change in the turbidity regime correspond to a total area of 1889 km2 . The areas of exposure according to the four levels of exposure index are No exposure: 21 km².Low exposure index: 1250 km².Medium exposure index: 622 km².High exposure index: 17 km².It should be noted that no threshold is currently available to assess whether or not the parameter has been reached.
The metric considered for this parameter is the area of exposure for each pressure considered (overall or as a function of the level of the exposure index). The areas potentially affected by a change in the wave regime correspond to a total area of 536 km2 , based on the four levels of exposure index: No Exposure: 1374 km² Low Exposure Index: 518 km² Medium Exposure Index: 17 km² High Exposure Index: 0 km² Note that no threshold is currently available to assess whether or not the parameter has been reached.
The metric considered for this parameter is the area of habitat potentially at risk (overall or based on the level of risk). The spatial extent of potential habitat modification related to permanent changes in hydrographic conditions in this MRU is 100 km2 (i.e. 100% of the assessed habitat). Furthermore, the indicator makes it possible to assess the intensity of the risk of modification: negligible or no risk of modification: 0 km², low risk of modification: 58 km², medium risk of modification: 38 km², high risk of modification: 3 km², although no threshold is currently available to assess whether or not the parameter has been reached.
The metric considered for this parameter is the area of habitat potentially at risk (overall or based on the level of risk). The spatial extent of potential habitat modification related to permanent changes in hydrographic conditions in this MRU is 182 km2 (96% of the assessed habitat). In addition, the indicator makes it possible to assess the intensity of the risk of modification: negligible or nil risk of modification: 7 km², low risk of modification: 96 km², medium risk of modification: 55 km², high risk of modification: 31 km², although no threshold is currently available to assess whether or not the parameter has been reached.
The metric considered for this parameter is the area of habitat potentially at risk (overall or as a function of the level of risk). The spatial extent of potential habitat modification related to permanent changes in hydrographic conditions in this MRU is 151 km2 (i.e. 100% of the habitat assessed). Furthermore, the indicator makes it possible to assess the intensity of the risk of modification: negligible or no risk of modification: 0 km², low risk of modification: 76 km², medium risk of modification: 72 km², high risk of modification: 3 km², although no threshold is currently available to assess whether or not the parameter has been reached.
The metric considered for this parameter is the area of habitat potentially at risk (overall or based on the level of risk). The spatial extent of potential habitat modification related to permanent changes in hydrographic conditions in this MRU is 395 km2 (i.e. 100% of the assessed habitat). Furthermore, the indicator makes it possible to assess the intensity of the risk of modification: negligible or no risk of modification: 0 km², low risk of modification: 110 km², medium risk of modification: 271 km², high risk of modification: 14 km², although no threshold is currently available to assess whether or not the parameter has been reached.
The metric considered for this parameter is the area of habitat potentially at risk (overall or as a function of the level of risk). The spatial extent of potential habitat modification related to permanent changes in hydrographic conditions in this MRU is 24 km2 (i.e. 100% of the habitat assessed). Furthermore, the indicator makes it possible to assess the intensity of the risk of modification: negligible or no risk of modification: 0 km², low risk of modification: 3 km², medium risk of modification: 14 km², high risk of modification: 7 km², although no threshold is currently available to assess whether or not the parameter has been reached.
The metric considered for this parameter is the area of habitat potentially at risk (overall or based on the level of risk). The spatial extent of potential habitat modification related to permanent changes in hydrographic conditions in this MRU is 182 km2 (i.e. 100% of the assessed habitat). In addition, the indicator makes it possible to assess the intensity of the risk of modification: negligible or nil risk of modification: 0 km², low risk of modification: 65 km², medium risk of modification: 52 km², high risk of modification: 65 km², although no threshold is currently available to assess whether or not the parameter has been reached.
The metric considered for this parameter is the area of habitat potentially at risk (overall or based on the level of risk). The spatial extent of potential habitat alteration associated with permanent changes in hydrographic conditions in this MRU is 165 km2 (i.e., 100% of the assessed habitat). In addition, the indicator makes it possible to assess the intensity of the risk of modification: negligible or nil risk of modification: 0 km², low risk of modification: 21 km², medium risk of modification: 93 km², high risk of modification: 51 km², although no threshold is currently available to assess whether or not the parameter has been reached.
The metric considered for this parameter is the area of habitat potentially at risk (overall or as a function of the level of risk). The spatial extent of potential habitat modification related to permanent changes in hydrographic conditions in this MRU is 285 km2 (i.e. 100% of the habitat assessed). In addition, the indicator makes it possible to assess the intensity of the risk of modification: negligible or nil risk of modification: 0 km², low risk of modification: 31 km², medium risk of modification: 196 km², high risk of modification: 58 km², it should be noted that no threshold is currently available to assess whether or not the parameter has been reached.
The metric considered for this parameter is the area of habitat potentially at risk (overall or as a function of the level of risk). The spatial extent of potential habitat modification related to permanent changes in hydrographic conditions in this MRU is 21 km2 (i.e. 100% of the habitat assessed). Furthermore, the indicator makes it possible to assess the intensity of the risk of modification: negligible or no risk of modification: 0 km², low risk of modification: 14 km², medium risk of modification: 3 km², high risk of modification: 3 km², although no threshold is currently available to assess whether or not the parameter has been reached.
Related indicator
Criteria status
Contributes to assessment of another criterion/ele
Contributes to assessment of another criterion/ele
Contributes to assessment of another criterion/ele
Contributes to assessment of another criterion/ele
Contributes to assessment of another criterion/ele
Contributes to assessment of another criterion/ele
Contributes to assessment of another criterion/ele
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Description criteria
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017) no threshold is to be specified for D7C1: the status of the D7C1 criterion is therefore not reported. However, the assessment of the D7C1 criterion has provided a first estimate of the exposure indices for spatial areas potentially affected by a change in current, tidal, wave, bottom nature, turbidity, thermal and salinity regimes. Indeed, the results show that the pressures linked to a change in the current, tidal and wave regime are relatively low (< 1% of the southern subdivision of the Bay of Biscay marine sub-region) and fairly localised since it is located almost exclusively in the coastal zone. They each represent 28% of the area of this MRU. It should also be noted that the exposure indices calculated for these pressures are mostly low. Pressures related to a change in the nature of the bottom and turbidity regime potentially affect a very large area (>99% of the MRU). The exposure indices calculated for the change in background are mostly low (>90% of the MRU), and higher for the change in turbidity regime in the coastal MRU (33% of the area of the MRU is subject to an average exposure index). Finally, pressures related to a change in thermal and salinity regime affect less than 1% of the MRU.
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017) no threshold is to be specified for D7C1: the status of the D7C1 criterion is therefore not reported. However, the assessment of the D7C1 criterion has provided a first estimate of the exposure indices for spatial areas potentially affected by a change in current, tidal, wave, bottom nature, turbidity, thermal and salinity regimes. Indeed, the results show that the pressures linked to a change in the current, tidal and wave regime are relatively low (< 1% of the southern subdivision of the Bay of Biscay marine sub-region) and fairly localised since it is located almost exclusively in the coastal zone. They each represent 28% of the area of this MRU. It should also be noted that the exposure indices calculated for these pressures are mostly low. Pressures related to a change in the nature of the bottom and turbidity regime potentially affect a very large area (>99% of the MRU). The exposure indices calculated for the change in background are mostly low (>90% of the MRU), and higher for the change in turbidity regime in the coastal MRU (33% of the area of the MRU is subject to an average exposure index). Finally, pressures related to a change in thermal and salinity regime affect less than 1% of the MRU.
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017) no threshold is to be specified for D7C1: the status of the D7C1 criterion is therefore not reported. However, the assessment of the D7C1 criterion has provided a first estimate of the exposure indices for spatial areas potentially affected by a change in current, tidal, wave, bottom nature, turbidity, thermal and salinity regimes. Indeed, the results show that the pressures linked to a change in the current, tidal and wave regime are relatively low (< 1% of the southern subdivision of the Bay of Biscay marine sub-region) and fairly localised since it is located almost exclusively in the coastal zone. They each represent 28% of the area of this MRU. It should also be noted that the exposure indices calculated for these pressures are mostly low. Pressures related to a change in the nature of the bottom and turbidity regime potentially affect a very large area (>99% of the MRU). The exposure indices calculated for the change in background are mostly low (>90% of the MRU), and higher for the change in turbidity regime in the coastal MRU (33% of the area of the MRU is subject to an average exposure index). Finally, pressures related to a change in thermal and salinity regime affect less than 1% of the MRU.
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017) no threshold is to be specified for D7C1: the status of the D7C1 criterion is therefore not reported. However, the assessment of the D7C1 criterion has provided a first estimate of the exposure indices for spatial areas potentially affected by a change in current, tidal, wave, bottom nature, turbidity, thermal and salinity regimes. Indeed, the results show that the pressures linked to a change in the current, tidal and wave regime are relatively low (< 1% of the southern subdivision of the Bay of Biscay marine sub-region) and fairly localised since it is located almost exclusively in the coastal zone. They each represent 28% of the area of this MRU. It should also be noted that the exposure indices calculated for these pressures are mostly low. Pressures related to a change in the nature of the bottom and turbidity regime potentially affect a very large area (>99% of the MRU). The exposure indices calculated for the change in background are mostly low (>90% of the MRU), and higher for the change in turbidity regime in the coastal MRU (33% of the area of the MRU is subject to an average exposure index). Finally, pressures related to a change in thermal and salinity regime affect less than 1% of the MRU.
