Member State report / Art8 / 2018 / D7 / France / NE Atlantic: Greater North Sea
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: Greater North Sea |
Reported by | Ministère de la transition Ecologique et Solidaire |
Report date | 2020-02-19 |
Report access | ART8_GES_FR_2020-02-17.xml |
MMN MEC DCE (ANS-FR-MS-MMN-MEC2010)
GES component |
D7
|
D7
|
D7
|
D7
|
D7
|
D7
|
D7
|
D7
|
D7
|
D7
|
D7
|
D7
|
D7
|
D7
|
D7
|
D7
|
D7
|
D7
|
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
Feature |
Hydrographical changes
|
Hydrographical changes
|
Hydrographical changes
|
Hydrographical changes
|
Hydrographical changes
|
Hydrographical changes
|
Hydrographical changes
|
Benthic broad habitats
|
Benthic broad habitats
|
Benthic broad habitats
|
Benthic broad habitats
|
Benthic broad habitats
|
Benthic broad habitats
|
Benthic broad habitats
|
Benthic broad habitats
|
Benthic broad habitats
|
Benthic broad habitats
|
Benthic broad habitats
|
Element |
Changes in current regime |
Changes in salinity regime |
Changes in seabed substrate |
Changes in thermal regime |
Changes in tide regime |
Changes in turbidity regime |
Changes in waves regime |
Circalittoral coarse sediment |
Circalittoral mud |
Circalittoral rock and biogenic reef |
Circalittoral sand |
Infralittoral coarse sediment |
Infralittoral mixed sediment |
Infralittoral mud |
Infralittoral rock and biogenic reef |
Infralittoral sand |
Offshore circalittoral coarse sediment |
Offshore circalittoral sand |
Element code |
ExpPresCurrents |
ExpPresSalinity |
ExpPresSeabedNature |
ExpPresTemperature |
ExpPresTide |
ExpPresTurbidity |
ExpPresWaves |
HabBenCircalitCoarSed |
HabBenCircalitMud |
HabBenCircalitRock |
HabBenCircalitSand |
HabBenInfralitCoarSed |
HabBenInfralitMxdSed |
HabBenInfralitMud |
HabBenInfralitRock |
HabBenInfralitSand |
HabBenOffshCoarSed |
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
|
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
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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
|
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 |
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Element 2 code |
||||||||||||||||||
Element 2 code source |
||||||||||||||||||
Element source |
National |
National |
National |
National |
National |
National |
National |
EU |
EU |
EU |
EU |
EU |
EU |
EU |
EU |
EU |
EU |
EU |
Criterion |
D7C1
|
D7C1
|
D7C1
|
D7C1
|
D7C1
|
D7C1
|
D7C1
|
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
|
Parameter other |
||||||||||||||||||
Threshold value upper |
||||||||||||||||||
Threshold value lower |
||||||||||||||||||
Threshold qualitative |
Not available yet
|
Not available yet
|
Not available yet
|
Not available yet
|
Not available yet
|
Not available yet
|
Not available yet
|
Not available yet
|
Not available yet
|
Not available yet
|
Not available yet
|
Not available yet
|
Not available yet
|
Not available yet
|
Not available yet
|
Not available yet
|
Not available yet
|
Not available yet
|
Threshold value source |
||||||||||||||||||
Threshold value source other |
||||||||||||||||||
Value achieved upper |
||||||||||||||||||
Value achieved lower |
||||||||||||||||||
Value unit |
||||||||||||||||||
Value unit other |
||||||||||||||||||
Proportion threshold value |
||||||||||||||||||
Proportion value achieved |
687.0 |
10.0 |
2174.0 |
10.0 |
649.0 |
2174.0 |
649.0 |
237.0 |
3.4 |
86.0 |
199.0 |
361.0 |
3.4 |
45.0 |
230.0 |
594.0 |
7.0 |
3.4 |
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 |
Trend |
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 |
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 687 km2 . The areas of exposure according to the four levels of exposure index are: No Exposure: 1487 km² Low Exposure Index: 680 km² Medium Exposure Index: 7 km² High Exposure Index: 0 km² Note that no threshold is currently available to assess whether or not the parameter has been reached.
|
The metric considered for this parameter is the area of exposure for each pressure considered (overall or as a function of the level of the exposure index). The areas potentially affected by a change in 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: 2174 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 2174 km2 . The areas of exposure according to the four levels of exposure index are: No exposure: 0 km² Low exposure index: 2092 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 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: 2174 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 649 km2 . The areas of exposure according to the four levels of exposure index are: No Exposure: 1525 km² Low Exposure Index: 591 km² Medium Exposure Index: 58 km² High Exposure Index: 0 km² Note that no threshold is currently available to assess whether or not the parameter has been reached.
|
The metric considered for this parameter is the area of exposure for each pressure considered (overall or 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 2174 km2 . The areas of exposure according to the four levels of exposure index are as follows: No Exposure: 0 km² Low Exposure Index: 1738 km² Medium Exposure Index: 436 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 wave regime correspond to a total area of 649 km2 . The areas of exposure according to the four levels of exposure index are: No Exposure: 1525 km² Low Exposure Index: 649 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 237 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: 113.3 km², medium risk of modification: 120.2 km², high risk of modification: 3.4 km², although no threshold is currently available to assess whether or not the parameter has been reached.
