Member State report / Art8 / 2018 / D7 / France / Mediterranean: Western Mediterranean 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 | Mediterranean: Western Mediterranean Sea |
Reported by | Ministère de la transition Ecologique et Solidaire |
Report date | 2020-02-19 |
Report access | ART8_GES_FR_2020-02-17.xml |
MO L200 (MWE-FR-MS-MO-L200)
GES component |
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
|
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 turbidity regime |
Changes in waves regime |
Circalittoral coarse sediment |
Circalittoral rock and biogenic reef |
Circalittoral sand |
Infralittoral coarse sediment |
Offshore circalittoral coarse sediment |
Offshore circalittoral mud |
Offshore circalittoral rock and biogenic reef |
Offshore circalittoral sand |
Element code |
ExpPresCurrents |
ExpPresSalinity |
ExpPresSeabedNature |
ExpPresTemperature |
ExpPresTurbidity |
ExpPresWaves |
HabBenCircalitCoarSed |
HabBenCircalitRock |
HabBenCircalitSand |
HabBenInfralitCoarSed |
HabBenOffshCoarSed |
HabBenOffshMud |
HabBenOffshRock |
HabBenOffshSand |
Element code source |
Link to other vocabulary or code lists that may be relevant
|
Link to other vocabulary or code lists that may be relevant
|
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
|
Element 2 |
||||||||||||||
Element 2 code |
||||||||||||||
Element 2 code source |
||||||||||||||
Element source |
National |
National |
National |
National |
National |
National |
EU |
EU |
EU |
EU |
EU |
EU |
EU |
EU |
Criterion |
D7C1
|
D7C1
|
D7C1
|
D7C1
|
D7C1
|
D7C1
|
D7C2
|
D7C2
|
D7C2
|
D7C2
|
D7C2
|
D7C2
|
D7C2
|
D7C2
|
Parameter |
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
|
Threshold value source |
||||||||||||||
Threshold value source other |
||||||||||||||
Value achieved upper |
||||||||||||||
Value achieved lower |
||||||||||||||
Value unit |
||||||||||||||
Value unit other |
||||||||||||||
Proportion threshold value |
||||||||||||||
Proportion value achieved |
10.0 |
4940.0 |
10.0 |
4940.0 |
14.0 |
23.0 |
471.0 |
126.0 |
||||||
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 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 |
Parameter achieved |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Description parameter |
The metric considered for this parameter is the area of exposure for each pressure considered (overall or according to the level of the exposure index). The areas potentially affected by a change in the current regime correspond to a total area of 0 km2 . The areas of exposure according to the four levels of exposure index are: No exposure: 104139 km² Low exposure index: 0 km² Medium exposure index: 0 km² High exposure index: 0 km² Note that no threshold is currently available to assess whether or not the parameter has been reached.
|
The metric considered for this parameter is the area of exposure for each pressure considered (overall or as a function of the level of the exposure index). The areas potentially affected by a change in salinity regime correspond to a total area of <10 km2 . The areas of exposure according to the four levels of exposure index are: No exposure: 104139 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 4940 km2 . The areas of exposure according to the four levels of exposure index are: No exposure: 99199 km² Low exposure index: 4940 km² Medium exposure index: 0 km² High exposure index: 0 km² Note that no threshold is currently available to assess whether or not the parameter has been reached.
|
The metric considered for this parameter is the area of exposure for each pressure considered (overall or as a function of the level of the exposure index). The areas potentially affected by a change in the thermal regime correspond to a total area of <10 km2 . The areas of exposure according to the four levels of exposure index are: No exposure: 104139 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 the turbidity regime correspond to a total area of 4940 km2 . The areas of exposure according to the four levels of exposure index are: No exposure: 99199 km² Low exposure index: 0 km² Medium exposure index: 4940 km² High exposure index: 0 km² Note that no threshold is currently available to assess whether or not the parameter has been reached.
|
The metric considered for this parameter is the area of exposure for each pressure considered (overall or as a function of the level of the exposure index). The areas potentially affected by a change in the wave regime correspond to a total area of 0 km2 . The areas of exposure according to the four levels of exposure index are: No Exposure: 104139 km² Low Exposure Index: 0 km² Medium Exposure Index: 0 km² High Exposure Index: 0 km² Note that no threshold is currently available to assess whether or not the parameter has been reached.
|
The metric considered for this parameter is the area of habitat potentially at risk (overall or based on the level of risk). The spatial extent of potential habitat alteration related to permanent changes in hydrographic conditions in this MRU is 0 km2 (i.e. 0% 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: 97 km².low risk of modification: 0 km².medium risk of modification: 0 km².high risk of modification: 0 km².It should be noted that no threshold is currently available to assess whether or not the parameter has been reached.
|
The metric considered for this parameter is the area of habitat potentially at risk (overall or based on the level of risk). The spatial extent of potential habitat alteration related to permanent changes in hydrographic conditions in this MRU is 0 km2 (i.e. 0% 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: 29 km², low risk of modification: 0 km², medium risk of modification: 0 km², high risk of modification: 0 km², and no threshold is currently available to assess whether or not the parameter has been reached.
|
The metric considered for this parameter is the area of habitat potentially at risk (overall or based on the level of risk). The spatial extent of potential habitat alteration associated with permanent changes in hydrographic conditions in this MRU is 14 km2 (or 17% 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: 69 km², low risk of modification: 0 km², medium risk of modification: 14 km², high risk of modification: 0 km², although no threshold is currently available to assess whether or not the parameter has been reached.
|
The metric considered for this parameter is the area of habitat potentially at risk (overall or based on the level of risk). The spatial extent of potential habitat alteration related to permanent changes in hydrographic conditions in this MRU is 0 km2 (i.e. 0% 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: 3 km², low risk of modification: 0 km², medium risk of modification: 0 km², high risk of modification: 0 km², and no threshold is currently available to assess whether or not the parameter has been reached.