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017) no threshold is to be specified for D7C1: the status of the D7C1 criterion is therefore not reported. However, the assessment of the D7C1 criterion has provided a first estimate of the exposure indices for spatial areas potentially affected by a change in current, tidal, wave, bottom nature, turbidity, thermal and salinity regimes. Indeed, the results show that the pressures linked to a change in the current, tidal and wave regime are relatively low (< 1% of the southern subdivision of the Bay of Biscay marine sub-region) and fairly localised since it is located almost exclusively in the coastal zone. They each represent 28% of the area of this MRU. It should also be noted that the exposure indices calculated for these pressures are mostly low. Pressures related to a change in the nature of the bottom and turbidity regime potentially affect a very large area (>99% of the MRU). The exposure indices calculated for the change in background are mostly low (>90% of the MRU), and higher for the change in turbidity regime in the coastal MRU (33% of the area of the MRU is subject to an average exposure index). Finally, pressures related to a change in thermal and salinity regime affect less than 1% of the MRU.
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017) no threshold is to be specified for D7C1: the status of the D7C1 criterion is therefore not reported. However, the assessment of the D7C1 criterion has provided a first estimate of the exposure indices for spatial areas potentially affected by a change in current, tidal, wave, bottom nature, turbidity, thermal and salinity regimes. Indeed, the results show that the pressures linked to a change in the current, tidal and wave regime are relatively low (< 1% of the southern subdivision of the Bay of Biscay marine sub-region) and fairly localised since it is located almost exclusively in the coastal zone. They each represent 28% of the area of this MRU. It should also be noted that the exposure indices calculated for these pressures are mostly low. Pressures related to a change in the nature of the bottom and turbidity regime potentially affect a very large area (>99% of the MRU). The exposure indices calculated for the change in background are mostly low (>90% of the MRU), and higher for the change in turbidity regime in the coastal MRU (33% of the area of the MRU is subject to an average exposure index). Finally, pressures related to a change in thermal and salinity regime affect less than 1% of the MRU.
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017) no threshold is to be specified for D7C1: the status of the D7C1 criterion is therefore not reported. However, the assessment of the D7C1 criterion has provided a first estimate of the exposure indices for spatial areas potentially affected by a change in current, tidal, wave, bottom nature, turbidity, thermal and salinity regimes. Indeed, the results show that the pressures linked to a change in the current, tidal and wave regime are relatively low (< 1% of the southern subdivision of the Bay of Biscay marine sub-region) and fairly localised since it is located almost exclusively in the coastal zone. They each represent 28% of the area of this MRU. It should also be noted that the exposure indices calculated for these pressures are mostly low. Pressures related to a change in the nature of the bottom and turbidity regime potentially affect a very large area (>99% of the MRU). The exposure indices calculated for the change in background are mostly low (>90% of the MRU), and higher for the change in turbidity regime in the coastal MRU (33% of the area of the MRU is subject to an average exposure index). Finally, pressures related to a change in thermal and salinity regime affect less than 1% of the MRU.
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017), the D7C2 assessment must be carried out for each habitat type that is affected by changing hydrographic conditions and the D7C2 results are not integrated. On the other hand, no threshold has been defined so far for the parameter "Extent" and therefore the status of D7C2 is not reported, but the assessment of D7C2 has provided a first estimate of the spatial extent of benthic habitats potentially subject to cumulative risks of alteration, based on the indices of exposure to hydrographic pressures generated by human activities. Thus, 3% of the area of "Coastal circalittoral coarse sediment" habitat appears to be at high risk and 38% at medium risk.
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017), the D7C2 assessment must be carried out for each habitat type that is affected by changing hydrographic conditions and the D7C2 results are not integrated. On the other hand, no threshold has been defined so far for the parameter "Extent" and therefore the status of D7C2 is not reported, but the assessment of D7C2 has provided a first estimate of the spatial extent of benthic habitats potentially subject to cumulative risks of alteration, based on the indices of exposure to hydrographic pressures generated by human activities. Thus, the "Coastal Circumvalittoral Mud" habitat presents a large area at high risk (16% of the total habitat area), and a larger area at medium risk (29% of the MRU).
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017), the D7C2 assessment must be carried out for each habitat type that is affected by changing hydrographic conditions and the D7C2 results are not integrated. On the other hand, no threshold has been defined so far for the parameter "Extent" and therefore the status of D7C2 is not reported, but the assessment of D7C2 has provided a first estimate of the spatial extent of benthic habitats potentially subject to cumulative risks of alteration, based on the indices of exposure to hydrographic pressures generated by human activities. Thus, 2% of the surface area of the "Coastal circalittoral biogenic rocks and reefs" habitat appears to be at high risk and 48% at medium risk.
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017), the D7C2 assessment must be carried out for each habitat type that is affected by changing hydrographic conditions and the D7C2 results are not integrated. On the other hand, no threshold has been defined so far for the parameter "Extent" and therefore the status of D7C2 is not reported, but the assessment of D7C2 has provided a first estimate of the spatial extent of benthic habitats potentially subject to cumulative risks of alteration, based on the indices of exposure to hydrographic pressures generated by human activities. Thus, 3% of the area of "Coastal circalittoral sands" habitat appears to be at high risk and 68% at medium risk.
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017), the D7C2 assessment must be carried out for each habitat type that is affected by changing hydrographic conditions and the D7C2 results are not integrated. On the other hand, no threshold has been defined so far for the parameter "Extent" and therefore the status of D7C2 is not reported, but the assessment of D7C2 has provided a first estimate of the spatial extent of benthic habitats potentially subject to cumulative risks of alteration, based on the indices of exposure to hydrographic pressures generated by human activities. Thus, "Subtidal coarse sediment" habitat presents one of the largest areas at high risk (29% of the total habitat area), and a larger area at medium risk (57% of the MRU).
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017), the D7C2 assessment must be carried out for each habitat type that is affected by changing hydrographic conditions and the D7C2 results are not integrated. On the other hand, no threshold has been defined so far for the parameter "Extent" and therefore the status of D7C2 is not reported, but the assessment of D7C2 has provided a first estimate of the spatial extent of benthic habitats potentially subject to cumulative risks of alteration, based on the indices of exposure to hydrographic pressures generated by human activities. Thus, the " infralittoral mud " habitat presents the largest area at high risk (36% of the total habitat area), and 28% of the MRU at medium risk.
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017), the D7C2 assessment must be carried out for each habitat type that is affected by changing hydrographic conditions and the D7C2 results are not integrated. On the other hand, no threshold has been defined so far for the parameter "Extent" and therefore the status of D7C2 is not reported, but the assessment of D7C2 has provided a first estimate of the spatial extent of benthic habitats potentially subject to cumulative risks of alteration, based on the indices of exposure to hydrographic pressures generated by human activities. Thus, the " infralittoral biogenic rocks and reefs " habitat presents one of the largest areas at high risk (31% of the total habitat area), and a larger area at medium risk (56% of the MRU).
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017), the D7C2 assessment must be carried out for each habitat type that is affected by changing hydrographic conditions and the D7C2 results are not integrated. On the other hand, no threshold has been defined so far for the parameter "Extent" and therefore the status of D7C2 is not reported, but the assessment of D7C2 has provided a first estimate of the spatial extent of benthic habitats potentially subject to cumulative risks of alteration, based on the indices of exposure to hydrographic pressures generated by human activities. Thus, the " infralittoral sands " habitat presents a large area at high risk (20% of the total habitat area), and a larger area at medium risk (69% of the MRU).
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017), the D7C2 assessment must be carried out for each habitat type that is affected by changing hydrographic conditions and the D7C2 results are not integrated. On the other hand, no threshold has been defined so far for the parameter "Extent" and therefore the status of D7C2 is not reported, but the assessment of D7C2 has provided a first estimate of the spatial extent of benthic habitats potentially subject to cumulative risks of alteration, based on the indices of exposure to hydrographic pressures generated by human activities. Thus, the "offshore circalittoral mud flats" habitat presents a large area at high risk (16.5% of the total habitat area) and the same area at medium risk (16.5% of the MRU).
Element status
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Description element
The assessment of criterion D7C1 contributes to the assessment of criterion D7C2. Thus, the accumulation of quantified pressures (i.e., exposure indices) under D7C1 is incorporated into the calculation of the risk of modification of each habitat for the D7C2 assessment.
The assessment of criterion D7C1 contributes to the assessment of criterion D7C2. Thus, the accumulation of quantified pressures (i.e., exposure indices) under D7C1 is incorporated into the calculation of the risk of modification of each habitat for the D7C2 assessment.
The assessment of criterion D7C1 contributes to the assessment of criterion D7C2. Thus, the accumulation of quantified pressures (i.e., exposure indices) under D7C1 is incorporated into the calculation of the risk of modification of each habitat for the D7C2 assessment.
The assessment of criterion D7C1 contributes to the assessment of criterion D7C2. Thus, the accumulation of quantified pressures (i.e., exposure indices) under D7C1 is incorporated into the calculation of the risk of modification of each habitat for the D7C2 assessment.
The assessment of criterion D7C1 contributes to the assessment of criterion D7C2. Thus, the accumulation of quantified pressures (i.e., exposure indices) under D7C1 is incorporated into the calculation of the risk of modification of each habitat for the D7C2 assessment.
The assessment of criterion D7C1 contributes to the assessment of criterion D7C2. Thus, the accumulation of quantified pressures (i.e., exposure indices) under D7C1 is incorporated into the calculation of the risk of modification of each habitat for the D7C2 assessment.
The assessment of criterion D7C1 contributes to the assessment of criterion D7C2. Thus, the accumulation of quantified pressures (i.e., exposure indices) under D7C1 is incorporated into the calculation of the risk of modification of each habitat for the D7C2 assessment.