|
The metric considered for this parameter is the area of habitat potentially at risk (overall or based on the level of risk). The spatial extent of potential habitat alteration related to permanent changes in hydrographic conditions in this MRU is 3.4 km2 (i.e., 100% of the assessed habitat). 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: 0 km².medium risk of modification: 3.4 km².high risk of modification: 0 km².It should be noted that no threshold is currently available to assess whether or not the parameter has been reached.
|
The metric considered for this parameter is the area of habitat potentially at risk (overall or 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 no risk of modification: 0 km², low risk of modification: 38 km², medium risk of modification: 48 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 199 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: 148 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 361 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: 110 km², medium risk of modification: 213 km², high risk of modification: 38 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: 0 km².medium risk of modification: 3.4 km².high risk of modification: 0 km².It should be noted that no threshold is currently available to assess whether or not the parameter has been reached.
|
The metric considered for this parameter is the area of habitat potentially at risk (overall or based on the level of risk). The spatial extent of potential habitat alteration associated with permanent changes in hydrographic conditions in this MRU is 45 km2 (i.e., 100% of the assessed habitat). In addition, the indicator makes it possible to assess the intensity of the risk of modification: negligible or nil risk of modification: 0 km², low risk of modification: 14 km², medium risk of modification: 28 km², high risk of modification: 3 km², although no threshold is currently available to assess whether or not the parameter has been reached.
|
The metric considered for this parameter is the area of habitat potentially at risk (overall or based on the level of risk). The spatial extent of potential habitat alteration related to permanent changes in hydrographic conditions in this MRU is 230 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: 41 km².medium risk of modification: 117 km².high risk of modification: 72 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 594 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: 364 km², high risk of modification: 86 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 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: 0 km².medium risk of modification: 3.4 km².high risk of modification: 0 km².It should be noted that no threshold is currently available to assess whether or not the parameter has been reached.
|
Related indicator |
||||||||||||||||||
Criteria status |
Contributes to assessment of another criterion/ele |
Contributes to assessment of another criterion/ele |
Contributes to assessment of another criterion/ele |
Contributes to assessment of another criterion/ele |
Contributes to assessment of another criterion/ele |
Contributes to assessment of another criterion/ele |
Contributes to assessment of another criterion/ele |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
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 bottom nature, tidal regime, salinity, turbidity, waves, currents and thermal regime. Indeed, the results show that the pressures associated with 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 indices calculated for the modification of the nature of the bottom are mostly low, whereas for the turbidity regime, the proportion of surface area subject to a medium level exposure index is relatively high (20% of the total surface area of the MRU). The pressures associated with a change in the tidal, wave and current regime are generally local and affect coastal waters almost exclusively. It should also be noted that the exposure indices calculated for these pressures are mostly low. Pressures linked to a change in the salinity and thermal regime each 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 bottom nature, tidal regime, salinity, turbidity, waves, currents and thermal regime. Indeed, the results show that the pressures associated with 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 indices calculated for the modification of the nature of the bottom are mostly low, whereas for the turbidity regime, the proportion of surface area subject to a medium level exposure index is relatively high (20% of the total surface area of the MRU). The pressures associated with a change in the tidal, wave and current regime are generally local and affect coastal waters almost exclusively. It should also be noted that the exposure indices calculated for these pressures are mostly low. Pressures linked to a change in the salinity and thermal regime each 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 bottom nature, tidal regime, salinity, turbidity, waves, currents and thermal regime. Indeed, the results show that the pressures associated with 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 indices calculated for the modification of the nature of the bottom are mostly low, whereas for the turbidity regime, the proportion of surface area subject to a medium level exposure index is relatively high (20% of the total surface area of the MRU). The pressures associated with a change in the tidal, wave and current regime are generally local and affect coastal waters almost exclusively. It should also be noted that the exposure indices calculated for these pressures are mostly low. Pressures linked to a change in the salinity and thermal regime each 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 bottom nature, tidal regime, salinity, turbidity, waves, currents and thermal regime. Indeed, the results show that the pressures associated with 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 indices calculated for the modification of the nature of the bottom are mostly low, whereas for the turbidity regime, the proportion of surface area subject to a medium level exposure index is relatively high (20% of the total surface area of the MRU). The pressures associated with a change in the tidal, wave and current regime are generally local and affect coastal waters almost exclusively. It should also be noted that the exposure indices calculated for these pressures are mostly low. Pressures linked to a change in the salinity and thermal regime each 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 bottom nature, tidal regime, salinity, turbidity, waves, currents and thermal regime. Indeed, the results show that the pressures associated with 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 indices calculated for the modification of the nature of the bottom are mostly low, whereas for the turbidity regime, the proportion of surface area subject to a medium level exposure index is relatively high (20% of the total surface area of the MRU). The pressures associated with a change in the tidal, wave and current regime are generally local and affect coastal waters almost exclusively. It should also be noted that the exposure indices calculated for these pressures are mostly low. Pressures linked to a change in the salinity and thermal regime each 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 bottom nature, tidal regime, salinity, turbidity, waves, currents and thermal regime. Indeed, the results show that the pressures associated with 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 indices calculated for the modification of the nature of the bottom are mostly low, whereas for the turbidity regime, the proportion of surface area subject to a medium level exposure index is relatively high (20% of the total surface area of the MRU). The pressures associated with a change in the tidal, wave and current regime are generally local and affect coastal waters almost exclusively. It should also be noted that the exposure indices calculated for these pressures are mostly low. Pressures linked to a change in the salinity and thermal regime each 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 bottom nature, tidal regime, salinity, turbidity, waves, currents and thermal regime. Indeed, the results show that the pressures associated with 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 indices calculated for the modification of the nature of the bottom are mostly low, whereas for the turbidity regime, the proportion of surface area subject to a medium level exposure index is relatively high (20% of the total surface area of the MRU). The pressures associated with a change in the tidal, wave and current regime are generally local and affect coastal waters almost exclusively. It should also be noted that the exposure indices calculated for these pressures are mostly low. Pressures linked to a change in the salinity and thermal regime each 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, 50% of the area of "Coastal circalittoral coarse sediment" habitat appears to be subject to a medium risk and 1% to a high risk.
