Member State report / Art8 / 2018 / D7 / France / NE Atlantic: Celtic Seas
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: Celtic Seas |
Reported by | Ministère de la transition Ecologique et Solidaire |
Report date | 2020-02-19 |
Report access | ART8_GES_FR_2020-02-17.xml |
MC L200 (ACS-FR-MS-MC-L200)
GES component |
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
|
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 mud |
Offshore circalittoral sand |
Element code |
ExpPresCurrents |
ExpPresSalinity |
ExpPresSeabedNature |
ExpPresTemperature |
ExpPresTide |
ExpPresTurbidity |
ExpPresWaves |
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
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Link to other vocabulary or code lists that may be relevant
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Link to other vocabulary or code lists that may be relevant
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Link to other vocabulary or code lists that may be relevant
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Link to other vocabulary or code lists that may be relevant
|
Link to other vocabulary or code lists that may be relevant
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Habitats (D1-D6) http://dd.eionet.europa.eu/vocabulary/msfd/broadHabitatTypes/view
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Habitats (D1-D6) http://dd.eionet.europa.eu/vocabulary/msfd/broadHabitatTypes/view
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Element 2 |
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Element 2 code |
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Element 2 code source |
|||||||||
Element source |
National |
National |
National |
National |
National |
National |
National |
EU |
EU |
Criterion |
D7C1
|
D7C1
|
D7C1
|
D7C1
|
D7C1
|
D7C1
|
D7C1
|
D7C2
|
D7C2
|
Parameter |
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
|
Threshold value source |
|||||||||
Threshold value source other |
|||||||||
Value achieved upper |
|||||||||
Value achieved lower |
|||||||||
Value unit |
|||||||||
Value unit other |
|||||||||
Proportion threshold value |
|||||||||
Proportion value achieved |
3033.0 |
10.0 |
3033.0 |
69.0 |
216.0 |
||||
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 |
Trend |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Parameter achieved |
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 according to 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 exposure index are: No exposure: 3142 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 according to 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 exposure index are: No exposure: 3142 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 according to the level of the exposure index). The areas potentially affected by a change in background nature correspond to a total area of 3033 km2 . The areas of exposure according to the four levels of exposure index are: No Exposure: 110 km² Low Exposure Index: 3033 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 <10 km2 . The areas of exposure according to the four levels of exposure index are: No exposure: 3142 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 according to the level of the exposure index). The metric considered for this parameter is the area of exposure for each pressure considered (overall or according to 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 . The areas of exposure according to the four levels of exposure index are: No exposure: 3142 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 according to the level of the exposure index). The areas potentially affected by a change in the turbidity regime correspond to a total area of 3033 km2 . The areas of exposure according to the four levels of exposure index are: No Exposure: 110 km² Low Exposure Index: 3033 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 exposure index are: No Exposure: 3142 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 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 69 km2 (i.e. 100% of the assessed habitat). The indicator also allows the intensity of the risk of modification to be assessed: negligible or no risk of modification: 0 km².low risk of modification: 38 km².medium risk of modification: 31 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 216 km2 (i.e., 100% of the assessed habitat). In addition, the indicator measures the intensity of the risk of modification: Negligible or no risk of modification: 0 km². Low risk of change: 82 km². Medium risk of change: 134 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 |
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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 |
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 associated with a change in the current, tidal and wave regime do not affect the MRU-L200 (0% of the total area of the MRU). Pressures related to a change in bottom nature and turbidity regime potentially affect a very large area (96.5% of the MRU). It should also be noted that the exposure index calculated for the change in background nature is exclusively low. Finally, the pressures associated with 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 associated with a change in the current, tidal and wave regime do not affect the MRU-L200 (0% of the total area of the MRU). Pressures related to a change in bottom nature and turbidity regime potentially affect a very large area (96.5% of the MRU). It should also be noted that the exposure index calculated for the change in background nature is exclusively low. Finally, the pressures associated with 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 associated with a change in the current, tidal and wave regime do not affect the MRU-L200 (0% of the total area of the MRU). Pressures related to a change in bottom nature and turbidity regime potentially affect a very large area (96.5% of the MRU). It should also be noted that the exposure index calculated for the change in background nature is exclusively low. Finally, the pressures associated with 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 associated with a change in the current, tidal and wave regime do not affect the MRU-L200 (0% of the total area of the MRU). Pressures related to a change in bottom nature and turbidity regime potentially affect a very large area (96.5% of the MRU). It should also be noted that the exposure index calculated for the change in background nature is exclusively low. Finally, the pressures associated with 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 associated with a change in the current, tidal and wave regime do not affect the MRU-L200 (0% of the total area of the MRU). Pressures related to a change