|
The metric considered for this parameter is the area of habitat potentially at risk (overall or based on the level of risk). The spatial extent of potential habitat alteration associated with permanent changes in hydrographic conditions in this MRU is 23 km2 (or 44% 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: 29 km², low risk of modification: 0 km², medium risk of modification: 23 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 471 km2 (88% 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: 66 km², low risk of modification: 417 km², medium risk of modification: 55 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 0 km2 (i.e. 0% 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: 6 km², low risk of modification: 0 km², medium risk of modification: 0 km², high risk of modification: 0 km², and no threshold is currently available to assess whether or not the parameter has been reached.
|
The metric considered for this parameter is the area of habitat potentially at risk (overall or based on the level of risk). The spatial extent of potential habitat alteration related to permanent changes in hydrographic conditions in this MRU is 126 km2 (or 24% 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: 401 km².low risk of modification: 43 km².medium risk of modification: 84 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 |
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 changes in current, wave, background, turbidity, thermal and salinity regimes. Indeed, the results show that the pressures linked to a change in current and wave regime do not affect the wide area (0% of the total area of the MRU). Pressures related to a change in the bottom nature and turbidity regime potentially affect a small area (5% of the MRU). The exposure indices calculated for the change in background are exclusively low, and more important for the change in turbidity regime are exclusively medium. Finally, the pressures associated with a change in the thermal and salinity regime affect less than 1% of the MRU.
|
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017) no threshold is to be specified for D7C1: the status of the D7C1 criterion is therefore not reported. However, the assessment of the D7C1 criterion has provided a first estimate of the exposure indices for spatial areas potentially affected by changes in current, wave, background, turbidity, thermal and salinity regimes. Indeed, the results show that the pressures linked to a change in current and wave regime do not affect the wide area (0% of the total area of the MRU). Pressures related to a change in the bottom nature and turbidity regime potentially affect a small area (5% of the MRU). The exposure indices calculated for the change in background are exclusively low, and more important for the change in turbidity regime are exclusively medium. Finally, the pressures associated with a change in the thermal and salinity regime affect less than 1% of the MRU.
|
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017) no threshold is to be specified for D7C1: the status of the D7C1 criterion is therefore not reported. However, the assessment of the D7C1 criterion has provided a first estimate of the exposure indices for spatial areas potentially affected by changes in current, wave, background, turbidity, thermal and salinity regimes. Indeed, the results show that the pressures linked to a change in current and wave regime do not affect the wide area (0% of the total area of the MRU). Pressures related to a change in the bottom nature and turbidity regime potentially affect a small area (5% of the MRU). The exposure indices calculated for the change in background are exclusively low, and more important for the change in turbidity regime are exclusively medium. Finally, the pressures associated with a change in the thermal and salinity regime affect less than 1% of the MRU.
|
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017) no threshold is to be specified for D7C1: the status of the D7C1 criterion is therefore not reported. However, the assessment of the D7C1 criterion has provided a first estimate of the exposure indices for spatial areas potentially affected by changes in current, wave, background, turbidity, thermal and salinity regimes. Indeed, the results show that the pressures linked to a change in current and wave regime do not affect the wide area (0% of the total area of the MRU). Pressures related to a change in the bottom nature and turbidity regime potentially affect a small area (5% of the MRU). The exposure indices calculated for the change in background are exclusively low, and more important for the change in turbidity regime are exclusively medium. Finally, the pressures associated with a change in the thermal and salinity regime affect less than 1% of the MRU.
|
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017) no threshold is to be specified for D7C1: the status of the D7C1 criterion is therefore not reported. However, the assessment of the D7C1 criterion has provided a first estimate of the exposure indices for spatial areas potentially affected by changes in current, wave, background, turbidity, thermal and salinity regimes. Indeed, the results show that the pressures linked to a change in current and wave regime do not affect the wide area (0% of the total area of the MRU). Pressures related to a change in the bottom nature and turbidity regime potentially affect a small area (5% of the MRU). The exposure indices calculated for the change in background are exclusively low, and more important for the change in turbidity regime are exclusively medium. Finally, the pressures associated with a change in the thermal and salinity regime affect less than 1% of the MRU.
|
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017) no threshold is to be specified for D7C1: the status of the D7C1 criterion is therefore not reported. However, the assessment of the D7C1 criterion has provided a first estimate of the exposure indices for spatial areas potentially affected by changes in current, wave, background, turbidity, thermal and salinity regimes. Indeed, the results show that the pressures linked to a change in current and wave regime do not affect the wide area (0% of the total area of the MRU). Pressures related to a change in the bottom nature and turbidity regime potentially affect a small area (5% of the MRU). The exposure indices calculated for the change in background are exclusively low, and more important for the change in turbidity regime are exclusively medium. Finally, the pressures associated with a change in the thermal and salinity regime affect less than 1% of the MRU.
|
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017), the D7C2 assessment must be carried out for each habitat type that is affected by changing hydrographic conditions and the D7C2 results are not integrated. On the other hand, no threshold has been defined so far for the parameter "Extent" and therefore the status of D7C2 is not reported, but the assessment of D7C2 has provided a first estimate of the spatial extent of benthic habitats potentially subject to cumulative risks of alteration, based on the indices of exposure to hydrographic pressures generated by human activities. Thus, "Coastal circalittoral coarse sediment" habitat does not appear to be at risk of alteration in the broad zone (100% of the total habitat area at negligible or no 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 "Coastal circalittoral biogenic rocks and reefs" does not appear to be subject to a risk of alteration in the broad zone (100% of the total area of habitat subject to negligible or no 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, 17% of the total area of "Coastal circalittoral sands" habitat appears to be at medium risk.
|
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017), the D7C2 assessment must be carried out for each habitat type that is affected by changing hydrographic conditions and the D7C2 results are not integrated. On the other hand, no threshold has been defined so far for the parameter "Extent" and therefore the status of D7C2 is not reported, but the assessment of D7C2 has provided a first estimate of the spatial extent of benthic habitats potentially subject to cumulative risks of alteration, based on the indices of exposure to hydrographic pressures generated by human activities. Thus, the "infralittoral coarse sediment" habitat does not appear to be at risk of alteration in the broad zone (100% of the total area of habitat subject to negligible or no 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, 44% of the total area of offshore circalittoral coarse sediment habitat appears to be at low risk.