|
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017), the D7C2 assessment must be carried out for each habitat type that is affected by changing hydrographic conditions and the D7C2 results are not integrated. On the other hand, no threshold has been defined so far for the parameter "Extent" and therefore the status of D7C2 is not reported, but the assessment of D7C2 has provided a first estimate of the spatial extent of benthic habitats potentially subject to cumulative risks of alteration, based on the indices of exposure to hydrographic pressures generated by human activities. Thus, 100% of the surface area of the "Coastal circalittoral mud flats" 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, 56% of the surface area of the "Coastal circalittoral biogenic rocks and reefs" habitat appears to be subject to an average risk.
|
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017), the D7C2 assessment must be carried out for each habitat type that is affected by changing hydrographic conditions and the D7C2 results are not integrated. On the other hand, no threshold has been defined so far for the parameter "Extent" and therefore the status of D7C2 is not reported, but the assessment of D7C2 has provided a first estimate of the spatial extent of benthic habitats potentially subject to cumulative risks of alteration, based on the indices of exposure to hydrographic pressures generated by human activities. Thus, the "Coastal circalittoral sands" habitat presents a relatively large area at high risk (9% of the total habitat area at high risk).
|
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017), the D7C2 assessment must be carried out for each habitat type that is affected by changing hydrographic conditions and the D7C2 results are not integrated. On the other hand, no threshold has been defined so far for the parameter "Extent" and therefore the status of D7C2 is not reported, but the assessment of D7C2 has provided a first estimate of the spatial extent of benthic habitats potentially subject to cumulative risks of alteration, based on the indices of exposure to hydrographic pressures generated by human activities. Thus, the "Coarse sediment infralittoral" habitat presents a large area at high risk (area at high risk >10% of 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, 100% of the surface area of the "mixed infralittoral 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, the "infralittoral mudflats" habitat presents a relatively large area at high risk (8% of the total habitat area at high risk).
|
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017), the D7C2 assessment must be carried out for each habitat type that is affected by changing hydrographic conditions and the D7C2 results are not integrated. On the other hand, no threshold has been defined so far for the parameter "Extent" and therefore the status of D7C2 is not reported, but the assessment of D7C2 has provided a first estimate of the spatial extent of benthic habitats potentially subject to cumulative risks of alteration, based on the indices of exposure to hydrographic pressures generated by human activities. Thus, the habitat "Rocks and biogenic infralittoral reefs" appears to be the habitat most at risk (area at high risk >30% of the total habitat area).
|
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017), the D7C2 assessment must be carried out for each habitat type that is affected by changing hydrographic conditions and the D7C2 results are not integrated. On the other hand, no threshold has been defined so far for the parameter "Extent" and therefore the status of D7C2 is not reported, but the assessment of D7C2 has provided a first estimate of the spatial extent of benthic habitats potentially subject to cumulative risks of alteration, based on the indices of exposure to hydrographic pressures generated by human activities. Thus, the "infralittoral sands" habitat presents a large area at high risk (area at high risk >10% of 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, 100% of the area of " circalittoral offshore 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, 100% of the area of "offshore circalittoral sands" habitat appears to be at medium risk.
|
Element status |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Description element |
The assessment of criterion D7C1 contributes to the assessment of criterion D7C2. Thus, the accumulation of quantified pressures (i.e., exposure indices) under D7C1 is incorporated into the calculation of the risk of modification of each habitat for the D7C2 assessment.
|
The assessment of criterion D7C1 contributes to the assessment of criterion D7C2. Thus, the accumulation of quantified pressures (i.e., exposure indices) under D7C1 is incorporated into the calculation of the risk of modification of each habitat for the D7C2 assessment.
|
The assessment of criterion D7C1 contributes to the assessment of criterion D7C2. Thus, the accumulation of quantified pressures (i.e., exposure indices) under D7C1 is incorporated into the calculation of the risk of modification of each habitat for the D7C2 assessment.
|
The assessment of criterion D7C1 contributes to the assessment of criterion D7C2. Thus, the accumulation of quantified pressures (i.e., exposure indices) under D7C1 is incorporated into the calculation of the risk of modification of each habitat for the D7C2 assessment.
|
The assessment of criterion D7C1 contributes to the assessment of criterion D7C2. Thus, the accumulation of quantified pressures (i.e., exposure indices) under D7C1 is incorporated into the calculation of the risk of modification of each habitat for the D7C2 assessment.
|
The assessment of criterion D7C1 contributes to the assessment of criterion D7C2. Thus, the accumulation of quantified pressures (i.e., exposure indices) under D7C1 is incorporated into the calculation of the risk of modification of each habitat for the D7C2 assessment.
|
The assessment of criterion D7C1 contributes to the assessment of criterion D7C2. Thus, the accumulation of quantified pressures (i.e., exposure indices) under D7C1 is incorporated into the calculation of the risk of modification of each habitat for the D7C2 assessment.