In the absence of a threshold for the "Extent" parameter, the state of the habitat could not be provided. Furthermore, according to Decision 2017/848/EU, the results of the assessment of criterion D7C2 (estimated extent of adverse effects by habitat type in each assessment area) are used for the assessment of criterion D6C5. However, in the absence of an operational indicator at the level of Descriptor 6 - Benthic Habitats, these results could not be taken into account in the assessment of D6C5.
In the absence of a threshold for the "Extent" parameter, the state of the habitat could not be provided. Furthermore, according to Decision 2017/848/EU, the results of the assessment of criterion D7C2 (estimated extent of adverse effects by habitat type in each assessment area) are used for the assessment of criterion D6C5. However, in the absence of an operational indicator at the level of Descriptor 6 - Benthic Habitats, these results could not be taken into account in the assessment of D6C5.
In the absence of a threshold for the "Extent" parameter, the state of the habitat could not be provided. Furthermore, according to Decision 2017/848/EU, the results of the assessment of criterion D7C2 (estimated extent of adverse effects by habitat type in each assessment area) are used for the assessment of criterion D6C5. However, in the absence of an operational indicator at the level of Descriptor 6 - Benthic Habitats, these results could not be taken into account in the assessment of D6C5.
In the absence of a threshold for the "Extent" parameter, the state of the habitat could not be provided. Furthermore, according to Decision 2017/848/EU, the results of the assessment of criterion D7C2 (estimated extent of adverse effects by habitat type in each assessment area) are used for the assessment of criterion D6C5. However, in the absence of an operational indicator at the level of Descriptor 6 - Benthic Habitats, these results could not be taken into account in the assessment of D6C5.
In the absence of a threshold for the "Extent" parameter, the state of the habitat could not be provided. Furthermore, according to Decision 2017/848/EU, the results of the assessment of criterion D7C2 (estimated extent of adverse effects by habitat type in each assessment area) are used for the assessment of criterion D6C5. However, in the absence of an operational indicator at the level of Descriptor 6 - Benthic Habitats, these results could not be taken into account in the assessment of D6C5.
In the absence of a threshold for the "Extent" parameter, the state of the habitat could not be provided. Furthermore, according to Decision 2017/848/EU, the results of the assessment of criterion D7C2 (estimated extent of adverse effects by habitat type in each assessment area) are used for the assessment of criterion D6C5. However, in the absence of an operational indicator at the level of Descriptor 6 - Benthic Habitats, these results could not be taken into account in the assessment of D6C5.
In the absence of a threshold for the "Extent" parameter, the state of the habitat could not be provided. Furthermore, according to Decision 2017/848/EU, the results of the assessment of criterion D7C2 (estimated extent of adverse effects by habitat type in each assessment area) are used for the assessment of criterion D6C5. However, in the absence of an operational indicator at the level of Descriptor 6 - Benthic Habitats, these results could not be taken into account in the assessment of D6C5.
In the absence of a threshold for the "Extent" parameter, the state of the habitat could not be provided. Furthermore, according to Decision 2017/848/EU, the results of the assessment of criterion D7C2 (estimated extent of adverse effects by habitat type in each assessment area) are used for the assessment of criterion D6C5. However, in the absence of an operational indicator at the level of Descriptor 6 - Benthic Habitats, these results could not be taken into account in the assessment of D6C5.
In the absence of a threshold for the "Extent" parameter, the state of the habitat could not be provided. Furthermore, according to Decision 2017/848/EU, the results of the assessment of criterion D7C2 (estimated extent of adverse effects by habitat type in each assessment area) are used for the assessment of criterion D6C5. However, in the absence of an operational indicator at the level of Descriptor 6 - Benthic Habitats, these results could not be taken into account in the assessment of D6C5.
Integration rule type parameter
Not relevant
Not relevant
Not relevant
Not relevant
Not relevant
Not relevant
Not relevant
Not relevant
Not relevant
Not relevant
Not relevant
Not relevant
Not relevant
Not relevant
Not relevant
Not relevant
Integration rule description parameter
Integration rule type criteria
Not relevant
Not relevant
Not relevant
Not relevant
Not relevant
Not relevant
Not relevant
Not relevant
Not relevant
Not relevant
Not relevant
Not relevant
Not relevant
Not relevant
Not relevant
Not relevant
Integration rule description criteria
GES extent threshold
GES extent achieved
GES extent unit
GES achieved
Not relevant
Not relevant
Not relevant
Not relevant
Not relevant
Not relevant
Not relevant
Not relevant
Not relevant
Not relevant
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Description overall status
The assessment of D7, based on data on anthropogenic activities, has highlighted significant variations in exposure to pressures:1/ The coastal zone is the most subject to exposure to the hydrographic pressures considered.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (53% of the southern subdivision of the Bay of Biscay marine sub-region). However, the exposure index remains mostly low, and for 90% of the major benthic habitat types, the area of habitat potentially at risk of moderate to high modification is greater than 30% of the total habitat area, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
The assessment of D7, based on data on anthropogenic activities, has highlighted significant variations in exposure to pressures:1/ The coastal zone is the most subject to exposure to the hydrographic pressures considered.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (53% of the southern subdivision of the Bay of Biscay marine sub-region). However, the exposure index remains mostly low, and for 90% of the major benthic habitat types, the area of habitat potentially at risk of moderate to high modification is greater than 30% of the total habitat area, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
The assessment of D7, based on data on anthropogenic activities, has highlighted significant variations in exposure to pressures:1/ The coastal zone is the most subject to exposure to the hydrographic pressures considered.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (53% of the southern subdivision of the Bay of Biscay marine sub-region). However, the exposure index remains mostly low, and for 90% of the major benthic habitat types, the area of habitat potentially at risk of moderate to high modification is greater than 30% of the total habitat area, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
The assessment of D7, based on data on anthropogenic activities, has highlighted significant variations in exposure to pressures:1/ The coastal zone is the most subject to exposure to the hydrographic pressures considered.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (53% of the southern subdivision of the Bay of Biscay marine sub-region). However, the exposure index remains mostly low, and for 90% of the major benthic habitat types, the area of habitat potentially at risk of moderate to high modification is greater than 30% of the total habitat area, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
The assessment of D7, based on data on anthropogenic activities, has highlighted significant variations in exposure to pressures:1/ The coastal zone is the most subject to exposure to the hydrographic pressures considered.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (53% of the southern subdivision of the Bay of Biscay marine sub-region). However, the exposure index remains mostly low, and for 90% of the major benthic habitat types, the area of habitat potentially at risk of moderate to high modification is greater than 30% of the total habitat area, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
The assessment of D7, based on data on anthropogenic activities, has highlighted significant variations in exposure to pressures:1/ The coastal zone is the most subject to exposure to the hydrographic pressures considered.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (53% of the southern subdivision of the Bay of Biscay marine sub-region). However, the exposure index remains mostly low, and for 90% of the major benthic habitat types, the area of habitat potentially at risk of moderate to high modification is greater than 30% of the total habitat area, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
The assessment of D7, based on data on anthropogenic activities, has highlighted significant variations in exposure to pressures:1/ The coastal zone is the most subject to exposure to the hydrographic pressures considered.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (53% of the southern subdivision of the Bay of Biscay marine sub-region). However, the exposure index remains mostly low, and for 90% of the major benthic habitat types, the area of habitat potentially at risk of moderate to high modification is greater than 30% of the total habitat area, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
The assessment of D7, based on data on anthropogenic activities, has highlighted significant variations in exposure to pressures:1/ The coastal zone is the most subject to exposure to the hydrographic pressures considered.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (53% of the southern subdivision of the Bay of Biscay marine sub-region). However, the exposure index remains mostly low, and for 90% of the major benthic habitat types, the area of habitat potentially at risk of moderate to high modification is greater than 30% of the total habitat area, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
The assessment of D7, based on data on anthropogenic activities, has highlighted significant variations in exposure to pressures:1/ The coastal zone is the most subject to exposure to the hydrographic pressures considered.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (53% of the southern subdivision of the Bay of Biscay marine sub-region). However, the exposure index remains mostly low, and for 90% of the major benthic habitat types, the area of habitat potentially at risk of moderate to high modification is greater than 30% of the total habitat area, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
The assessment of D7, based on data on anthropogenic activities, has highlighted significant variations in exposure to pressures:1/ The coastal zone is the most subject to exposure to the hydrographic pressures considered.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (53% of the southern subdivision of the Bay of Biscay marine sub-region). However, the exposure index remains mostly low, and for 90% of the major benthic habitat types, the area of habitat potentially at risk of moderate to high modification is greater than 30% of the total habitat area, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