|
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017), the D7C2 assessment must be carried out for each habitat type that is affected by changing hydrographic conditions and the D7C2 results are not integrated. On the other hand, no threshold has been defined so far for the parameter "Extent" and therefore the status of D7C2 is not reported, but the assessment of D7C2 has provided a first estimate of the spatial extent of benthic habitats potentially subject to cumulative risks of alteration, based on the indices of exposure to hydrographic pressures generated by human activities. Thus, 10% of the total area of "offshore circalittoral mud flats" habitat appears to be at medium risk, and 78% at low risk.
|
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017), the D7C2 assessment must be carried out for each habitat type that is affected by changing hydrographic conditions and the D7C2 results are not integrated. On the other hand, no threshold has been defined so far for the parameter "Extent" and therefore the status of D7C2 is not reported, but the assessment of D7C2 has provided a first estimate of the spatial extent of benthic habitats potentially subject to cumulative risks of alteration, based on the indices of exposure to hydrographic pressures generated by human activities. For example, the habitat "circalittoral offshore biogenic rocks and reefs" does not appear to be at risk of alteration in the offshore area (100% of the total habitat area at negligible or no 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, 16% of the total area of offshore circalittoral sands habitat appears to be at medium risk and 8% at low risk.
|
Element status |
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.
|
In the absence of a threshold for the "Extent" parameter, the state of the habitat could not be provided. Furthermore, according to Decision 2017/848/EU, the results of the assessment of criterion D7C2 (estimated extent of adverse effects by habitat type in each assessment area) are used for the assessment of criterion D6C5. However, in the absence of an operational indicator at the level of Descriptor 6 - Benthic Habitats, these results could not be taken into account in the assessment of D6C5.
|
In the absence of a threshold for the "Extent" parameter, the state of the habitat could not be provided. Furthermore, according to Decision 2017/848/EU, the results of the assessment of criterion D7C2 (estimated extent of adverse effects by habitat type in each assessment area) are used for the assessment of criterion D6C5. However, in the absence of an operational indicator at the level of Descriptor 6 - Benthic Habitats, these results could not be taken into account in the assessment of D6C5.
|
In the absence of a threshold for the "Extent" parameter, the state of the habitat could not be provided. Furthermore, according to Decision 2017/848/EU, the results of the assessment of criterion D7C2 (estimated extent of adverse effects by habitat type in each assessment area) are used for the assessment of criterion D6C5. However, in the absence of an operational indicator at the level of Descriptor 6 - Benthic Habitats, these results could not be taken into account in the assessment of D6C5.
|
In the absence of a threshold for the "Extent" parameter, the state of the habitat could not be provided. Furthermore, according to Decision 2017/848/EU, the results of the assessment of criterion D7C2 (estimated extent of adverse effects by habitat type in each assessment area) are used for the assessment of criterion D6C5. However, in the absence of an operational indicator at the level of Descriptor 6 - Benthic Habitats, these results could not be taken into account in the assessment of D6C5.
|
In the absence of a threshold for the "Extent" parameter, the state of the habitat could not be provided. Furthermore, according to Decision 2017/848/EU, the results of the assessment of criterion D7C2 (estimated extent of adverse effects by habitat type in each assessment area) are used for the assessment of criterion D6C5. However, in the absence of an operational indicator at the level of Descriptor 6 - Benthic Habitats, these results could not be taken into account in the assessment of D6C5.
|
In the absence of a threshold for the "Extent" parameter, the state of the habitat could not be provided. Furthermore, according to Decision 2017/848/EU, the results of the assessment of criterion D7C2 (estimated extent of adverse effects by habitat type in each assessment area) are used for the assessment of criterion D6C5. However, in the absence of an operational indicator at the level of Descriptor 6 - Benthic Habitats, these results could not be taken into account in the assessment of D6C5.
|
In the absence of a threshold for the "Extent" parameter, the state of the habitat could not be provided. Furthermore, according to Decision 2017/848/EU, the results of the assessment of criterion D7C2 (estimated extent of adverse effects by habitat type in each assessment area) are used for the assessment of criterion D6C5. However, in the absence of an operational indicator at the level of Descriptor 6 - Benthic Habitats, these results could not be taken into account in the assessment of D6C5.
|
In the absence of a threshold for the "Extent" parameter, the state of the habitat could not be provided. Furthermore, according to Decision 2017/848/EU, the results of the assessment of criterion D7C2 (estimated extent of adverse effects by habitat type in each assessment area) are used for the assessment of criterion D6C5. However, in the absence of an operational indicator at the level of Descriptor 6 - Benthic Habitats, these results could not be taken into account in the assessment of D6C5.