|
In the absence of a threshold for the "Extent" parameter, the state of the habitat could not be provided. Furthermore, according to Decision 2017/848/EU, the results of the assessment of criterion D7C2 (estimated extent of adverse effects by habitat type in each assessment area) are used for the assessment of criterion D6C5. However, in the absence of an operational indicator at the level of Descriptor 6 - Benthic Habitats, these results could not be taken into account in the assessment of D6C5.
|
In the absence of a threshold for the "Extent" parameter, the state of the habitat could not be provided. Furthermore, according to Decision 2017/848/EU, the results of the assessment of criterion D7C2 (estimated extent of adverse effects by habitat type in each assessment area) are used for the assessment of criterion D6C5. However, in the absence of an operational indicator at the level of Descriptor 6 - Benthic Habitats, these results could not be taken into account in the assessment of D6C5.
|
In the absence of a threshold for the "Extent" parameter, the state of the habitat could not be provided. Furthermore, according to Decision 2017/848/EU, the results of the assessment of criterion D7C2 (estimated extent of adverse effects by habitat type in each assessment area) are used for the assessment of criterion D6C5. However, in the absence of an operational indicator at the level of Descriptor 6 - Benthic Habitats, these results could not be taken into account in the assessment of D6C5.
|
In the absence of a threshold for the "Extent" parameter, the state of the habitat could not be provided. Furthermore, according to Decision 2017/848/EU, the results of the assessment of criterion D7C2 (estimated extent of adverse effects by habitat type in each assessment area) are used for the assessment of criterion D6C5. However, in the absence of an operational indicator at the level of Descriptor 6 - Benthic Habitats, these results could not be taken into account in the assessment of D6C5.
|
In the absence of a threshold for the "Extent" parameter, the state of the habitat could not be provided. Furthermore, according to Decision 2017/848/EU, the results of the assessment of criterion D7C2 (estimated extent of adverse effects by habitat type in each assessment area) are used for the assessment of criterion D6C5. However, in the absence of an operational indicator at the level of Descriptor 6 - Benthic Habitats, these results could not be taken into account in the assessment of D6C5.
|
In the absence of a threshold for the "Extent" parameter, the state of the habitat could not be provided. Furthermore, according to Decision 2017/848/EU, the results of the assessment of criterion D7C2 (estimated extent of adverse effects by habitat type in each assessment area) are used for the assessment of criterion D6C5. However, in the absence of an operational indicator at the level of Descriptor 6 - Benthic Habitats, these results could not be taken into account in the assessment of D6C5.
|
In the absence of a threshold for the "Extent" parameter, the state of the habitat could not be provided. Furthermore, according to Decision 2017/848/EU, the results of the assessment of criterion D7C2 (estimated extent of adverse effects by habitat type in each assessment area) are used for the assessment of criterion D6C5. However, in the absence of an operational indicator at the level of Descriptor 6 - Benthic Habitats, these results could not be taken into account in the assessment of D6C5.
|
In the absence of a threshold for the "Extent" parameter, the state of the habitat could not be provided. Furthermore, according to Decision 2017/848/EU, the results of the assessment of criterion D7C2 (estimated extent of adverse effects by habitat type in each assessment area) are used for the assessment of criterion D6C5. However, in the absence of an operational indicator at the level of Descriptor 6 - Benthic Habitats, these results could not be taken into account in the assessment of D6C5.
|
In the absence of a threshold for the "Extent" parameter, the state of the habitat could not be provided. Furthermore, according to Decision 2017/848/EU, the results of the assessment of criterion D7C2 (estimated extent of adverse effects by habitat type in each assessment area) are used for the assessment of criterion D6C5. However, in the absence of an operational indicator at the level of Descriptor 6 - Benthic Habitats, these results could not be taken into account in the assessment of D6C5.
|
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.
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Integration rule type parameter |
Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Integration rule description parameter |
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Integration rule type criteria |
Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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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 |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Description overall status |
The D7 assessment, based on data on anthropic activities, has highlighted significant variations in exposure to pressures:1/ The coastal zone is the most subject to exposure to the hydrographic pressures considered.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (100% of the Channel/North 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 medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
|
The D7 assessment, based on data on anthropic activities, has highlighted significant variations in exposure to pressures:1/ The coastal zone is the most subject to exposure to the hydrographic pressures considered.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (100% of the Channel/North 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 medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
|
The D7 assessment, based on data on anthropic activities, has highlighted significant variations in exposure to pressures:1/ The coastal zone is the most subject to exposure to the hydrographic pressures considered.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (100% of the Channel/North 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 medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
|
The D7 assessment, based on data on anthropic activities, has highlighted significant variations in exposure to pressures:1/ The coastal zone is the most subject to exposure to the hydrographic pressures considered.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (100% of the Channel/North 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 medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
|
The D7 assessment, based on data on anthropic activities, has highlighted significant variations in exposure to pressures:1/ The coastal zone is the most subject to exposure to the hydrographic pressures considered.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (100% of the Channel/North 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 medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
|