The assessment of D7, based on data on anthropogenic activities, has highlighted significant variations in exposure to pressures:1/ The coastal zone is the most subject to exposure to the hydrographic pressures considered.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (53% of the southern subdivision of the Bay of Biscay marine sub-region). However, the exposure index remains mostly low, and for 90% of the major benthic habitat types, the area of habitat potentially at risk of moderate to high modification is greater than 30% of the total habitat area, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
The assessment of D7, based on data on anthropogenic activities, has highlighted significant variations in exposure to pressures:1/ The coastal zone is the most subject to exposure to the hydrographic pressures considered.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (53% of the southern subdivision of the Bay of Biscay marine sub-region). However, the exposure index remains mostly low, and for 90% of the major benthic habitat types, the area of habitat potentially at risk of moderate to high modification is greater than 30% of the total habitat area, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
The assessment of D7, based on data on anthropogenic activities, has highlighted significant variations in exposure to pressures:1/ The coastal zone is the most subject to exposure to the hydrographic pressures considered.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (53% of the southern subdivision of the Bay of Biscay marine sub-region). However, the exposure index remains mostly low, and for 90% of the major benthic habitat types, the area of habitat potentially at risk of moderate to high modification is greater than 30% of the total habitat area, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
The assessment of D7, based on data on anthropogenic activities, has highlighted significant variations in exposure to pressures:1/ The coastal zone is the most subject to exposure to the hydrographic pressures considered.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (53% of the southern subdivision of the Bay of Biscay marine sub-region). However, the exposure index remains mostly low, and for 90% of the major benthic habitat types, the area of habitat potentially at risk of moderate to high modification is greater than 30% of the total habitat area, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
The assessment of D7, based on data on anthropogenic activities, has highlighted significant variations in exposure to pressures:1/ The coastal zone is the most subject to exposure to the hydrographic pressures considered.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (53% of the southern subdivision of the Bay of Biscay marine sub-region). However, the exposure index remains mostly low, and for 90% of the major benthic habitat types, the area of habitat potentially at risk of moderate to high modification is greater than 30% of the total habitat area, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
The assessment of D7, based on data on anthropogenic activities, has highlighted significant variations in exposure to pressures:1/ The coastal zone is the most subject to exposure to the hydrographic pressures considered.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (53% of the southern subdivision of the Bay of Biscay marine sub-region). However, the exposure index remains mostly low, and for 90% of the major benthic habitat types, the area of habitat potentially at risk of moderate to high modification is greater than 30% of the total habitat area, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
Assessments period
2012-2018
2012-2018
2012-2018
2012-2018
2012-2018
2012-2018
2012-2018
2012-2018
2012-2018
2012-2018
2012-2018
2012-2018
2012-2018
2012-2018
2012-2018
2012-2018
Related pressures
Related targets

Sud SRM GdG Z200 (ABI-FR-MS-GDG-SUD-Z200)

GES component
D7
D7
D7
D7
D7
D7
D7
D7
D7
D7
D7
D7
D7
D7
D7
D7
D7
D7
D7
D7
Feature
Hydrographical changes
Hydrographical changes
Hydrographical changes
Hydrographical changes
Hydrographical changes
Hydrographical changes
Hydrographical changes
Benthic broad habitats
Benthic broad habitats
Benthic broad habitats
Benthic broad habitats
Benthic broad habitats
Benthic broad habitats
Benthic broad habitats
Benthic broad habitats
Benthic broad habitats
Benthic broad habitats
Benthic broad habitats
Benthic broad habitats
Benthic broad habitats
Element
Changes in current regime
Changes in salinity regime
Changes in seabed substrate
Changes in thermal regime
Changes in tide regime
Changes in turbidity regime
Changes in waves regime
Circalittoral coarse sediment
Circalittoral mixed sediment
Circalittoral mud
Circalittoral rock and biogenic reef
Circalittoral sand
Infralittoral mud
Infralittoral rock and biogenic reef
Infralittoral sand
Offshore circalittoral coarse sediment
Offshore circalittoral mixed sediment
Offshore circalittoral mud
Offshore circalittoral rock and biogenic reef
Offshore circalittoral sand
Element code
ExpPresCurrents
ExpPresSalinity
ExpPresSeabedNature
ExpPresTemperature
ExpPresTide
ExpPresTurbidity
ExpPresWaves
HabBenCircalitCoarSed
HabBenCircalitMxdSed
HabBenCircalitMud
HabBenCircalitRock
HabBenCircalitSand
HabBenInfralitMud
HabBenInfralitRock
HabBenInfralitSand
HabBenOffshCoarSed
HabBenOffshMxdSed
HabBenOffshMud
HabBenOffshRock
HabBenOffshSand
Element code source
Link to other vocabulary or code lists that may be relevant
Link to other vocabulary or code lists that may be relevant
Link to other vocabulary or code lists that may be relevant
Link to other vocabulary or code lists that may be relevant
Link to other vocabulary or code lists that may be relevant
Link to other vocabulary or code lists that may be relevant
Link to other vocabulary or code lists that may be relevant
Habitats (D1-D6) http://dd.eionet.europa.eu/vocabulary/msfd/broadHabitatTypes/view
Habitats (D1-D6) http://dd.eionet.europa.eu/vocabulary/msfd/broadHabitatTypes/view
Habitats (D1-D6) http://dd.eionet.europa.eu/vocabulary/msfd/broadHabitatTypes/view
Habitats (D1-D6) http://dd.eionet.europa.eu/vocabulary/msfd/broadHabitatTypes/view
Habitats (D1-D6) http://dd.eionet.europa.eu/vocabulary/msfd/broadHabitatTypes/view
Habitats (D1-D6) http://dd.eionet.europa.eu/vocabulary/msfd/broadHabitatTypes/view
Habitats (D1-D6) http://dd.eionet.europa.eu/vocabulary/msfd/broadHabitatTypes/view
Habitats (D1-D6) http://dd.eionet.europa.eu/vocabulary/msfd/broadHabitatTypes/view
Habitats (D1-D6) http://dd.eionet.europa.eu/vocabulary/msfd/broadHabitatTypes/view
Habitats (D1-D6) http://dd.eionet.europa.eu/vocabulary/msfd/broadHabitatTypes/view
Habitats (D1-D6) http://dd.eionet.europa.eu/vocabulary/msfd/broadHabitatTypes/view
Habitats (D1-D6) http://dd.eionet.europa.eu/vocabulary/msfd/broadHabitatTypes/view
Habitats (D1-D6) http://dd.eionet.europa.eu/vocabulary/msfd/broadHabitatTypes/view
Element 2
Element 2 code
Element 2 code source
Element source
National
National
National
National
National
National
National
EU
EU
EU
EU
EU
EU
EU
EU
EU
EU
EU
EU
EU
Criterion
D7C1
D7C1
D7C1
D7C1
D7C1
D7C1
D7C1
D7C2
D7C2
D7C2
D7C2
D7C2
D7C2
D7C2
D7C2
D7C2
D7C2
D7C2
D7C2
D7C2
Parameter
Extent
Extent
Extent
Extent
Extent
Extent
Extent
Extent
Extent
Extent
Extent
Extent
Extent
Extent
Extent
Extent
Extent
Extent
Extent
Extent
Parameter other
Threshold value upper
Threshold value lower
Threshold qualitative
Not available yet
Not available yet
Not available yet
Not available yet
Not available yet
Not available yet
Not available yet
Not available yet
Not available yet
Not available yet
Not available yet
Not available yet
Not available yet
Not available yet
Not available yet
Not available yet
Not available yet
Not available yet
Not available yet
Not available yet
Threshold value source
Threshold value source other
Value achieved upper
Value achieved lower
Value unit
Value unit other
Proportion threshold value
Proportion value achieved
14.0
31400.0
10.0
7.0
31400.0
7.0
2322.0
1137.0
1621.0
433.0
5818.0
10.0
38.0
261.0
2040.0
618.0
3324.0
965.0
12765.0
Proportion threshold value unit
extent in km2 of pressure
extent in km2 of pressure
extent in km2 of pressure
extent in km2 of pressure
extent in km2 of pressure
extent in km2 of pressure
extent in km2 of pressure
extent in km2 of habitat adversely affected
extent in km2 of habitat adversely affected
extent in km2 of habitat adversely affected
extent in km2 of habitat adversely affected
extent in km2 of habitat adversely affected
extent in km2 of habitat adversely affected
extent in km2 of habitat adversely affected
extent in km2 of habitat adversely affected
extent in km2 of habitat adversely affected
extent in km2 of habitat adversely affected
extent in km2 of habitat adversely affected
extent in km2 of habitat adversely affected
extent in km2 of habitat adversely affected
Trend
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Parameter achieved
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Description parameter
The metric considered for this parameter is the area of exposure for each pressure considered (overall or as a function of the level of the exposure index). The areas potentially affected by a change in the current regime correspond to a total area of 14 km2 . The areas of exposure according to the four levels of exposure index are: No exposure: 31386 km² Low exposure index: 14 km² Medium exposure index: 0 km² High exposure index: 0 km² Note that no threshold is currently available to assess whether or not the parameter has been reached.
The metric considered for this parameter is the area of exposure for each pressure considered (overall or as a function of the level of the exposure index). The areas potentially affected by a change in salinity regime correspond to a total surface area of 0 km2 . The areas of exposure according to the four levels of the exposure index are No exposure: 31400 km² Low exposure index: 0 km² Medium exposure index: 0 km² High exposure index: 0 km² Note that no threshold is currently available to assess whether or not the parameter has been reached.
The metric considered for this parameter is the area of exposure for each pressure considered (overall or as a function of the level of the exposure index). The areas potentially affected by a change in the background nature correspond to a total area of 31400 km2 . The areas of exposure according to the four levels of exposure index are: No exposure: 0 km².Low exposure index: 0 km².Medium exposure index: 31400 km².High exposure index: 0 km².Note that no threshold is currently available to assess whether or not the parameter has been reached.
The metric considered for this parameter is the area of exposure for each pressure considered (overall or as a function of the level of the exposure index). The areas potentially affected by a change in the thermal regime correspond to a total surface area of <10 km2 . The areas of exposure according to the four levels of the exposure index are No exposure: 31400 km² Low exposure index: <10 km² Medium exposure index: 0 km² High exposure index: 0 km² Note that no threshold is currently available to assess whether or not the parameter has been reached.
The metric considered for this parameter is the area of exposure for each pressure considered (overall or as a function of the level of the exposure index). The areas potentially affected by a change in the tidal regime correspond to a total area of 7 km2 , based on the four levels of exposure index: No exposure: 31393 km² Low exposure index: 7 km² Medium exposure index: 0 km² High exposure index: 0 km² Note that no threshold is currently available to assess whether or not the parameter has been reached.