|
Integration rule type parameter |
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Integration rule description parameter |
||||||||||||||
Integration rule type criteria |
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Integration rule description criteria |
||||||||||||||
GES extent threshold |
||||||||||||||
GES extent achieved |
||||||||||||||
GES extent unit |
||||||||||||||
GES achieved |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Description overall status |
The assessment of D7, based on data on anthropogenic activities, has highlighted significant variations in exposure to pressures:1/ The wide area is the least subject to exposure to the hydrographic pressures considered.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (15% of the Western Mediterranean marine sub-region). However, the exposure index remains mostly low.3/ For 70% of the major benthic habitat types, the area of habitat potentially subject to a medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures.4/ Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
|
The assessment of D7, based on data on anthropogenic activities, has highlighted significant variations in exposure to pressures:1/ The wide area is the least subject to exposure to the hydrographic pressures considered.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (15% of the Western Mediterranean marine sub-region). However, the exposure index remains mostly low.3/ For 70% of the major benthic habitat types, the area of habitat potentially subject to a medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures.4/ Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
|
The assessment of D7, based on data on anthropogenic activities, has highlighted significant variations in exposure to pressures:1/ The wide area is the least subject to exposure to the hydrographic pressures considered.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (15% of the Western Mediterranean marine sub-region). However, the exposure index remains mostly low.3/ For 70% of the major benthic habitat types, the area of habitat potentially subject to a medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures.4/ Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
|
The assessment of D7, based on data on anthropogenic activities, has highlighted significant variations in exposure to pressures:1/ The wide area is the least subject to exposure to the hydrographic pressures considered.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (15% of the Western Mediterranean marine sub-region). However, the exposure index remains mostly low.3/ For 70% of the major benthic habitat types, the area of habitat potentially subject to a medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures.4/ Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
|
The assessment of D7, based on data on anthropogenic activities, has highlighted significant variations in exposure to pressures:1/ The wide area is the least subject to exposure to the hydrographic pressures considered.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (15% of the Western Mediterranean marine sub-region). However, the exposure index remains mostly low.3/ For 70% of the major benthic habitat types, the area of habitat potentially subject to a medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures.4/ Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
|
The assessment of D7, based on data on anthropogenic activities, has highlighted significant variations in exposure to pressures:1/ The wide area is the least subject to exposure to the hydrographic pressures considered.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (15% of the Western Mediterranean marine sub-region). However, the exposure index remains mostly low.3/ For 70% of the major benthic habitat types, the area of habitat potentially subject to a medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures.4/ Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
|
The assessment of D7, based on data on anthropogenic activities, has highlighted significant variations in exposure to pressures:1/ The wide area is the least subject to exposure to the hydrographic pressures considered.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (15% of the Western Mediterranean marine sub-region). However, the exposure index remains mostly low.3/ For 70% of the major benthic habitat types, the area of habitat potentially subject to a medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures.4/ Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
|
The assessment of D7, based on data on anthropogenic activities, has highlighted significant variations in exposure to pressures:1/ The wide area is the least subject to exposure to the hydrographic pressures considered.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (15% of the Western Mediterranean marine sub-region). However, the exposure index remains mostly low.3/ For 70% of the major benthic habitat types, the area of habitat potentially subject to a medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures.4/ Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
|
The assessment of D7, based on data on anthropogenic activities, has highlighted significant variations in exposure to pressures:1/ The wide area is the least subject to exposure to the hydrographic pressures considered.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (15% of the Western Mediterranean marine sub-region). However, the exposure index remains mostly low.3/ For 70% of the major benthic habitat types, the area of habitat potentially subject to a medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures.4/ Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
|
The assessment of D7, based on data on anthropogenic activities, has highlighted significant variations in exposure to pressures:1/ The wide area is the least subject to exposure to the hydrographic pressures considered.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (15% of the Western Mediterranean marine sub-region). However, the exposure index remains mostly low.3/ For 70% of the major benthic habitat types, the area of habitat potentially subject to a medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures.4/ Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
|
The assessment of D7, based on data on anthropogenic activities, has highlighted significant variations in exposure to pressures:1/ The wide area is the least subject to exposure to the hydrographic pressures considered.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (15% of the Western Mediterranean marine sub-region). However, the exposure index remains mostly low.3/ For 70% of the major benthic habitat types, the area of habitat potentially subject to a medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures.4/ Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
|
The assessment of D7, based on data on anthropogenic activities, has highlighted significant variations in exposure to pressures:1/ The wide area is the least subject to exposure to the hydrographic pressures considered.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (15% of the Western Mediterranean marine sub-region). However, the exposure index remains mostly low.3/ For 70% of the major benthic habitat types, the area of habitat potentially subject to a medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures.4/ Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
|
The assessment of D7, based on data on anthropogenic activities, has highlighted significant variations in exposure to pressures:1/ The wide area is the least subject to exposure to the hydrographic pressures considered.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (15% of the Western Mediterranean marine sub-region). However, the exposure index remains mostly low.3/ For 70% of the major benthic habitat types, the area of habitat potentially subject to a medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures.4/ Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
|
The assessment of D7, based on data on anthropogenic activities, has highlighted significant variations in exposure to pressures:1/ The wide area is the least subject to exposure to the hydrographic pressures considered.2/ The modification pressures of "turbidity" and "bottom nature" present the largest potential areas of exposure (15% of the Western Mediterranean marine sub-region). However, the exposure index remains mostly low.3/ For 70% of the major benthic habitat types, the area of habitat potentially subject to a medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures.4/ 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 |
Related pressures |
||||||||||||||
Related targets |
MO MEC DCE (MWE-FR-MS-MO-MEC2010)
GES component |
D7
|
D7
|
D7
|
D7
|
D7
|
D7
|
D7
|
D7
|
D7
|
D7
|
D7
|
D7
|
D7
|
D7
|
D7
|
D7
|
D7
|
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
Feature |
Hydrographical changes
|
Hydrographical changes
|
Hydrographical changes
|
Hydrographical changes
|
Hydrographical changes
|