The D7 assessment, based on data on anthropic activities, has highlighted significant variations in exposure to pressures:1/ The coastal zone is the most subject to exposure to the hydrographic pressures considered.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (100% of the Channel/North 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 medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
|
The D7 assessment, based on data on anthropic activities, has highlighted significant variations in exposure to pressures:1/ The coastal zone is the most subject to exposure to the hydrographic pressures considered.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (100% of the Channel/North 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 medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
|
The D7 assessment, based on data on anthropic activities, has highlighted significant variations in exposure to pressures:1/ The coastal zone is the most subject to exposure to the hydrographic pressures considered.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (100% of the Channel/North 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 medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
|
The D7 assessment, based on data on anthropic activities, has highlighted significant variations in exposure to pressures:1/ The coastal zone is the most subject to exposure to the hydrographic pressures considered.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (100% of the Channel/North 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 medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
|
The D7 assessment, based on data on anthropic activities, has highlighted significant variations in exposure to pressures:1/ The coastal zone is the most subject to exposure to the hydrographic pressures considered.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (100% of the Channel/North 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 medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
|
The D7 assessment, based on data on anthropic activities, has highlighted significant variations in exposure to pressures:1/ The coastal zone is the most subject to exposure to the hydrographic pressures considered.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (100% of the Channel/North 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 medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
|
The D7 assessment, based on data on anthropic activities, has highlighted significant variations in exposure to pressures:1/ The coastal zone is the most subject to exposure to the hydrographic pressures considered.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (100% of the Channel/North 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 medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
|
The D7 assessment, based on data on anthropic activities, has highlighted significant variations in exposure to pressures:1/ The coastal zone is the most subject to exposure to the hydrographic pressures considered.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (100% of the Channel/North 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 medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
|
The D7 assessment, based on data on anthropic activities, has highlighted significant variations in exposure to pressures:1/ The coastal zone is the most subject to exposure to the hydrographic pressures considered.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (100% of the Channel/North 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 medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
|
The D7 assessment, based on data on anthropic activities, has highlighted significant variations in exposure to pressures:1/ The coastal zone is the most subject to exposure to the hydrographic pressures considered.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (100% of the Channel/North 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 medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
|
The D7 assessment, based on data on anthropic activities, has highlighted significant variations in exposure to pressures:1/ The coastal zone is the most subject to exposure to the hydrographic pressures considered.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (100% of the Channel/North 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 medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
|
The D7 assessment, based on data on anthropic activities, has highlighted significant variations in exposure to pressures:1/ The coastal zone is the most subject to exposure to the hydrographic pressures considered.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (100% of the Channel/North 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 medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures. Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
|
The D7 assessment, based on data on anthropic activities, has highlighted significant variations in exposure to pressures:1/ The coastal zone is the most subject to exposure to the hydrographic pressures considered.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (100% of the Channel/North 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 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 |
Related pressures |
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Related targets |
MMN Z200 (ANS-FR-MS-MMN-Z200)
GES component |
D7
|
D7
|
D7
|
D7
|
D7
|
D7
|
D7
|
D7
|
D7
|
D7
|
D7
|
D7
|
D7
|
D7
|
D7
|
D7
|
D7
|
D7
|
D7
|
D7
|
D7
|
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
Feature |
Hydrographical changes
|
Hydrographical changes
|
Hydrographical changes
|
Hydrographical changes
|
Hydrographical changes
|
Hydrographical changes
|
Hydrographical changes
|
Benthic broad habitats
|
Benthic broad habitats
|
Benthic broad habitats
|
Benthic broad habitats
|
Benthic broad habitats
|
Benthic broad habitats
|
Benthic broad habitats
|
Benthic broad habitats
|
Benthic broad habitats
|
Benthic broad habitats
|
Benthic broad habitats
|
Benthic broad habitats
|
Benthic broad habitats
|
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 mud |
Infralittoral rock and biogenic reef |
Infralittoral sand |
Offshore circalittoral coarse sediment |
Offshore circalittoral mixed sediment |
Offshore circalittoral mud |
Offshore circalittoral rock and biogenic reef |
Offshore circalittoral sand |
Element code |
ExpPresCurrents |
ExpPresSalinity |
ExpPresSeabedNature |
ExpPresTemperature |
ExpPresTide |
ExpPresTurbidity |
ExpPresWaves |
HabBenCircalitCoarSed |
HabBenCircalitMxdSed |
HabBenCircalitMud |
HabBenCircalitRock |
HabBenCircalitSand |
HabBenInfralitCoarSed |
HabBenInfralitMud |
HabBenInfralitRock |
HabBenInfralitSand |
HabBenOffshCoarSed |
HabBenOffshMxdSed |
HabBenOffshMud |
HabBenOffshRock |
HabBenOffshSand |
Element code source |
Link to other vocabulary or code lists that may be relevant
|
Link to other vocabulary or code lists that may be relevant
|
Link to other vocabulary or code lists that may be relevant
|
Link to other vocabulary or code lists that may be relevant
|
Link to other vocabulary or code lists that may be relevant
|
Link to other vocabulary or code lists that may be relevant
|
Link to other vocabulary or code lists that may be relevant
|
Habitats (D1-D6) http://dd.eionet.europa.eu/vocabulary/msfd/broadHabitatTypes/view
|