in bottom nature and turbidity regime potentially affect a very large area (96.5% of the MRU). It should also be noted that the exposure index calculated for the change in background nature is exclusively low. Finally, the pressures associated with 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 associated with a change in the current, tidal and wave regime do not affect the MRU-L200 (0% of the total area of the MRU). Pressures related to a change in bottom nature and turbidity regime potentially affect a very large area (96.5% of the MRU). It should also be noted that the exposure index calculated for the change in background nature is exclusively low. Finally, the pressures associated with 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 associated with a change in the current, tidal and wave regime do not affect the MRU-L200 (0% of the total area of the MRU). Pressures related to a change in bottom nature and turbidity regime potentially affect a very large area (96.5% of the MRU). It should also be noted that the exposure index calculated for the change in background nature is exclusively low. Finally, the pressures associated with 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, 45% of the area of "offshore circalittoral mud" habitat appears to be at medium risk and 55% 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. For example, "offshore circalittoral sands" habitat has a large area at medium risk (62% of the habitat area).
|
Element status |
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.
|
Integration rule type parameter |
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
|
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 |
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 (100% of the Celtic Sea 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 a 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 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 (100% of the Celtic Sea 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 a 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 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 (100% of the Celtic Sea 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 a 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 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 (100% of the Celtic Sea 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 a 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 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 (100% of the Celtic Sea 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 a 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 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 (100% of the Celtic Sea 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 a 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 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 (100% of the Celtic Sea 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 a 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 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 (100% of the Celtic Sea 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 a 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 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 (100% of the Celtic Sea 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 a 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 |
Related pressures |
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Related targets |
MC MEC DCE (ACS-FR-MS-MC-MEC2010)
GES component |
D7
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D7
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D7
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D7
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D7
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D7
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D7
|
D7
|
D7
|
D7
|
D7
|
D7
|
D7
|
D7
|
D7
|
D7
|
D7
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D7
|
D7
|
D7
|
D7
|
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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
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Benthic broad habitats
|
Benthic broad habitats
|
Benthic broad habitats
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Benthic broad habitats
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Benthic broad habitats
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Benthic broad habitats
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Benthic broad habitats
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Benthic broad habitats
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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 |
Offshore circalittoral sand |
Element code |
ExpPresCurrents |
ExpPresSalinity |
ExpPresSeabedNature |
ExpPresTemperature |
ExpPresTide |
ExpPresTurbidity |
ExpPresWaves |
HabBenCircalitCoarSed |
HabBenCircalitMxdSed |
HabBenCircalitMud |
HabBenCircalitRock |
HabBenCircalitSand |
HabBenInfralitCoarSed |
HabBenInfralitMxdSed |
HabBenInfralitMud |
HabBenInfralitRock |
HabBenInfralitSand |
HabBenOffshCoarSed |
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
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Link to other vocabulary or code lists that may be relevant
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Link to other vocabulary or code lists that may be relevant
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Link to other vocabulary or code lists that may be relevant
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Link to other vocabulary or code lists that may be relevant
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Link to other vocabulary or code lists that may be relevant
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Habitats (D1-D6) http://dd.eionet.europa.eu/vocabulary/msfd/broadHabitatTypes/view
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Habitats (D1-D6) http://dd.eionet.europa.eu/vocabulary/msfd/broadHabitatTypes/view
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Habitats (D1-D6) http://dd.eionet.europa.eu/vocabulary/msfd/broadHabitatTypes/view
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Habitats (D1-D6) http://dd.eionet.europa.eu/vocabulary/msfd/broadHabitatTypes/view
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Habitats (D1-D6) http://dd.eionet.europa.eu/vocabulary/msfd/broadHabitatTypes/view
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Habitats (D1-D6) http://dd.eionet.europa.eu/vocabulary/msfd/broadHabitatTypes/view
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Habitats (D1-D6) http://dd.eionet.europa.eu/vocabulary/msfd/broadHabitatTypes/view
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Habitats (D1-D6) http://dd.eionet.europa.eu/vocabulary/msfd/broadHabitatTypes/view