The metric considered for this parameter is the area of exposure for each pressure considered (overall or as a function of the level of the exposure index). The areas potentially affected by a change in the turbidity regime correspond to a total area of 31400 km2 . The areas of exposure according to the four levels of exposure index are: No exposure: 0 km².Low exposure index: 31249 km².Medium exposure index: 151 km².High exposure index: 0 km².Note that no threshold is currently available to assess whether or not the parameter has been reached.
The metric considered for this parameter is the area of exposure for each pressure considered (overall or as a function of the level of the exposure index). The areas potentially affected by a change in the wave regime correspond to a total area of 7 km2 . The areas of exposure according to the four levels of exposure index are: No Exposure: 31393 km² Low Exposure Index: 7 km² Medium Exposure Index: 0 km² High Exposure Index: 0 km² Note that no threshold is currently available to assess whether or not the parameter has been reached.
The metric considered for this parameter is the area of habitat potentially at risk (overall or as a function of the level of risk). The spatial extent of potential habitat modification related to permanent changes in hydrographic conditions in this MRU is 2322 km2 (i.e., 100% of the assessed habitat). Furthermore, the indicator makes it possible to assess the intensity of the risk of modification: negligible or nil risk of modification: 0 km², low risk of modification: 227 km², medium risk of modification: 2095 km², high risk of modification: 0 km², it should be noted that no threshold is currently available to assess whether or not the parameter has been reached.
The metric considered for this parameter is the area of habitat potentially at risk (overall or based on the level of risk). The spatial extent of potential habitat modification related to permanent changes in hydrographic conditions in this MRU is 1137 km2 (i.e. 100% of the assessed habitat). Furthermore, the indicator makes it possible to assess the intensity of the risk of modification: negligible or no risk of modification: 0 km², low risk of modification: 96 km², medium risk of modification: 1041 km², high risk of modification: 0 km², it should be noted that no threshold is currently available to assess whether or not the parameter has been reached.
The metric considered for this parameter is the area of habitat potentially at risk (overall or as a function of the level of risk). The spatial extent of potential habitat modification related to permanent changes in hydrographic conditions in this MRU is 1621 km2 (i.e. 100% of the habitat assessed). Furthermore, the indicator makes it possible to assess the intensity of the risk of modification: negligible or no risk of modification: 0 km², low risk of modification: 107 km², medium risk of modification: 1515 km², high risk of modification: 0 km², it should be noted that no threshold is currently available to assess whether or not the parameter has been reached.
The metric considered for this parameter is the area of habitat potentially at risk (overall or as a function of the level of risk). The spatial extent of potential habitat modification related to permanent changes in hydrographic conditions in this MRU is 433 km2 (i.e. 100% of the habitat assessed). Furthermore, the indicator makes it possible to assess the intensity of the risk of modification: negligible or no risk of modification: 0 km², low risk of modification: 113 km², medium risk of modification: 319 km², high risk of modification: 0 km², it should be noted that no threshold is currently available to assess whether or not the parameter has been reached.
The metric considered for this parameter is the area of habitat potentially at risk (overall or as a function of the level of risk). The spatial extent of potential habitat modification related to permanent changes in hydrographic conditions in this MRU is 5818 km2 (i.e. 100% of the habitat assessed). Furthermore, the indicator makes it possible to assess the intensity of the risk of modification: negligible or nil risk of modification: 0 km², low risk of modification: 323 km², medium risk of modification: 5495 km², high risk of modification: 0 km², it should be noted that no threshold is currently available to assess whether or not the parameter has been reached.
The metric considered for this parameter is the area of habitat potentially at risk (overall or as a function of the level of risk). The spatial extent of potential habitat modification related to permanent changes in hydrographic conditions in this MRU is 10 km2 (i.e. 100% of the habitat assessed). Furthermore, the indicator makes it possible to assess the intensity of the risk of modification: negligible or nil risk of modification: 0 km², low risk of modification: 10 km², medium risk of modification: 0 km², high risk of modification: 0 km², and no threshold is currently available to assess whether or not the parameter has been reached.
The metric considered for this parameter is the area of habitat potentially at risk (overall or based on the level of risk). The spatial extent of potential habitat alteration associated with permanent changes in hydrographic conditions in this MRU is 38 km2 (i.e., 100% of the assessed habitat). In addition, the indicator makes it possible to assess the intensity of the risk of modification: negligible or nil risk of modification: 0 km², low risk of modification: 14 km², medium risk of modification: 24 km², high risk of modification: 0 km², it should be noted that no threshold is currently available to assess whether or not the parameter has been reached.
The metric considered for this parameter is the area of habitat potentially at risk (overall or as a function of the level of risk). The spatial extent of potential habitat modification related to permanent changes in hydrographic conditions in this MRU is 261 km2 (i.e. 100% of the habitat assessed). Furthermore, the indicator makes it possible to assess the intensity of the risk of modification: negligible or no risk of modification: 0 km², low risk of modification: 21 km², medium risk of modification: 240 km², high risk of modification: 0 km², it should be noted that no threshold is currently available to assess whether or not the parameter has been reached.
The metric considered for this parameter is the area of habitat potentially at risk (overall or as a function of the level of risk). The spatial extent of potential habitat modification related to permanent changes in hydrographic conditions in this MRU is 2040 km2 (i.e., 100% of the assessed habitat). Furthermore, the indicator makes it possible to assess the intensity of the risk of modification: negligible or nil risk of modification: 0 km², low risk of modification: 745 km², medium risk of modification: 1295 km², high risk of modification: 0 km², it should be noted that no threshold is currently available to assess whether or not the parameter has been reached.
The metric considered for this parameter is the area of habitat potentially at risk (overall or as a function of the level of risk). The spatial extent of potential habitat modification related to permanent changes in hydrographic conditions in this MRU is 618 km2 (i.e. 100% of the habitat assessed). Furthermore, the indicator makes it possible to assess the intensity of the risk of modification: negligible or nil risk of modification: 0 km², low risk of modification: 130 km², medium risk of modification: 488 km², high risk of modification: 0 km², it should be noted that no threshold is currently available to assess whether or not the parameter has been reached.
The metric considered for this parameter is the area of habitat potentially at risk (overall or as a function of the level of risk). The spatial extent of potential habitat modification related to permanent changes in hydrographic conditions in this MRU is 3324 km2 (i.e. 100% of the habitat assessed). Furthermore, the indicator makes it possible to assess the intensity of the risk of modification: negligible or nil risk of modification: 0 km², low risk of modification: 735 km², medium risk of modification: 2589 km², high risk of modification: 0 km², it should be noted that no threshold is currently available to assess whether or not the parameter has been reached.
The metric considered for this parameter is the area of habitat potentially at risk (overall or as a function of the level of risk). The spatial extent of potential habitat modification related to permanent changes in hydrographic conditions in this MRU is 965 km2 (i.e. 100% of the habitat assessed). Furthermore, the indicator makes it possible to assess the intensity of the risk of modification: negligible or nil risk of modification: 0 km², low risk of modification: 893 km², medium risk of modification: 72 km², high risk of modification: 0 km², it should be noted that no threshold is currently available to assess whether or not the parameter has been reached.
The metric considered for this parameter is the area of habitat potentially at risk (overall or as a function of the level of risk). The spatial extent of potential habitat modification related to permanent changes in hydrographic conditions in this MRU is 12765 km2 (i.e. 100% of the assessed habitat). Furthermore, the indicator makes it possible to assess the intensity of the risk of modification: negligible or nil risk of modification: 0 km², low risk of modification: 5615 km², medium risk of modification: 7150 km², high risk of modification: 0 km², it should be noted that no threshold is currently available to assess whether or not the parameter has been reached.
Related indicator
Criteria status
Contributes to assessment of another criterion/ele
Contributes to assessment of another criterion/ele
Contributes to assessment of another criterion/ele
Contributes to assessment of another criterion/ele
Contributes to assessment of another criterion/ele
Contributes to assessment of another criterion/ele
Contributes to assessment of another criterion/ele
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Description criteria
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017) no threshold is to be specified for D7C1: the status of the D7C1 criterion is therefore not reported. However, the assessment of the D7C1 criterion has provided a first estimate of the exposure indices for spatial areas potentially affected by a change in current, tidal, wave, bottom nature, turbidity, thermal and salinity regimes. Indeed, the results show that the pressures linked to a change in the current, tidal and wave regime are relatively low (< 1% of the southern subdivision of the Bay of Biscay marine sub-region). and fairly localised since it is located almost exclusively in the coastal zone. They represent less than 1% of the area of this MRU. It should also be noted that the exposure indices calculated for these pressures are mostly low. Pressures linked to a change in the nature of the bottom and the turbidity regime potentially affect a very large area (100% of the MRU). The exposure indices calculated for the change in background are exclusively low (100% of the MRU), and mostly low for the change in turbidity regime (>99% of the MRU). Finally, pressures related to a change in thermal and salinity regime affect less than 1% of the MRU.
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017) no threshold is to be specified for D7C1: the status of the D7C1 criterion is therefore not reported. However, the assessment of the D7C1 criterion has provided a first estimate of the exposure indices for spatial areas potentially affected by a change in current, tidal, wave, bottom nature, turbidity, thermal and salinity regimes. Indeed, the results show that the pressures linked to a change in the current, tidal and wave regime are relatively low (< 1% of the southern subdivision of the Bay of Biscay marine sub-region). and fairly localised since it is located almost exclusively in the coastal zone. They represent less than 1% of the area of this MRU. It should also be noted that the exposure indices calculated for these pressures are mostly low. Pressures linked to a change in the nature of the bottom and the turbidity regime potentially affect a very large area (100% of the MRU). The exposure indices calculated for the change in background are exclusively low (100% of the MRU), and mostly low for the change in turbidity regime (>99% of the MRU). Finally, pressures related to a change in thermal and salinity regime affect less than 1% of the MRU.