Habitats (D1-D6) http://dd.eionet.europa.eu/vocabulary/msfd/broadHabitatTypes/view
|
Habitats (D1-D6) http://dd.eionet.europa.eu/vocabulary/msfd/broadHabitatTypes/view
|
Habitats (D1-D6) http://dd.eionet.europa.eu/vocabulary/msfd/broadHabitatTypes/view
|
Habitats (D1-D6) http://dd.eionet.europa.eu/vocabulary/msfd/broadHabitatTypes/view
|
Habitats (D1-D6) http://dd.eionet.europa.eu/vocabulary/msfd/broadHabitatTypes/view
|
Habitats (D1-D6) http://dd.eionet.europa.eu/vocabulary/msfd/broadHabitatTypes/view
|
Habitats (D1-D6) http://dd.eionet.europa.eu/vocabulary/msfd/broadHabitatTypes/view
|
Habitats (D1-D6) http://dd.eionet.europa.eu/vocabulary/msfd/broadHabitatTypes/view
|
Habitats (D1-D6) http://dd.eionet.europa.eu/vocabulary/msfd/broadHabitatTypes/view
|
Habitats (D1-D6) http://dd.eionet.europa.eu/vocabulary/msfd/broadHabitatTypes/view
|
Habitats (D1-D6) http://dd.eionet.europa.eu/vocabulary/msfd/broadHabitatTypes/view
|
Habitats (D1-D6) http://dd.eionet.europa.eu/vocabulary/msfd/broadHabitatTypes/view
|
Habitats (D1-D6) http://dd.eionet.europa.eu/vocabulary/msfd/broadHabitatTypes/view
|
Element 2 |
|||||||||||||||||||||
Element 2 code |
|||||||||||||||||||||
Element 2 code source |
|||||||||||||||||||||
Element source |
National |
National |
National |
National |
National |
National |
National |
EU |
EU |
EU |
EU |
EU |
EU |
EU |
EU |
EU |
EU |
EU |
EU |
EU |
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 |
|||||||||||||||||||||
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 |
141.0 |
10.0 |
24590.0 |
10.0 |
7.0 |
24590.0 |
7.0 |
4743.0 |
3.4 |
58.0 |
58.4 |
1291.0 |
725.0 |
86.0 |
24.0 |
261.0 |
16828.0 |
110.0 |
52.0 |
48.0 |
288.0 |
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 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 141 km2 . The areas of exposure according to the four levels of exposure index are: No exposure: 24449 km² Low exposure index: 141 km² Medium exposure index: 0 km² High exposure index: 0 km² Note that no threshold is currently available to assess whether or not the parameter has been reached.
|
The metric considered for this parameter is the area of exposure for each pressure considered (overall or as a function of the level of the exposure index). The areas potentially affected by a change in salinity regime correspond to a total area of <10 km2 . The areas of exposure according to the four levels of exposure index are: No Exposure: 24590 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 24590 km2 . The areas of exposure according to the four levels of exposure index are: No Exposure: 0 km² Low Exposure Index: 24586 km² Medium Exposure Index: 3.4 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: 24590 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 7 km2 . The areas of exposure according to the four levels of exposure index are: No exposure: 24583 km² Low exposure index: 3.4 km² Medium exposure index: 3.4 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 24590 km2. The areas of exposure according to the four levels of exposure index are: No Exposure: 0 km² Low Exposure Index: 24208 km² Medium Exposure Index: 381 km² High Exposure Index: 0 km² Note that no threshold is currently available to assess whether or not the parameter has been reached.
|
The metric considered for this parameter is the area of exposure for each pressure considered (overall or as a function of the level of the exposure index). The areas potentially affected by a change in the wave regime correspond to a total area of 7 km2 . The areas of exposure according to the four levels of exposure index are: No Exposure: 24583 km² Low Exposure Index: 7 km² Medium Exposure Index: 0 km² High Exposure Index: 0 km² Note that no threshold is currently available to assess whether or not the parameter has been reached.
|
The metric considered for this parameter is the area of habitat potentially at risk (overall or based on the level of risk). The spatial extent of potential habitat alteration associated with permanent changes in hydrographic conditions in this MRU is 4743 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: 1243 km², medium risk of modification: 3500 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 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: 0 km².medium risk of modification: 3.4 km².high risk of modification: 0 km².It should be noted that no threshold is currently available to assess whether or not the parameter has been reached.
|
The metric considered for this parameter is the area of habitat potentially at risk (overall or based on the level of risk). The spatial extent of potential habitat alteration associated with permanent changes in hydrographic conditions in this MRU is 58 km2 (i.e., 100% of the assessed habitat). In addition, the indicator makes it possible to assess the intensity of the risk of modification: negligible or nil risk of modification: 0 km², low risk of modification: 3 km², medium risk of modification: 55 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 58.4 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: 13.7 km².medium risk of modification: 44.7 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 1291 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: 79 km², medium risk of modification: 1212 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 725 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: 120 km², medium risk of modification: 605 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 86 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: 86 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 24 km2 (i.e., 100% of the assessed habitat). In addition, the indicator makes it possible to assess the intensity of the risk of modification: negligible or nil risk of modification: 0 km², low risk of modification: 3 km², medium risk of modification: 21 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 261 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: 17 km², medium risk of modification: 244 km², high risk of modification: 0 km², it should be noted that no threshold is currently available to assess whether or not the parameter has been reached.
|
The metric considered for this parameter is the area of habitat potentially at risk (overall or based on the level of risk). The spatial extent of potential habitat alteration associated with permanent changes in hydrographic conditions in this MRU is 16828 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: 3836 km², medium risk of modification: 12985 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 110 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: 100 km², medium risk of modification: 10 km², high risk of modification: 0 km².
|
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). 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: 52 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 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 associated with permanent changes in hydrographic conditions in this MRU is 288 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: 17 km², medium risk of modification: 271 km², high risk of modification: 0 km², it should be noted that no threshold is currently available to assess whether or not the parameter has been reached.