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Habitats (D1-D6) http://dd.eionet.europa.eu/vocabulary/msfd/broadHabitatTypes/view
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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
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Habitats (D1-D6) http://dd.eionet.europa.eu/vocabulary/msfd/broadHabitatTypes/view
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Element 2 |
|||||||||||||||||||||
Element 2 code |
|||||||||||||||||||||
Element 2 code source |
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Element source |
National |
National |
National |
National |
National |
National |
National |
EU |
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
|
D7C2
|
Parameter |
Extent
|
Extent
|
Extent
|
Extent
|
Extent
|
Extent
|
Extent
|
Extent
|
Extent
|
Extent
|
Extent
|
Extent
|
Extent
|
Extent
|
Extent
|
Extent
|
Extent
|
Extent
|
Extent
|
Extent
|
Extent
|
Parameter other |
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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
|
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 |
742.0 |
10.0 |
5059.0 |
10.0 |
680.0 |
5048.0 |
680.0 |
1137.0 |
10.0 |
86.0 |
680.0 |
306.0 |
409.0 |
52.0 |
68.0 |
563.0 |
677.0 |
615.0 |
34.0 |
48.0 |
130.0 |
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 |
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 |
Unknown |
Parameter achieved |
Unknown |
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 flow regime correspond to a total area of 742 km2 . The areas of exposure according to the four levels of exposure index are: No Exposure: 4317 km² Low Exposure Index: 659 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 area of <10 km2 . The areas of exposure according to the four levels of exposure index are: No exposure: 5059 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 according to the level of the exposure index). The areas potentially affected by a change in background nature correspond to a total area of 5059 km2 . The areas of exposure according to the four levels of exposure index are: No exposure: 0 km² Low exposure index: 4987 km² Medium exposure index: 72 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 <10 km2 . The areas of exposure according to the four levels of exposure index are: No exposure: 5059 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 according to the level of the exposure index). The areas potentially affected by a change in tidal regime correspond to a total area of 680 km2 . The areas of exposure according to the four levels of exposure index are: No exposure: 4379 km² Low exposure index: 594 km² Medium exposure index: 86 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 according to the level of the exposure index). The areas potentially affected by a change in the turbidity regime correspond to a total area of 5048 km2 . The areas of exposure according to the four levels of exposure index are: No Exposure: 10 km² Low Exposure Index: 4691 km² Medium Exposure Index: 343 km² High Exposure Index: 14 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 wave regime correspond to a total area of 680 km2 . The areas of exposure according to the four levels of exposure index are: No Exposure: 4379 km² Low Exposure Index: 663 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 alteration 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 nil risk of modification: 0 km², low risk of modification: 464 km², medium risk of modification: 666 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 alteration associated with permanent changes in hydrographic conditions in this MRU is 10 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: 0 km², medium risk of modification: 7 km², high risk of modification: 3 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 86 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: 62 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 680 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: 364 km², medium risk of modification: 309 km², high risk of modification: 7 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: 158 km².medium risk of modification: 148 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 409 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: 83 km², medium risk of modification: 292 km², high risk of modification: 34 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 52 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: 0 km², medium risk of modification: 31 km², high risk of modification: 21 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 68 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: 17 km², high risk of modification: 17 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 563 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: 144 km², medium risk of modification: 316 km², high risk of modification: 103 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 677 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: 141 km², medium risk of modification: 460 km², high risk of modification: 76 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 615 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: 244 km².medium risk of modification: 371 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 34 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: 34 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 related to permanent changes in hydrographic conditions in this MRU is 48 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: 27 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 130 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: 113 km², medium risk of modification: 17 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 |
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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 |