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017) no threshold is to be specified for D7C1: the status of the D7C1 criterion is therefore not reported. However, the assessment of the D7C1 criterion has provided a first estimate of the exposure indices for spatial areas potentially affected by a change in current, tidal, wave, bottom nature, turbidity, thermal and salinity regimes. Indeed, the results show that the pressures linked to a change in the current, tidal and wave regime are relatively low (< 1% of the southern subdivision of the Bay of Biscay marine sub-region). and fairly localised since it is located almost exclusively in the coastal zone. They represent less than 1% of the area of this MRU. It should also be noted that the exposure indices calculated for these pressures are mostly low. Pressures linked to a change in the nature of the bottom and the turbidity regime potentially affect a very large area (100% of the MRU). The exposure indices calculated for the change in background are exclusively low (100% of the MRU), and mostly low for the change in turbidity regime (>99% of the MRU). Finally, pressures related to a change in thermal and salinity regime affect less than 1% of the MRU.
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017) no threshold is to be specified for D7C1: the status of the D7C1 criterion is therefore not reported. However, the assessment of the D7C1 criterion has provided a first estimate of the exposure indices for spatial areas potentially affected by a change in current, tidal, wave, bottom nature, turbidity, thermal and salinity regimes. Indeed, the results show that the pressures linked to a change in the current, tidal and wave regime are relatively low (< 1% of the southern subdivision of the Bay of Biscay marine sub-region). and fairly localised since it is located almost exclusively in the coastal zone. They represent less than 1% of the area of this MRU. It should also be noted that the exposure indices calculated for these pressures are mostly low. Pressures linked to a change in the nature of the bottom and the turbidity regime potentially affect a very large area (100% of the MRU). The exposure indices calculated for the change in background are exclusively low (100% of the MRU), and mostly low for the change in turbidity regime (>99% of the MRU). Finally, pressures related to a change in thermal and salinity regime affect less than 1% of the MRU.
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017) no threshold is to be specified for D7C1: the status of the D7C1 criterion is therefore not reported. However, the assessment of the D7C1 criterion has provided a first estimate of the exposure indices for spatial areas potentially affected by a change in current, tidal, wave, bottom nature, turbidity, thermal and salinity regimes. Indeed, the results show that the pressures linked to a change in the current, tidal and wave regime are relatively low (< 1% of the southern subdivision of the Bay of Biscay marine sub-region). and fairly localised since it is located almost exclusively in the coastal zone. They represent less than 1% of the area of this MRU. It should also be noted that the exposure indices calculated for these pressures are mostly low. Pressures linked to a change in the nature of the bottom and the turbidity regime potentially affect a very large area (100% of the MRU). The exposure indices calculated for the change in background are exclusively low (100% of the MRU), and mostly low for the change in turbidity regime (>99% of the MRU). Finally, pressures related to a change in thermal and salinity regime affect less than 1% of the MRU.
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017) no threshold is to be specified for D7C1: the status of the D7C1 criterion is therefore not reported. However, the assessment of the D7C1 criterion has provided a first estimate of the exposure indices for spatial areas potentially affected by a change in current, tidal, wave, bottom nature, turbidity, thermal and salinity regimes. Indeed, the results show that the pressures linked to a change in the current, tidal and wave regime are relatively low (< 1% of the southern subdivision of the Bay of Biscay marine sub-region). and fairly localised since it is located almost exclusively in the coastal zone. They represent less than 1% of the area of this MRU. It should also be noted that the exposure indices calculated for these pressures are mostly low. Pressures linked to a change in the nature of the bottom and the turbidity regime potentially affect a very large area (100% of the MRU). The exposure indices calculated for the change in background are exclusively low (100% of the MRU), and mostly low for the change in turbidity regime (>99% of the MRU). Finally, pressures related to a change in thermal and salinity regime affect less than 1% of the MRU.
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017) no threshold is to be specified for D7C1: the status of the D7C1 criterion is therefore not reported. However, the assessment of the D7C1 criterion has provided a first estimate of the exposure indices for spatial areas potentially affected by a change in current, tidal, wave, bottom nature, turbidity, thermal and salinity regimes. Indeed, the results show that the pressures linked to a change in the current, tidal and wave regime are relatively low (< 1% of the southern subdivision of the Bay of Biscay marine sub-region). and fairly localised since it is located almost exclusively in the coastal zone. They represent less than 1% of the area of this MRU. It should also be noted that the exposure indices calculated for these pressures are mostly low. Pressures linked to a change in the nature of the bottom and the turbidity regime potentially affect a very large area (100% of the MRU). The exposure indices calculated for the change in background are exclusively low (100% of the MRU), and mostly low for the change in turbidity regime (>99% of the MRU). Finally, pressures related to a change in thermal and salinity regime affect less than 1% of the MRU.
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017), the D7C2 assessment must be carried out for each habitat type that is affected by changing hydrographic conditions and the D7C2 results are not integrated. On the other hand, no threshold has been defined so far for the parameter "Extent" and therefore the status of D7C2 is not reported, but the assessment of D7C2 has provided a first estimate of the spatial extent of benthic habitats potentially subject to cumulative risks of alteration, based on the indices of exposure to hydrographic pressures generated by human activities. Thus, the "Coastal circalittoral coarse sediment" habitat presents a large area at medium risk (90% of the total habitat area), and the remainder is at low risk (10% of the RMU).
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017), the D7C2 assessment must be carried out for each habitat type that is affected by changing hydrographic conditions and the D7C2 results are not integrated. On the other hand, no threshold has been defined so far for the parameter "Extent" and therefore the status of D7C2 is not reported, but the assessment of D7C2 has provided a first estimate of the spatial extent of benthic habitats potentially subject to cumulative risks of alteration, based on the indices of exposure to hydrographic pressures generated by human activities. Thus, the "Coastal circalittoral mixed sediment" habitat presents a large area subject to a medium risk (92% of the total habitat area), and the rest is subject to a low risk (8% of the RMU).
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017), the D7C2 assessment must be carried out for each habitat type that is affected by changing hydrographic conditions and the D7C2 results are not integrated. On the other hand, no threshold has been defined so far for the parameter "Extent" and therefore the status of D7C2 is not reported, but the assessment of D7C2 has provided a first estimate of the spatial extent of benthic habitats potentially subject to cumulative risks of alteration, based on the indices of exposure to hydrographic pressures generated by human activities. Thus, the "Coastal Circumvalittoral Mudflats" habitat presents a large area at medium risk (93% of the total habitat area), and the rest is at low risk (7% of the MRU).
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017), the D7C2 assessment must be carried out for each habitat type that is affected by changing hydrographic conditions and the D7C2 results are not integrated. On the other hand, no threshold has been defined so far for the parameter "Extent" and therefore the status of D7C2 is not reported, but the assessment of D7C2 has provided a first estimate of the spatial extent of benthic habitats potentially subject to cumulative risks of alteration, based on the indices of exposure to hydrographic pressures generated by human activities. Thus, the "Coastal circalittoral biogenic rocks and reefs" habitat presents a large area at medium risk (74% of the total habitat area), and the rest is at low risk (26% of the MRU).
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017), the D7C2 assessment must be carried out for each habitat type that is affected by changing hydrographic conditions and the D7C2 results are not integrated. On the other hand, no threshold has been defined so far for the parameter "Extent" and therefore the status of D7C2 is not reported, but the assessment of D7C2 has provided a first estimate of the spatial extent of benthic habitats potentially subject to cumulative risks of alteration, based on the indices of exposure to hydrographic pressures generated by human activities. Thus, the "Coastal circalittoral sands" habitat presents a large area at medium risk (94% of the total habitat area), and the remainder is at low risk (6% of the MRU).
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017), the D7C2 assessment must be carried out for each habitat type that is affected by changing hydrographic conditions and the D7C2 results are not integrated. On the other hand, no threshold has been defined so far for the parameter "Extent" and therefore the status of D7C2 is not reported, but the assessment of D7C2 has provided a first estimate of the spatial extent of benthic habitats potentially subject to cumulative risks of alteration, based on the indices of exposure to hydrographic pressures generated by human activities. Thus, the " infralittoral mud " habitat is entirely subject to a low risk (100% of the total habitat area).
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017), the D7C2 assessment must be carried out for each habitat type that is affected by changing hydrographic conditions and the D7C2 results are not integrated. On the other hand, no threshold has been defined so far for the parameter "Extent" and therefore the status of D7C2 is not reported, but the assessment of D7C2 has provided a first estimate of the spatial extent of benthic habitats potentially subject to cumulative risks of alteration, based on the indices of exposure to hydrographic pressures generated by human activities. Thus, the " infralittoral biogenic rocks and reefs " habitat presents a large area subject to a medium risk (64% of the total habitat area).
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017), the D7C2 assessment must be carried out for each habitat type that is affected by changing hydrographic conditions and the D7C2 results are not integrated. On the other hand, no threshold has been defined so far for the parameter "Extent" and therefore the status of D7C2 is not reported, but the assessment of D7C2 has provided a first estimate of the spatial extent of benthic habitats potentially subject to cumulative risks of alteration, based on the indices of exposure to hydrographic pressures generated by human activities. Thus, the " infralittoral sands " habitat presents a large area subject to a medium risk (92% of the total habitat area).