|
Related indicator |
|||||||||||||||||||||
Criteria status |
Contributes to assessment of another criterion/ele |
Contributes to assessment of another criterion/ele |
Contributes to assessment of another criterion/ele |
Contributes to assessment of another criterion/ele |
Contributes to assessment of another criterion/ele |
Contributes to assessment of another criterion/ele |
Contributes to assessment of another criterion/ele |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
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 bottom nature, current, tidal, wave, turbidity, salinity, and thermal regime. Indeed, the results show that the pressures associated with a change in the current, tidal and wave regimes are generally local and affect the MRU-Z200 very little (less than 1% of the total area of the MRU). It should also be noted that the exposure indices calculated for the modification of the current regime are exclusively low, and mostly low for the modification of the wave regime. The pressures associated with a change in the thermal and salinity regimes each affect less than 1% of the MRU. On the other hand, pressures related to the modification of the bottom nature and turbidity regime potentially affect a very large area (100% of the MRU). It should also be noted that the exposure indices calculated for the modification of the nature of the bottom are mostly low, whereas for the modification of the turbidity regime, the proportion of surface area subject to a medium level exposure index is relatively high (20% of the total surface area 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 bottom nature, current, tidal, wave, turbidity, salinity, and thermal regime. Indeed, the results show that the pressures associated with a change in the current, tidal and wave regimes are generally local and affect the MRU-Z200 very little (less than 1% of the total area of the MRU). It should also be noted that the exposure indices calculated for the modification of the current regime are exclusively low, and mostly low for the modification of the wave regime. The pressures associated with a change in the thermal and salinity regimes each affect less than 1% of the MRU. On the other hand, pressures related to the modification of the bottom nature and turbidity regime potentially affect a very large area (100% of the MRU). It should also be noted that the exposure indices calculated for the modification of the nature of the bottom are mostly low, whereas for the modification of the turbidity regime, the proportion of surface area subject to a medium level exposure index is relatively high (20% of the total surface area 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 bottom nature, current, tidal, wave, turbidity, salinity, and thermal regime. Indeed, the results show that the pressures associated with a change in the current, tidal and wave regimes are generally local and affect the MRU-Z200 very little (less than 1% of the total area of the MRU). It should also be noted that the exposure indices calculated for the modification of the current regime are exclusively low, and mostly low for the modification of the wave regime. The pressures associated with a change in the thermal and salinity regimes each affect less than 1% of the MRU. On the other hand, pressures related to the modification of the bottom nature and turbidity regime potentially affect a very large area (100% of the MRU). It should also be noted that the exposure indices calculated for the modification of the nature of the bottom are mostly low, whereas for the modification of the turbidity regime, the proportion of surface area subject to a medium level exposure index is relatively high (20% of the total surface area 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 bottom nature, current, tidal, wave, turbidity, salinity, and thermal regime. Indeed, the results show that the pressures associated with a change in the current, tidal and wave regimes are generally local and affect the MRU-Z200 very little (less than 1% of the total area of the MRU). It should also be noted that the exposure indices calculated for the modification of the current regime are exclusively low, and mostly low for the modification of the wave regime. The pressures associated with a change in the thermal and salinity regimes each affect less than 1% of the MRU. On the other hand, pressures related to the modification of the bottom nature and turbidity regime potentially affect a very large area (100% of the MRU). It should also be noted that the exposure indices calculated for the modification of the nature of the bottom are mostly low, whereas for the modification of the turbidity regime, the proportion of surface area subject to a medium level exposure index is relatively high (20% of the total surface area 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 bottom nature, current, tidal, wave, turbidity, salinity, and thermal regime. Indeed, the results show that the pressures associated with a change in the current, tidal and wave regimes are generally local and affect the MRU-Z200 very little (less than 1% of the total area of the MRU). It should also be noted that the exposure indices calculated for the modification of the current regime are exclusively low, and mostly low for the modification of the wave regime. The pressures associated with a change in the thermal and salinity regimes each affect less than 1% of the MRU. On the other hand, pressures related to the modification of the bottom nature and turbidity regime potentially affect a very large area (100% of the MRU). It should also be noted that the exposure indices calculated for the modification of the nature of the bottom are mostly low, whereas for the modification of the turbidity regime, the proportion of surface area subject to a medium level exposure index is relatively high (20% of the total surface area 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 bottom nature, current, tidal, wave, turbidity, salinity, and thermal regime. Indeed, the results show that the pressures associated with a change in the current, tidal and wave regimes are generally local and affect the MRU-Z200 very little (less than 1% of the total area of the MRU). It should also be noted that the exposure indices calculated for the modification of the current regime are exclusively low, and mostly low for the modification of the wave regime. The pressures associated with a change in the thermal and salinity regimes each affect less than 1% of the MRU. On the other hand, pressures related to the modification of the bottom nature and turbidity regime potentially affect a very large area (100% of the MRU). It should also be noted that the exposure indices calculated for the modification of the nature of the bottom are mostly low, whereas for the modification of the turbidity regime, the proportion of surface area subject to a medium level exposure index is relatively high (20% of the total surface area 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 bottom nature, current, tidal, wave, turbidity, salinity, and thermal regime. Indeed, the results show that the pressures associated with a change in the current, tidal and wave regimes are generally local and affect the MRU-Z200 very little (less than 1% of the total area of the MRU). It should also be noted that the exposure indices calculated for the modification of the current regime are exclusively low, and mostly low for the modification of the wave regime. The pressures associated with a change in the thermal and salinity regimes each affect less than 1% of the MRU. On the other hand, pressures related to the modification of the bottom nature and turbidity regime potentially affect a very large area (100% of the MRU). It should also be noted that the exposure indices calculated for the modification of the nature of the bottom are mostly low, whereas for the modification of the turbidity regime, the proportion of surface area subject to a medium level exposure index is relatively high (20% of the total surface area of the MRU).