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 (< 2% of the Celtic Sea marine sub-region) and fairly localised since they affect only coastal waters. 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 turbidity regime potentially affect a very large area (100% of the MRU) although the exposure indices calculated for these pressures are mostly low (respectively >98% of the MRU and nearly 93% of the MRU). 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 (< 2% of the Celtic Sea marine sub-region) and fairly localised since they affect only coastal waters. 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 turbidity regime potentially affect a very large area (100% of the MRU) although the exposure indices calculated for these pressures are mostly low (respectively >98% of the MRU and nearly 93% of the MRU). 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 (< 2% of the Celtic Sea marine sub-region) and fairly localised since they affect only coastal waters. 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 turbidity regime potentially affect a very large area (100% of the MRU) although the exposure indices calculated for these pressures are mostly low (respectively >98% of the MRU and nearly 93% of the MRU). 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 (< 2% of the Celtic Sea marine sub-region) and fairly localised since they affect only coastal waters. 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 turbidity regime potentially affect a very large area (100% of the MRU) although the exposure indices calculated for these pressures are mostly low (respectively >98% of the MRU and nearly 93% of the MRU). 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 (< 2% of the Celtic Sea marine sub-region) and fairly localised since they affect only coastal waters. 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 turbidity regime potentially affect a very large area (100% of the MRU) although the exposure indices calculated for these pressures are mostly low (respectively >98% of the MRU and nearly 93% of the MRU). 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 (< 2% of the Celtic Sea marine sub-region) and fairly localised since they affect only coastal waters. 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 turbidity regime potentially affect a very large area (100% of the MRU) although the exposure indices calculated for these pressures are mostly low (respectively >98% of the MRU and nearly 93% of the MRU). 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 (< 2% of the Celtic Sea marine sub-region) and fairly localised since they affect only coastal waters. 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 turbidity regime potentially affect a very large area (100% of the MRU) although the exposure indices calculated for these pressures are mostly low (respectively >98% of the MRU and nearly 93% of the MRU). 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, more than 58% of the area of the "Coastal circalittoral coarse sediment" habitat appears to be subject to a medium risk and less than 1% to a high risk.
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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 coastal circalittoral sediment" habitat presents one of the largest areas at high risk, with 33% of the total habitat area subject to a high risk and the rest subject to a medium risk.
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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, 28% of the "Coastal circalittoral mud" habitat area appears to be at medium risk.
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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, 46% of the surface area of the habitat "Rocks and coastal circalittoral biogenic reefs" appears to be subject to a medium risk and 1% to a high risk.
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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, 48% of the total area of the "Coastal circalittoral sands" habitat appears to be at medium risk.
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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 "Subtidal coarse sediment" habitat presents a high risk area of 8% of the total habitat area.
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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 subtidal sediment" habitat presents the largest area at high risk with 40% of the total habitat area at high risk.
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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 one of the largest areas at high risk, with 25% of the total area of the habitat subject to high risk.
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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 "Subtidal biogenic rocks and reefs" habitat presents a large area at high risk (18% of the total habitat area).
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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 "Subtidal Sands" habitat presents a large area at high risk (11% of the total habitat area).
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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, 60% of the area of "coarse circalittoral offshore sediment" habitat appears to be at medium risk.
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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, 100% of the area of "offshore circalittoral mud" habitat appears to be at low risk.
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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, 57% of the total area of "offshore circalittoral biogenic rock and reef" habitat appears to be at medium risk.
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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, 13% of the area of offshore circalittoral sands habitat appears to be at medium risk, with the majority (87% of the habitat area) at low risk.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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Integration rule type parameter |
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Integration rule description parameter |
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Integration rule type criteria |
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Integration rule description criteria |
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GES extent threshold |
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GES extent achieved |
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GES extent unit |
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GES achieved |
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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 under consideration.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (100% of the Celtic Sea 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 a 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.
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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 under consideration.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (100% of the Celtic Sea 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 a 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.
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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 under consideration.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (100% of the Celtic Sea 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 a 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.