Hydrographical changes
|
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 turbidity regime |
Changes in waves regime |
Circalittoral coarse sediment |
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 mud |
Offshore circalittoral rock and biogenic reef |
Offshore circalittoral sand |
Element code |
ExpPresCurrents |
ExpPresSalinity |
ExpPresSeabedNature |
ExpPresTemperature |
ExpPresTurbidity |
ExpPresWaves |
HabBenCircalitCoarSed |
HabBenCircalitRock |
HabBenCircalitSand |
HabBenInfralitCoarSed |
HabBenInfralitMud |
HabBenInfralitRock |
HabBenInfralitSand |
HabBenOffshCoarSed |
HabBenOffshMud |
HabBenOffshRock |
HabBenOffshSand |
Element code source |
Link to other vocabulary or code lists that may be relevant
|
Link to other vocabulary or code lists that may be relevant
|
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
|
Element 2 |
|||||||||||||||||
Element 2 code |
|||||||||||||||||
Element 2 code source |
|||||||||||||||||
Element source |
National |
National |
National |
National |
National |
National |
EU |
EU |
EU |
EU |
EU |
EU |
EU |
EU |
EU |
EU |
EU |
Criterion |
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
|
Parameter other |
|||||||||||||||||
Threshold value upper |
|||||||||||||||||
Threshold value lower |
|||||||||||||||||
Threshold qualitative |
Not available yet
|
Not available yet
|
Not available yet
|
Not available yet
|
Not available yet
|
Not available yet
|
Not available yet
|
Not available yet
|
Not available yet
|
Not available yet
|
Not available yet
|
Not available yet
|
Not available yet
|
Not available yet
|
Not available yet
|
Not available yet
|
Not available yet
|
Threshold value source |
|||||||||||||||||
Threshold value source other |
|||||||||||||||||
Value achieved upper |
|||||||||||||||||
Value achieved lower |
|||||||||||||||||
Value unit |
|||||||||||||||||
Value unit other |
|||||||||||||||||
Proportion threshold value |
|||||||||||||||||
Proportion value achieved |
972.0 |
10.0 |
2534.0 |
10.0 |
5131.0 |
837.0 |
242.0 |
20.0 |
527.0 |
52.0 |
35.0 |
454.0 |
403.0 |
11.0 |
551.0 |
6.0 |
69.0 |
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 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 |
Parameter achieved |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Description parameter |
The metric considered for this parameter is the area of exposure for each pressure considered (overall or as a function of the level of the exposure index). The areas potentially affected by a change in the current regime correspond to a total area of 972 km2 . The areas of exposure according to the four levels of exposure index are: No exposure: 4156 km² Low exposure index: 618 km² Medium exposure index: 314 km² High exposure index: 41 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: 5129 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 2534 km2 . The areas of exposure according to the four levels of exposure index are: No Exposure: 2594 km² Low Exposure Index: 2168 km² Medium Exposure Index: 367 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: 5129 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 the turbidity regime correspond to a total area of 5131 km2 . The areas of exposure according to the four levels of exposure index are: No exposure: 3059 km² Low exposure index: 0 km² Medium exposure index: 4940 km² High exposure index: 191 km² 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 837 km2 . The areas of exposure according to the four levels of exposure index are: No Exposure: 4291 km² Low Exposure Index: 759 km² Medium Exposure Index: 78 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 242 km2 (33% 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: 495 km².low risk of modification: 3 km².medium risk of modification: 225 km².high risk of modification: 14 km².It should be noted that no threshold is currently available to assess whether or not the parameter has been reached.
|
The metric considered for this parameter is the area of habitat potentially at risk (overall or based on the level of risk). The spatial extent of potential habitat alteration associated with permanent changes in hydrographic conditions in this MRU is 20 km2 (or 44% 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: 26 km².low risk of modification: 17 km².medium risk of modification: 3 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 527 km2 (69% 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: 241 km².low risk of modification: 6 km².medium risk of modification: 418 km².high risk of modification: 104 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 51 km2 (i.e., 32% 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: 108 km².low risk of modification: 0 km².medium risk of modification: 34 km².high risk of modification: 17 km².It should be noted that no threshold is currently available to assess whether or not the parameter has been reached.
|
The metric considered for this parameter is the area of 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 35 km2 (i.e., 80% of the habitat assessed). In addition, the indicator makes it possible to assess the intensity of the risk of modification: negligible or no risk of modification: 9 km².low risk of modification: 9 km².medium risk of modification: 0 km².high risk of modification: 26 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 454 km2 (or 51% 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: 428 km².low risk of modification: 210 km².medium risk of modification: 109 km².high risk of modification: 135 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 403 km2 (or 82% 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: 92 km², low risk of modification: 169 km², medium risk of modification: 29 km², high risk of modification: 205 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 11 km2 (or 44% 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: 14 km², low risk of modification: 6 km², medium risk of modification: 3 km², high risk of modification: 3 km², although no threshold is currently available to assess whether or not the parameter has been reached.
|
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 551 km2 (or 84% 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: 109 km².low risk of modification: 138 km².medium risk of modification: 378 km².high risk of modification: 35 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 6 km2 (i.e., 100% of the assessed habitat). In addition, the indicator makes it possible to assess the intensity of the risk of modification: negligible or nil risk of modification: 0 km², low risk of modification: 0 km², medium risk of modification: 6 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 69 km2 (or 24% 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: 218 km².low risk of modification: 29 km².medium risk of modification: 32 km².high risk of modification: 9 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 |
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 changes in current, wave, background, turbidity, thermal and salinity regimes. Indeed, the results show that the pressures linked to a modification of the current and wave regime are relatively low (< 1% of the Western Mediterranean marine sub-region) and fairly localised since they are almost exclusively located in the coastal zone (18% and 16% of the MRU respectively). It should also be noted that the exposure indices calculated for these pressures are mostly low. Pressures linked to a change in the background and turbidity regime potentially affect a large area (respectively 49% and 40% of the MRU area). Exposure indices calculated for the change in background are mostly low, and higher for the change in turbidity regime (>36% of the MRU area is subject to an average exposure index). Finally, the pressures associated with a change in the thermal and salinity regime affect less than 1% of the MRU.
|
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017) no threshold is to be specified for D7C1: the status of the D7C1 criterion is therefore not reported. However, the assessment of the D7C1 criterion has provided a first estimate of the exposure indices for spatial areas potentially affected by changes in current, wave, background, turbidity, thermal and salinity regimes. Indeed, the results show that the pressures linked to a modification of the current and wave regime are relatively low (< 1% of the Western Mediterranean marine sub-region) and fairly localised since they are almost exclusively located in the coastal zone (18% and 16% of the MRU respectively). It should also be noted that the exposure indices calculated for these pressures are mostly low. Pressures linked to a change in the background and turbidity regime potentially affect a large area (respectively 49% and 40% of the MRU area). Exposure indices calculated for the change in background are mostly low, and higher for the change in turbidity regime (>36% of the MRU area is subject to an average exposure index). Finally, the pressures associated with a change in the thermal and salinity regime affect less than 1% of the MRU.