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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, 74% of the area of "coastal circalittoral coarse sediment 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 surface area of the "coastal circalittoral mixed sediment" habitat appears to be subject to an average 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, 94% of the surface area of the "Coastal circalittoral mud flats" habitat appears to be 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, 76% of the surface area of the habitat "Rocks and coastal circalittoral biogenic reefs" appears to be subject to an average 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 "Coastal circalittoral sands" habitat presents a significant area at medium risk (area at medium risk of 94% 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 "infralittoral coarse sediment" habitat presents a large area at medium risk (83% 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, 100% of the surface area of the "infralittoral mudflats" habitat appears to be 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, the "Rocks and biogenic infralittoral reefs" habitat presents a large area at medium risk (86% 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 "infralittoral sands" habitat presents a large area at medium risk (93% 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, 77% of the area of " circalittoral offshore 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 habitat "Mixed offshore circalittoral sediments" presents an area that is mostly at low risk (low risk area of 91% 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, 100% of the surface area of the " circalittoral offshore mud " habitat appears to be 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, 57% of the surface area of the habitat "Rocks and offshore circalittoral biogenic reefs" appears to be 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, 94% of the area of "offshore circalittoral sands" habitat appears to be at medium risk.
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Description element |
The assessment of criterion D7C1 contributes to the assessment of criterion D7C2. Thus, the accumulation of quantified pressures (i.e., exposure indices) under D7C1 is incorporated into the calculation of the risk of modification of each habitat for the D7C2 assessment.
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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 achieved |
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Description overall status |
The D7 assessment, based on data on anthropic activities, has 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 Channel/North Sea marine sub-region). However, the exposure index remains mostly low, and for 90% of the major types of benthic habitats, 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 D7 assessment, based on data on anthropic activities, has 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 Channel/North Sea marine sub-region). However, the exposure index remains mostly low, and for 90% of the major types of benthic habitats, 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 D7 assessment, based on data on anthropic activities, has 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 Channel/North Sea marine sub-region). However, the exposure index remains mostly low, and for 90% of the major types of benthic habitats, 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 D7 assessment, based on data on anthropic activities, has 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 Channel/North Sea marine sub-region). However, the exposure index remains mostly low, and for 90% of the major types of benthic habitats, 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 D7 assessment, based on data on anthropic activities, has 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 Channel/North Sea marine sub-region). However, the exposure index remains mostly low, and for 90% of the major types of benthic habitats, 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 D7 assessment, based on data on anthropic activities, has 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 Channel/North Sea marine sub-region). However, the exposure index remains mostly low, and for 90% of the major types of benthic habitats, 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 D7 assessment, based on data on anthropic activities, has 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 Channel/North Sea marine sub-region). However, the exposure index remains mostly low, and for 90% of the major types of benthic habitats, 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 D7 assessment, based on data on anthropic activities, has 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 Channel/North Sea marine sub-region). However, the exposure index remains mostly low, and for 90% of the major types of benthic habitats, 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 D7 assessment, based on data on anthropic activities, has 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 Channel/North Sea marine sub-region). However, the exposure index remains mostly low, and for 90% of the major types of benthic habitats, 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 D7 assessment, based on data on anthropic activities, has 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 Channel/North Sea marine sub-region). However, the exposure index remains mostly low, and for 90% of the major types of benthic habitats, 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 D7 assessment, based on data on anthropic activities, has 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 Channel/North Sea marine sub-region). However, the exposure index remains mostly low, and for 90% of the major types of benthic habitats, 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 D7 assessment, based on data on anthropic activities, has 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 Channel/North Sea marine sub-region). However, the exposure index remains mostly low, and for 90% of the major types of benthic habitats, 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 D7 assessment, based on data on anthropic activities, has 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 Channel/North Sea marine sub-region). However, the exposure index remains mostly low, and for 90% of the major types of benthic habitats, 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 D7 assessment, based on data on anthropic activities, has 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 Channel/North Sea marine sub-region). However, the exposure index remains mostly low, and for 90% of the major types of benthic habitats, 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 D7 assessment, based on data on anthropic activities, has 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 Channel/North Sea marine sub-region). However, the exposure index remains mostly low, and for 90% of the major types of benthic habitats, 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 D7 assessment, based on data on anthropic activities, has 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 Channel/North Sea marine sub-region). However, the exposure index remains mostly low, and for 90% of the major types of benthic habitats, 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 D7 assessment, based on data on anthropic activities, has 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 Channel/North Sea marine sub-region). However, the exposure index remains mostly low, and for 90% of the major types of benthic habitats, 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 D7 assessment, based on data on anthropic activities, has 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 Channel/North Sea marine sub-region). However, the exposure index remains mostly low, and for 90% of the major types of benthic habitats, 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 D7 assessment, based on data on anthropic activities, has 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 Channel/North Sea marine sub-region). However, the exposure index remains mostly low, and for 90% of the major types of benthic habitats, 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 D7 assessment, based on data on anthropic activities, has 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 Channel/North Sea marine sub-region). However, the exposure index remains mostly low, and for 90% of the major types of benthic habitats, 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 D7 assessment, based on data on anthropic activities, has 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 Channel/North Sea marine sub-region). However, the exposure index remains mostly low, and for 90% of the major types of benthic habitats, 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 |
2012-2018 |
2012-2018 |
2012-2018 |
2012-2018 |
Related pressures |
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Related targets |