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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 under consideration.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (100% of the Celtic Sea 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 a 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.
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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 under consideration.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (100% of the Celtic Sea 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 a 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 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 under consideration.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (100% of the Celtic Sea 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 a 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 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 under consideration.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (100% of the Celtic Sea 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 a 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 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 under consideration.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (100% of the Celtic Sea 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 a 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 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 under consideration.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (100% of the Celtic Sea 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 a 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 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 under consideration.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (100% of the Celtic Sea 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 a 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 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 under consideration.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (100% of the Celtic Sea 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 a 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 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 under consideration.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (100% of the Celtic Sea 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 a 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 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 under consideration.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (100% of the Celtic Sea 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 a 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 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 under consideration.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (100% of the Celtic Sea 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 a 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 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 under consideration.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (100% of the Celtic Sea 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 a 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 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 under consideration.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (100% of the Celtic Sea 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 a 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 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 under consideration.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (100% of the Celtic Sea 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 a 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 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 under consideration.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (100% of the Celtic Sea 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 a 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 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 under consideration.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (100% of the Celtic Sea 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 a 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 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 under consideration.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (100% of the Celtic Sea 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 a 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 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 under consideration.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (100% of the Celtic Sea 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 a 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 |
2012-2018 |
Related pressures |
|||||||||||||||||||||
Related targets |
MC Z200 (ACS-FR-MS-MC-Z200)
GES component |
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
|
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 rock and biogenic reef |
Circalittoral sand |
Infralittoral coarse 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 |
HabBenCircalitRock |
HabBenCircalitSand |
HabBenInfralitCoarSed |
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
|
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 |
Criterion |
D7C1
|
D7C1
|
D7C1
|
D7C1
|
D7C1
|
D7C1
|
D7C1
|
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
|
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
|
Threshold value source |
|||||||||||||||||
Threshold value source other |
|||||||||||||||||
Value achieved upper |
|||||||||||||||||
Value achieved lower |
|||||||||||||||||
Value unit |
|||||||||||||||||
Value unit other |
|||||||||||||||||
Proportion threshold value |
|||||||||||||||||
Proportion value achieved |
34999.0 |
10.0 |
34999.0 |
1782.0 |
62.0 |
7.0 |
10.0 |
3.4 |
20705.0 |
10.0 |
28.0 |
62.0 |
12212.0 |
||||
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 |
Trend |
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 |
Description parameter |
The metric considered for this parameter is the area of exposure for each pressure considered (overall or according to 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 exposure index are: No exposure: 34999 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 according to 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 exposure index are: No exposure: 34999 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 according to the level of the exposure index). The areas potentially affected by a change in background nature correspond to a total area of 34999 km2 . The areas of exposure according to the four levels of exposure index are: No Exposure: 0 km² Low Exposure Index: 34999 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 <10 km2 . The areas of exposure according to the four levels of exposure index are: No exposure: 34999 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 tidal regime correspond to a total area of 0 km2 . The areas of exposure according to the four levels of exposure index are: No exposure: 34999 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 according to the level of the exposure index). The areas potentially affected by a change in the turbidity regime correspond to a total area of 34999 km2 . The areas of exposure according to the four levels of exposure index are: No Exposure: 0 km² Low Exposure Index: 34999 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 exposure index are: No Exposure: 34999 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 1782 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: 412 km², medium risk of modification: 1370 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 62 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: 31 km², medium risk of modification: 31 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 based on the level of risk). The spatial extent of potential habitat alteration associated with permanent changes in hydrographic conditions in this MRU is 7 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: 0 km², medium risk of modification: 7 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 based on the level of risk). The spatial extent of potential habitat alteration associated with permanent changes in hydrographic conditions in this MRU is 10 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: 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 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). 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: 3.4 km².medium risk of modification: 0 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 20705 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: 7947 km².medium risk of modification: 12758 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 10 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: 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 based on the level of risk). The spatial extent of potential habitat alteration associated with permanent changes in hydrographic conditions in this MRU is 28 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: 14 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 based on the level of risk). The spatial extent of potential habitat alteration associated with permanent changes in hydrographic conditions in this MRU is 62 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: 38 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 12212 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: 2936 km², medium risk of modification: 9276 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 |