|
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017) no threshold is to be specified for D7C1: the status of the D7C1 criterion is therefore not reported. However, the assessment of the D7C1 criterion has provided a first estimate of the exposure indices for spatial areas potentially affected by changes in current, wave, background, turbidity, thermal and salinity regimes. Indeed, the results show that the pressures linked to a modification of the current and wave regime are relatively low (< 1% of the Western Mediterranean marine sub-region) and fairly localised since they are almost exclusively located in the coastal zone (18% and 16% of the MRU respectively). It should also be noted that the exposure indices calculated for these pressures are mostly low. Pressures linked to a change in the background and turbidity regime potentially affect a large area (respectively 49% and 40% of the MRU area). Exposure indices calculated for the change in background are mostly low, and higher for the change in turbidity regime (>36% of the MRU area is subject to an average exposure index). Finally, the pressures associated with a change in the thermal and salinity regime affect less than 1% of the MRU.
|
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017) no threshold is to be specified for D7C1: the status of the D7C1 criterion is therefore not reported. However, the assessment of the D7C1 criterion has provided a first estimate of the exposure indices for spatial areas potentially affected by changes in current, wave, background, turbidity, thermal and salinity regimes. Indeed, the results show that the pressures linked to a modification of the current and wave regime are relatively low (< 1% of the Western Mediterranean marine sub-region) and fairly localised since they are almost exclusively located in the coastal zone (18% and 16% of the MRU respectively). It should also be noted that the exposure indices calculated for these pressures are mostly low. Pressures linked to a change in the background and turbidity regime potentially affect a large area (respectively 49% and 40% of the MRU area). Exposure indices calculated for the change in background are mostly low, and higher for the change in turbidity regime (>36% of the MRU area is subject to an average exposure index). Finally, the pressures associated with a change in the thermal and salinity regime affect less than 1% of the MRU.
|
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017) no threshold is to be specified for D7C1: the status of the D7C1 criterion is therefore not reported. However, the assessment of the D7C1 criterion has provided a first estimate of the exposure indices for spatial areas potentially affected by changes in current, wave, background, turbidity, thermal and salinity regimes. Indeed, the results show that the pressures linked to a modification of the current and wave regime are relatively low (< 1% of the Western Mediterranean marine sub-region) and fairly localised since they are almost exclusively located in the coastal zone (18% and 16% of the MRU respectively). It should also be noted that the exposure indices calculated for these pressures are mostly low. Pressures linked to a change in the background and turbidity regime potentially affect a large area (respectively 49% and 40% of the MRU area). Exposure indices calculated for the change in background are mostly low, and higher for the change in turbidity regime (>36% of the MRU area is subject to an average exposure index). Finally, the pressures associated with a change in the thermal and salinity regime affect less than 1% of the MRU.
|
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017) no threshold is to be specified for D7C1: the status of the D7C1 criterion is therefore not reported. However, the assessment of the D7C1 criterion has provided a first estimate of the exposure indices for spatial areas potentially affected by changes in current, wave, background, turbidity, thermal and salinity regimes. Indeed, the results show that the pressures linked to a modification of the current and wave regime are relatively low (< 1% of the Western Mediterranean marine sub-region) and fairly localised since they are almost exclusively located in the coastal zone (18% and 16% of the MRU respectively). It should also be noted that the exposure indices calculated for these pressures are mostly low. Pressures linked to a change in the background and turbidity regime potentially affect a large area (respectively 49% and 40% of the MRU area). Exposure indices calculated for the change in background are mostly low, and higher for the change in turbidity regime (>36% of the MRU area is subject to an average exposure index). Finally, the pressures associated with a change in the thermal and salinity regime affect less than 1% of the MRU.
|
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017), the D7C2 assessment must be carried out for each habitat type that is affected by changing hydrographic conditions and the D7C2 results are not integrated. On the other hand, no threshold has been defined so far for the parameter "Extent" and therefore the status of D7C2 is not reported, but the assessment of D7C2 has provided a first estimate of the spatial extent of benthic habitats potentially subject to cumulative risks of alteration, based on the indices of exposure to hydrographic pressures generated by human activities. Thus, 31% of the area of "coastal circalittoral coarse sediment sediment" habitat appears to be subject to a medium risk and 2% to a high risk.
|
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017), the D7C2 assessment must be carried out for each habitat type that is affected by changing hydrographic conditions and the D7C2 results are not integrated. On the other hand, no threshold has been defined so far for the parameter "Extent" and therefore the status of D7C2 is not reported, but the assessment of D7C2 has provided a first estimate of the spatial extent of benthic habitats potentially subject to cumulative risks of alteration, based on the indices of exposure to hydrographic pressures generated by human activities.Thus, 6% of the surface area of the "Coastal circalittoral biogenic rocks and reefs" habitat appears to be subject to a medium risk and 38% to a low risk.
|
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017), the D7C2 assessment must be carried out for each habitat type that is affected by changing hydrographic conditions and the D7C2 results are not integrated. On the other hand, no threshold has been defined so far for the parameter "Extent" and therefore the status of D7C2 is not reported, but the assessment of D7C2 has provided a first estimate of the spatial extent of benthic habitats potentially subject to cumulative risks of alteration, based on the indices of exposure to hydrographic pressures generated by human activities. Thus, 13.5% of the total area of "Coastal circalittoral sands" habitat appears to be at high risk and over 54% at medium risk.
|
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017), the D7C2 assessment must be carried out for each habitat type that is affected by changing hydrographic conditions and the D7C2 results are not integrated. On the other hand, no threshold has been defined so far for the parameter "Extent" and therefore the status of D7C2 is not reported, but the assessment of D7C2 has provided a first estimate of the spatial extent of benthic habitats potentially subject to cumulative risks of alteration, based on the indices of exposure to hydrographic pressures generated by human activities. Thus, the "infralittoral coarse sediment" habitat presents a high-risk area of 11.7% of the total habitat area and a medium-risk area of 21.6% of the habitat.
|
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017), the D7C2 assessment must be carried out for each habitat type that is affected by changing hydrographic conditions and the D7C2 results are not integrated. On the other hand, no threshold has been defined so far for the parameter "Extent" and therefore the status of D7C2 is not reported, but the assessment of D7C2 has provided a first estimate of the spatial extent of benthic habitats potentially subject to cumulative risks of alteration, based on the indices of exposure to hydrographic pressures generated by human activities. Thus, the "infralittoral mud flats" habitat presents the largest area at high risk (60% of the total habitat area), and 20% at low risk.