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017), the D7C2 assessment must be carried out for each habitat type that is affected by changing hydrographic conditions and the D7C2 results are not integrated. On the other hand, no threshold has been defined so far for the parameter "Extent" and therefore the status of D7C2 is not reported, but the assessment of D7C2 has provided a first estimate of the spatial extent of benthic habitats potentially subject to cumulative risks of alteration, based on the indices of exposure to hydrographic pressures generated by human activities. Thus, 63% of the area of offshore circalittoral coarse sediment habitat appears to be at medium risk and 37% at low risk.
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017), the D7C2 assessment must be carried out for each habitat type that is affected by changing hydrographic conditions and the D7C2 results are not integrated. On the other hand, no threshold has been defined so far for the parameter "Extent" and therefore the status of D7C2 is not reported, but the assessment of D7C2 has provided a first estimate of the spatial extent of benthic habitats potentially subject to cumulative risks of alteration, based on the indices of exposure to hydrographic pressures generated by human activities. Thus, 79% of the area of " Mixed circalittoral offshore sediment " habitat appears to be subject to a medium risk and 21% to a low risk.
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017), the D7C2 assessment must be carried out for each habitat type that is affected by changing hydrographic conditions and the D7C2 results are not integrated. On the other hand, no threshold has been defined so far for the parameter "Extent" and therefore the status of D7C2 is not reported, but the assessment of D7C2 has provided a first estimate of the spatial extent of benthic habitats potentially subject to cumulative risks of alteration, based on the indices of exposure to hydrographic pressures generated by human activities. Thus, 78% of the area of "offshore circalittoral mud flats" habitat appears to be at medium risk and 22% at low risk.
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017), the D7C2 assessment must be carried out for each habitat type that is affected by changing hydrographic conditions and the D7C2 results are not integrated. On the other hand, no threshold has been defined so far for the parameter "Extent" and therefore the status of D7C2 is not reported, but the assessment of D7C2 has provided a first estimate of the spatial extent of benthic habitats potentially subject to cumulative risks of alteration, based on the indices of exposure to hydrographic pressures generated by human activities. Thus, 7% of the area of "offshore circalittoral biogenic rocks and reefs" habitat appears to be at medium risk and 93% at low risk.
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017), the D7C2 assessment must be carried out for each habitat type that is affected by changing hydrographic conditions and the D7C2 results are not integrated. On the other hand, no threshold has been defined so far for the parameter "Extent" and therefore the status of D7C2 is not reported, but the assessment of D7C2 has provided a first estimate of the spatial extent of benthic habitats potentially subject to cumulative risks of alteration, based on the indices of exposure to hydrographic pressures generated by human activities. Thus, 56% of the area of offshore circalittoral sands habitat appears to be at medium risk and 44% at low risk.
Element status
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Description element
The assessment of criterion D7C1 contributes to the assessment of criterion D7C2. Thus, the accumulation of quantified pressures (i.e., exposure indices) under D7C1 is incorporated into the calculation of the risk of modification of each habitat for the D7C2 assessment.
The assessment of criterion D7C1 contributes to the assessment of criterion D7C2. Thus, the accumulation of quantified pressures (i.e., exposure indices) under D7C1 is incorporated into the calculation of the risk of modification of each habitat for the D7C2 assessment.
The assessment of criterion D7C1 contributes to the assessment of criterion D7C2. Thus, the accumulation of quantified pressures (i.e., exposure indices) under D7C1 is incorporated into the calculation of the risk of modification of each habitat for the D7C2 assessment.
The assessment of criterion D7C1 contributes to the assessment of criterion D7C2. Thus, the accumulation of quantified pressures (i.e., exposure indices) under D7C1 is incorporated into the calculation of the risk of modification of each habitat for the D7C2 assessment.
The assessment of criterion D7C1 contributes to the assessment of criterion D7C2. Thus, the accumulation of quantified pressures (i.e., exposure indices) under D7C1 is incorporated into the calculation of the risk of modification of each habitat for the D7C2 assessment.
The assessment of criterion D7C1 contributes to the assessment of criterion D7C2. Thus, the accumulation of quantified pressures (i.e., exposure indices) under D7C1 is incorporated into the calculation of the risk of modification of each habitat for the D7C2 assessment.
The assessment of criterion D7C1 contributes to the assessment of criterion D7C2. Thus, the accumulation of quantified pressures (i.e., exposure indices) under D7C1 is incorporated into the calculation of the risk of modification of each habitat for the D7C2 assessment.
In the absence of a threshold for the "Extent" parameter, the state of the habitat could not be provided. Furthermore, according to Decision 2017/848/EU, the results of the assessment of criterion D7C2 (estimated extent of adverse effects by habitat type in each assessment area) are used for the assessment of criterion D6C5. However, in the absence of an operational indicator at the level of Descriptor 6 - Benthic Habitats, these results could not be taken into account in the assessment of D6C5.
In the absence of a threshold for the "Extent" parameter, the state of the habitat could not be provided. Furthermore, according to Decision 2017/848/EU, the results of the assessment of criterion D7C2 (estimated extent of adverse effects by habitat type in each assessment area) are used for the assessment of criterion D6C5. However, in the absence of an operational indicator at the level of Descriptor 6 - Benthic Habitats, these results could not be taken into account in the assessment of D6C5.
In the absence of a threshold for the "Extent" parameter, the state of the habitat could not be provided. Furthermore, according to Decision 2017/848/EU, the results of the assessment of criterion D7C2 (estimated extent of adverse effects by habitat type in each assessment area) are used for the assessment of criterion D6C5. However, in the absence of an operational indicator at the level of Descriptor 6 - Benthic Habitats, these results could not be taken into account in the assessment of D6C5.
In the absence of a threshold for the "Extent" parameter, the state of the habitat could not be provided. Furthermore, according to Decision 2017/848/EU, the results of the assessment of criterion D7C2 (estimated extent of adverse effects by habitat type in each assessment area) are used for the assessment of criterion D6C5. However, in the absence of an operational indicator at the level of Descriptor 6 - Benthic Habitats, these results could not be taken into account in the assessment of D6C5.
In the absence of a threshold for the "Extent" parameter, the state of the habitat could not be provided. Furthermore, according to Decision 2017/848/EU, the results of the assessment of criterion D7C2 (estimated extent of adverse effects by habitat type in each assessment area) are used for the assessment of criterion D6C5. However, in the absence of an operational indicator at the level of Descriptor 6 - Benthic Habitats, these results could not be taken into account in the assessment of D6C5.
In the absence of a threshold for the "Extent" parameter, the state of the habitat could not be provided. Furthermore, according to Decision 2017/848/EU, the results of the assessment of criterion D7C2 (estimated extent of adverse effects by habitat type in each assessment area) are used for the assessment of criterion D6C5. However, in the absence of an operational indicator at the level of Descriptor 6 - Benthic Habitats, these results could not be taken into account in the assessment of D6C5.
In the absence of a threshold for the "Extent" parameter, the state of the habitat could not be provided. Furthermore, according to Decision 2017/848/EU, the results of the assessment of criterion D7C2 (estimated extent of adverse effects by habitat type in each assessment area) are used for the assessment of criterion D6C5. However, in the absence of an operational indicator at the level of Descriptor 6 - Benthic Habitats, these results could not be taken into account in the assessment of D6C5.
In the absence of a threshold for the "Extent" parameter, the state of the habitat could not be provided. Furthermore, according to Decision 2017/848/EU, the results of the assessment of criterion D7C2 (estimated extent of adverse effects by habitat type in each assessment area) are used for the assessment of criterion D6C5. However, in the absence of an operational indicator at the level of Descriptor 6 - Benthic Habitats, these results could not be taken into account in the assessment of D6C5.
In the absence of a threshold for the "Extent" parameter, the state of the habitat could not be provided. Furthermore, according to Decision 2017/848/EU, the results of the assessment of criterion D7C2 (estimated extent of adverse effects by habitat type in each assessment area) are used for the assessment of criterion D6C5. However, in the absence of an operational indicator at the level of Descriptor 6 - Benthic Habitats, these results could not be taken into account in the assessment of D6C5.
In the absence of a threshold for the "Extent" parameter, the state of the habitat could not be provided. Furthermore, according to Decision 2017/848/EU, the results of the assessment of criterion D7C2 (estimated extent of adverse effects by habitat type in each assessment area) are used for the assessment of criterion D6C5. However, in the absence of an operational indicator at the level of Descriptor 6 - Benthic Habitats, these results could not be taken into account in the assessment of D6C5.
In the absence of a threshold for the "Extent" parameter, the state of the habitat could not be provided. Furthermore, according to Decision 2017/848/EU, the results of the assessment of criterion D7C2 (estimated extent of adverse effects by habitat type in each assessment area) are used for the assessment of criterion D6C5. However, in the absence of an operational indicator at the level of Descriptor 6 - Benthic Habitats, these results could not be taken into account in the assessment of D6C5.
In the absence of a threshold for the "Extent" parameter, the state of the habitat could not be provided. Furthermore, according to Decision 2017/848/EU, the results of the assessment of criterion D7C2 (estimated extent of adverse effects by habitat type in each assessment area) are used for the assessment of criterion D6C5. However, in the absence of an operational indicator at the level of Descriptor 6 - Benthic Habitats, these results could not be taken into account in the assessment of D6C5.
In the absence of a threshold for the "Extent" parameter, the state of the habitat could not be provided. Furthermore, according to Decision 2017/848/EU, the results of the assessment of criterion D7C2 (estimated extent of adverse effects by habitat type in each assessment area) are used for the assessment of criterion D6C5. However, in the absence of an operational indicator at the level of Descriptor 6 - Benthic Habitats, these results could not be taken into account in the assessment of D6C5.