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 associated with a change in the current, tidal and wave regime do not affect MRU-Z200 (0% of the total area of the MRU). Pressures related to a change in bottom nature and turbidity regime potentially affect a very large area (100% of the MRU). It should also be noted that the exposure index calculated for these pressures is exclusively low. 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 associated with a change in the current, tidal and wave regime do not affect MRU-Z200 (0% of the total area of the MRU). Pressures related to a change in bottom nature and turbidity regime potentially affect a very large area (100% of the MRU). It should also be noted that the exposure index calculated for these pressures is exclusively low. 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 associated with a change in the current, tidal and wave regime do not affect MRU-Z200 (0% of the total area of the MRU). Pressures related to a change in bottom nature and turbidity regime potentially affect a very large area (100% of the MRU). It should also be noted that the exposure index calculated for these pressures is exclusively low. 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 associated with a change in the current, tidal and wave regime do not affect MRU-Z200 (0% of the total area of the MRU). Pressures related to a change in bottom nature and turbidity regime potentially affect a very large area (100% of the MRU). It should also be noted that the exposure index calculated for these pressures is exclusively low. 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 associated with a change in the current, tidal and wave regime do not affect MRU-Z200 (0% of the total area of the MRU). Pressures related to a change in bottom nature and turbidity regime potentially affect a very large area (100% of the MRU). It should also be noted that the exposure index calculated for these pressures is exclusively low. 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 associated with a change in the current, tidal and wave regime do not affect MRU-Z200 (0% of the total area of the MRU). Pressures related to a change in bottom nature and turbidity regime potentially affect a very large area (100% of the MRU). It should also be noted that the exposure index calculated for these pressures is exclusively low. 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 associated with a change in the current, tidal and wave regime do not affect MRU-Z200 (0% of the total area of the MRU). Pressures related to a change in bottom nature and turbidity regime potentially affect a very large area (100% of the MRU). It should also be noted that the exposure index calculated for these pressures is exclusively low. 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, 77% of the surface area of the "coastal circalittoral coarse 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, 50% of the surface area of the "Coastal circalittoral biogenic rocks and reefs" habitat appears to be subject to a medium risk, and 50% 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, "coastal circalittoral sands" 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. Thus, the "coarse sediment infralittoral" habitat appears to be totally 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. Thus, the " infralittoral biogenic rocks and reefs " habitat appears to be totally 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. Thus, 62% 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, the "offshore circalittoral mixed sediment" 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. Thus, 50% of the area of "offshore circalittoral mud" habitat appears to be at medium risk and 50% at low risk.
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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, 39% of the area of "offshore circalittoral biogenic rock and reef" habitat appears to be at medium risk.
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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, "offshore circalittoral sands" habitat has a large area at medium risk (76% of the habitat area).
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Element status |
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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Integration rule type parameter |
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Integration rule description parameter |
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Integration rule type criteria |
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Integration rule description criteria |
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GES extent threshold |
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GES extent achieved |
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GES extent unit |
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GES achieved |
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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 (100% of the Celtic Sea 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 a 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.
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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 (100% of the Celtic Sea 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 a 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 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 (100% of the Celtic Sea 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 a 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 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 (100% of the Celtic Sea 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 a 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 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 (100% of the Celtic Sea 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 a 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 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 (100% of the Celtic Sea 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 a 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 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 (100% of the Celtic Sea 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 a 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 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 (100% of the Celtic Sea 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 a 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 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 (100% of the Celtic Sea 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 a 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 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 (100% of the Celtic Sea 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 a 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 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 (100% of the Celtic Sea 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 a 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 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 (100% of the Celtic Sea 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 a 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 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 (100% of the Celtic Sea 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 a 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.
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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 (100% of the Celtic Sea 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 a 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.
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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 (100% of the Celtic Sea 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 a 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.
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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 (100% of the Celtic Sea 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 a 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.
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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 (100% of the Celtic Sea 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 a 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.
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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 |
Related pressures |
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Related targets |