|
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017), the D7C2 assessment must be carried out for each habitat type that is affected by changing hydrographic conditions and the D7C2 results are not integrated. On the other hand, no threshold has been defined so far for the parameter "Extent" and therefore the status of D7C2 is not reported, but the assessment of D7C2 has provided a first estimate of the spatial extent of benthic habitats potentially subject to cumulative risks of alteration, based on the indices of exposure to hydrographic pressures generated by human activities. Thus, the "Rocks and biogenic infralittoral reefs" habitat presents a large area at high risk (15% of the total habitat area), and 12% at medium risk.
|
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017), the D7C2 assessment must be carried out for each habitat type that is affected by changing hydrographic conditions and the D7C2 results are not integrated. On the other hand, no threshold has been defined so far for the parameter "Extent" and therefore the status of D7C2 is not reported, but the assessment of D7C2 has provided a first estimate of the spatial extent of benthic habitats potentially subject to cumulative risks of alteration, based on the indices of exposure to hydrographic pressures generated by human activities. Thus, the "infralittoral sands" habitat presents one of the largest areas at high risk (41.5% 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, 11% of the area of "offshore circalittoral coarse sediment" habitat appears to be at high risk, 11% at medium risk and 22% at low risk.
|
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017), the D7C2 assessment must be carried out for each habitat type that is affected by changing hydrographic conditions and the D7C2 results are not integrated. On the other hand, no threshold has been defined so far for the parameter "Extent" and therefore the status of D7C2 is not reported, but the assessment of D7C2 has provided a first estimate of the spatial extent of benthic habitats potentially subject to cumulative risks of alteration, based on the indices of exposure to hydrographic pressures generated by human activities. Thus, the majority of "offshore mud" habitat appears to be at medium risk (57% of the habitat area), with 5% 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, 100% of the total area of "offshore circalittoral biogenic rock and reef" habitat appears to be at medium risk.
|
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017), the D7C2 assessment must be carried out for each habitat type that is affected by changing hydrographic conditions and the D7C2 results are not integrated. On the other hand, no threshold has been defined so far for the parameter "Extent" and therefore the status of D7C2 is not reported, but the assessment of D7C2 has provided a first estimate of the spatial extent of benthic habitats potentially subject to cumulative risks of alteration, based on the indices of exposure to hydrographic pressures generated by human activities. Thus, 3% of the area of "offshore circalittoral sands" habitat appears to be at high risk, 11% at medium risk and 10% at low risk.
|
Element status |
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.
|
In the absence of a threshold for the "Extent" parameter, the state of the habitat could not be provided. Furthermore, according to Decision 2017/848/EU, the results of the assessment of criterion D7C2 (estimated extent of adverse effects by habitat type in each assessment area) are used for the assessment of criterion D6C5. However, in the absence of an operational indicator at the level of Descriptor 6 - Benthic Habitats, these results could not be taken into account in the assessment of D6C5.
|
In the absence of a threshold for the "Extent" parameter, the state of the habitat could not be provided. Furthermore, according to Decision 2017/848/EU, the results of the assessment of criterion D7C2 (estimated extent of adverse effects by habitat type in each assessment area) are used for the assessment of criterion D6C5. However, in the absence of an operational indicator at the level of Descriptor 6 - Benthic Habitats, these results could not be taken into account in the assessment of D6C5.
|
In the absence of a threshold for the "Extent" parameter, the state of the habitat could not be provided. Furthermore, according to Decision 2017/848/EU, the results of the assessment of criterion D7C2 (estimated extent of adverse effects by habitat type in each assessment area) are used for the assessment of criterion D6C5. However, in the absence of an operational indicator at the level of Descriptor 6 - Benthic Habitats, these results could not be taken into account in the assessment of D6C5.
|
In the absence of a threshold for the "Extent" parameter, the state of the habitat could not be provided. Furthermore, according to Decision 2017/848/EU, the results of the assessment of criterion D7C2 (estimated extent of adverse effects by habitat type in each assessment area) are used for the assessment of criterion D6C5. However, in the absence of an operational indicator at the level of Descriptor 6 - Benthic Habitats, these results could not be taken into account in the assessment of D6C5.
|
In the absence of a threshold for the "Extent" parameter, the state of the habitat could not be provided. Furthermore, according to Decision 2017/848/EU, the results of the assessment of criterion D7C2 (estimated extent of adverse effects by habitat type in each assessment area) are used for the assessment of criterion D6C5. However, in the absence of an operational indicator at the level of Descriptor 6 - Benthic Habitats, these results could not be taken into account in the assessment of D6C5.
|
In the absence of a threshold for the "Extent" parameter, the state of the habitat could not be provided. Furthermore, according to Decision 2017/848/EU, the results of the assessment of criterion D7C2 (estimated extent of adverse effects by habitat type in each assessment area) are used for the assessment of criterion D6C5. However, in the absence of an operational indicator at the level of Descriptor 6 - Benthic Habitats, these results could not be taken into account in the assessment of D6C5.
|
In the absence of a threshold for the "Extent" parameter, the state of the habitat could not be provided. Furthermore, according to Decision 2017/848/EU, the results of the assessment of criterion D7C2 (estimated extent of adverse effects by habitat type in each assessment area) are used for the assessment of criterion D6C5. However, in the absence of an operational indicator at the level of Descriptor 6 - Benthic Habitats, these results could not be taken into account in the assessment of D6C5.
|
In the absence of a threshold for the "Extent" parameter, the state of the habitat could not be provided. Furthermore, according to Decision 2017/848/EU, the results of the assessment of criterion D7C2 (estimated extent of adverse effects by habitat type in each assessment area) are used for the assessment of criterion D6C5. However, in the absence of an operational indicator at the level of Descriptor 6 - Benthic Habitats, these results could not be taken into account in the assessment of D6C5.