Integration rule type parameter
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Integration rule description parameter
Integration rule type criteria
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Integration rule description criteria
GES extent threshold
GES extent achieved
GES extent unit
GES achieved
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Description overall status
The assessment of D7, based on data on anthropogenic activities, highlighted significant variations in exposure to pressures:1/ The Z200 zone is less subject than the coastal zone (MEC DCE) to exposure to the hydrographic pressures considered.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (53% of the southern subdivision of the Bay of Biscay marine sub-region). However, the exposure index remains mostly low, and for 90% of the major benthic habitat types, the area of habitat potentially at risk of moderate to high modification is greater than 30% of the total habitat area, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
The assessment of D7, based on data on anthropogenic activities, highlighted significant variations in exposure to pressures:1/ The Z200 zone is less subject than the coastal zone (MEC DCE) to exposure to the hydrographic pressures considered.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (53% of the southern subdivision of the Bay of Biscay marine sub-region). However, the exposure index remains mostly low, and for 90% of the major benthic habitat types, the area of habitat potentially at risk of moderate to high modification is greater than 30% of the total habitat area, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
The assessment of D7, based on data on anthropogenic activities, highlighted significant variations in exposure to pressures:1/ The Z200 zone is less subject than the coastal zone (MEC DCE) to exposure to the hydrographic pressures considered.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (53% of the southern subdivision of the Bay of Biscay marine sub-region). However, the exposure index remains mostly low, and for 90% of the major benthic habitat types, the area of habitat potentially at risk of moderate to high modification is greater than 30% of the total habitat area, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
The assessment of D7, based on data on anthropogenic activities, highlighted significant variations in exposure to pressures:1/ The Z200 zone is less subject than the coastal zone (MEC DCE) to exposure to the hydrographic pressures considered.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (53% of the southern subdivision of the Bay of Biscay marine sub-region). However, the exposure index remains mostly low, and for 90% of the major benthic habitat types, the area of habitat potentially at risk of moderate to high modification is greater than 30% of the total habitat area, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
The assessment of D7, based on data on anthropogenic activities, highlighted significant variations in exposure to pressures:1/ The Z200 zone is less subject than the coastal zone (MEC DCE) to exposure to the hydrographic pressures considered.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (53% of the southern subdivision of the Bay of Biscay marine sub-region). However, the exposure index remains mostly low, and for 90% of the major benthic habitat types, the area of habitat potentially at risk of moderate to high modification is greater than 30% of the total habitat area, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
The assessment of D7, based on data on anthropogenic activities, highlighted significant variations in exposure to pressures:1/ The Z200 zone is less subject than the coastal zone (MEC DCE) to exposure to the hydrographic pressures considered.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (53% of the southern subdivision of the Bay of Biscay marine sub-region). However, the exposure index remains mostly low, and for 90% of the major benthic habitat types, the area of habitat potentially at risk of moderate to high modification is greater than 30% of the total habitat area, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
The assessment of D7, based on data on anthropogenic activities, highlighted significant variations in exposure to pressures:1/ The Z200 zone is less subject than the coastal zone (MEC DCE) to exposure to the hydrographic pressures considered.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (53% of the southern subdivision of the Bay of Biscay marine sub-region). However, the exposure index remains mostly low, and for 90% of the major benthic habitat types, the area of habitat potentially at risk of moderate to high modification is greater than 30% of the total habitat area, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
The assessment of D7, based on data on anthropogenic activities, highlighted significant variations in exposure to pressures:1/ The Z200 zone is less subject than the coastal zone (MEC DCE) to exposure to the hydrographic pressures considered.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (53% of the southern subdivision of the Bay of Biscay marine sub-region). However, the exposure index remains mostly low, and for 90% of the major benthic habitat types, the area of habitat potentially at risk of moderate to high modification is greater than 30% of the total habitat area, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
The assessment of D7, based on data on anthropogenic activities, highlighted significant variations in exposure to pressures:1/ The Z200 zone is less subject than the coastal zone (MEC DCE) to exposure to the hydrographic pressures considered.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (53% of the southern subdivision of the Bay of Biscay marine sub-region). However, the exposure index remains mostly low, and for 90% of the major benthic habitat types, the area of habitat potentially at risk of moderate to high modification is greater than 30% of the total habitat area, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
The assessment of D7, based on data on anthropogenic activities, highlighted significant variations in exposure to pressures:1/ The Z200 zone is less subject than the coastal zone (MEC DCE) to exposure to the hydrographic pressures considered.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (53% of the southern subdivision of the Bay of Biscay marine sub-region). However, the exposure index remains mostly low, and for 90% of the major benthic habitat types, the area of habitat potentially at risk of moderate to high modification is greater than 30% of the total habitat area, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
The assessment of D7, based on data on anthropogenic activities, highlighted significant variations in exposure to pressures:1/ The Z200 zone is less subject than the coastal zone (MEC DCE) to exposure to the hydrographic pressures considered.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (53% of the southern subdivision of the Bay of Biscay marine sub-region). However, the exposure index remains mostly low, and for 90% of the major benthic habitat types, the area of habitat potentially at risk of moderate to high modification is greater than 30% of the total habitat area, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
The assessment of D7, based on data on anthropogenic activities, highlighted significant variations in exposure to pressures:1/ The Z200 zone is less subject than the coastal zone (MEC DCE) to exposure to the hydrographic pressures considered.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (53% of the southern subdivision of the Bay of Biscay marine sub-region). However, the exposure index remains mostly low, and for 90% of the major benthic habitat types, the area of habitat potentially at risk of moderate to high modification is greater than 30% of the total habitat area, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
The assessment of D7, based on data on anthropogenic activities, highlighted significant variations in exposure to pressures:1/ The Z200 zone is less subject than the coastal zone (MEC DCE) to exposure to the hydrographic pressures considered.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (53% of the southern subdivision of the Bay of Biscay marine sub-region). However, the exposure index remains mostly low, and for 90% of the major benthic habitat types, the area of habitat potentially at risk of moderate to high modification is greater than 30% of the total habitat area, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
The assessment of D7, based on data on anthropogenic activities, highlighted significant variations in exposure to pressures:1/ The Z200 zone is less subject than the coastal zone (MEC DCE) to exposure to the hydrographic pressures considered.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (53% of the southern subdivision of the Bay of Biscay marine sub-region). However, the exposure index remains mostly low, and for 90% of the major benthic habitat types, the area of habitat potentially at risk of moderate to high modification is greater than 30% of the total habitat area, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
The assessment of D7, based on data on anthropogenic activities, highlighted significant variations in exposure to pressures:1/ The Z200 zone is less subject than the coastal zone (MEC DCE) to exposure to the hydrographic pressures considered.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (53% of the southern subdivision of the Bay of Biscay marine sub-region). However, the exposure index remains mostly low, and for 90% of the major benthic habitat types, the area of habitat potentially at risk of moderate to high modification is greater than 30% of the total habitat area, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
The assessment of D7, based on data on anthropogenic activities, highlighted significant variations in exposure to pressures:1/ The Z200 zone is less subject than the coastal zone (MEC DCE) to exposure to the hydrographic pressures considered.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (53% of the southern subdivision of the Bay of Biscay marine sub-region). However, the exposure index remains mostly low, and for 90% of the major benthic habitat types, the area of habitat potentially at risk of moderate to high modification is greater than 30% of the total habitat area, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
The assessment of D7, based on data on anthropogenic activities, highlighted significant variations in exposure to pressures:1/ The Z200 zone is less subject than the coastal zone (MEC DCE) to exposure to the hydrographic pressures considered.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (53% of the southern subdivision of the Bay of Biscay marine sub-region). However, the exposure index remains mostly low, and for 90% of the major benthic habitat types, the area of habitat potentially at risk of moderate to high modification is greater than 30% of the total habitat area, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
The assessment of D7, based on data on anthropogenic activities, highlighted significant variations in exposure to pressures:1/ The Z200 zone is less subject than the coastal zone (MEC DCE) to exposure to the hydrographic pressures considered.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (53% of the southern subdivision of the Bay of Biscay marine sub-region). However, the exposure index remains mostly low, and for 90% of the major benthic habitat types, the area of habitat potentially at risk of moderate to high modification is greater than 30% of the total habitat area, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
The assessment of D7, based on data on anthropogenic activities, highlighted significant variations in exposure to pressures:1/ The Z200 zone is less subject than the coastal zone (MEC DCE) to exposure to the hydrographic pressures considered.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (53% of the southern subdivision of the Bay of Biscay marine sub-region). However, the exposure index remains mostly low, and for 90% of the major benthic habitat types, the area of habitat potentially at risk of moderate to high modification is greater than 30% of the total habitat area, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
The assessment of D7, based on data on anthropogenic activities, highlighted significant variations in exposure to pressures:1/ The Z200 zone is less subject than the coastal zone (MEC DCE) to exposure to the hydrographic pressures considered.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (53% of the southern subdivision of the Bay of Biscay marine sub-region). However, the exposure index remains mostly low, and for 90% of the major benthic habitat types, the area of habitat potentially at risk of moderate to high modification is greater than 30% of the total habitat area, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
Assessments period
2012-2018
2012-2018
2012-2018
2012-2018
2012-2018
2012-2018
2012-2018
2012-2018
2012-2018
2012-2018
2012-2018
2012-2018
2012-2018
2012-2018
2012-2018
2012-2018
2012-2018
2012-2018
2012-2018
2012-2018
Related pressures
Related targets