|
In the absence of a threshold for the "Extent" parameter, the state of the habitat could not be provided. Furthermore, according to Decision 2017/848/EU, the results of the assessment of criterion D7C2 (estimated extent of adverse effects by habitat type in each assessment area) are used for the assessment of criterion D6C5. However, in the absence of an operational indicator at the level of Descriptor 6 - Benthic Habitats, these results could not be taken into account in the assessment of D6C5.
|
In the absence of a threshold for the "Extent" parameter, the state of the habitat could not be provided. Furthermore, according to Decision 2017/848/EU, the results of the assessment of criterion D7C2 (estimated extent of adverse effects by habitat type in each assessment area) are used for the assessment of criterion D6C5. However, in the absence of an operational indicator at the level of Descriptor 6 - Benthic Habitats, these results could not be taken into account in the assessment of D6C5.
|
In the absence of a threshold for the "Extent" parameter, the state of the habitat could not be provided. Furthermore, according to Decision 2017/848/EU, the results of the assessment of criterion D7C2 (estimated extent of adverse effects by habitat type in each assessment area) are used for the assessment of criterion D6C5. However, in the absence of an operational indicator at the level of Descriptor 6 - Benthic Habitats, these results could not be taken into account in the assessment of D6C5.
|
Integration rule type parameter |
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Integration rule description parameter |
|||||||||||||||||
Integration rule type criteria |
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Integration rule description criteria |
|||||||||||||||||
GES extent threshold |
|||||||||||||||||
GES extent achieved |
|||||||||||||||||
GES extent unit |
|||||||||||||||||
GES achieved |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Description overall status |
The D7 assessment, based on data on anthropogenic activities, highlighted significant variations in exposure to pressures:1/ The coastal zone and the plateau area are 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 (15% of the Western Mediterranean marine sub-region). However, the exposure index remains mostly low.3/ For 70% of the major benthic habitat types, the area of habitat potentially subject to a medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures.4/ Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
|
The D7 assessment, based on data on anthropogenic activities, highlighted significant variations in exposure to pressures:1/ The coastal zone and the plateau area are 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 (15% of the Western Mediterranean marine sub-region). However, the exposure index remains mostly low.3/ For 70% of the major benthic habitat types, the area of habitat potentially subject to a medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures.4/ Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
|
The D7 assessment, based on data on anthropogenic activities, highlighted significant variations in exposure to pressures:1/ The coastal zone and the plateau area are 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 (15% of the Western Mediterranean marine sub-region). However, the exposure index remains mostly low.3/ For 70% of the major benthic habitat types, the area of habitat potentially subject to a medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures.4/ Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
|
The D7 assessment, based on data on anthropogenic activities, highlighted significant variations in exposure to pressures:1/ The coastal zone and the plateau area are 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 (15% of the Western Mediterranean marine sub-region). However, the exposure index remains mostly low.3/ For 70% of the major benthic habitat types, the area of habitat potentially subject to a medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures.4/ Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
|
The D7 assessment, based on data on anthropogenic activities, highlighted significant variations in exposure to pressures:1/ The coastal zone and the plateau area are 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 (15% of the Western Mediterranean marine sub-region). However, the exposure index remains mostly low.3/ For 70% of the major benthic habitat types, the area of habitat potentially subject to a medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures.4/ Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
|
The D7 assessment, based on data on anthropogenic activities, highlighted significant variations in exposure to pressures:1/ The coastal zone and the plateau area are 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 (15% of the Western Mediterranean marine sub-region). However, the exposure index remains mostly low.3/ For 70% of the major benthic habitat types, the area of habitat potentially subject to a medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures.4/ Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
|
The D7 assessment, based on data on anthropogenic activities, highlighted significant variations in exposure to pressures:1/ The coastal zone and the plateau area are 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 (15% of the Western Mediterranean marine sub-region). However, the exposure index remains mostly low.3/ For 70% of the major benthic habitat types, the area of habitat potentially subject to a medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures.4/ Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
|
The D7 assessment, based on data on anthropogenic activities, highlighted significant variations in exposure to pressures:1/ The coastal zone and the plateau area are 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 (15% of the Western Mediterranean marine sub-region). However, the exposure index remains mostly low.3/ For 70% of the major benthic habitat types, the area of habitat potentially subject to a medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures.4/ Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
|
The D7 assessment, based on data on anthropogenic activities, highlighted significant variations in exposure to pressures:1/ The coastal zone and the plateau area are 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 (15% of the Western Mediterranean marine sub-region). However, the exposure index remains mostly low.3/ For 70% of the major benthic habitat types, the area of habitat potentially subject to a medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures.4/ Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
|
The D7 assessment, based on data on anthropogenic activities, highlighted significant variations in exposure to pressures:1/ The coastal zone and the plateau area are 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 (15% of the Western Mediterranean marine sub-region). However, the exposure index remains mostly low.3/ For 70% of the major benthic habitat types, the area of habitat potentially subject to a medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures.4/ Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
|
The D7 assessment, based on data on anthropogenic activities, highlighted significant variations in exposure to pressures:1/ The coastal zone and the plateau area are 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 (15% of the Western Mediterranean marine sub-region). However, the exposure index remains mostly low.3/ For 70% of the major benthic habitat types, the area of habitat potentially subject to a medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures.4/ Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
|
The D7 assessment, based on data on anthropogenic activities, highlighted significant variations in exposure to pressures:1/ The coastal zone and the plateau area are 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 (15% of the Western Mediterranean marine sub-region). However, the exposure index remains mostly low.3/ For 70% of the major benthic habitat types, the area of habitat potentially subject to a medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures.4/ Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
|
The D7 assessment, based on data on anthropogenic activities, highlighted significant variations in exposure to pressures:1/ The coastal zone and the plateau area are 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 (15% of the Western Mediterranean marine sub-region). However, the exposure index remains mostly low.3/ For 70% of the major benthic habitat types, the area of habitat potentially subject to a medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures.4/ Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
|
The D7 assessment, based on data on anthropogenic activities, highlighted significant variations in exposure to pressures:1/ The coastal zone and the plateau area are 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 (15% of the Western Mediterranean marine sub-region). However, the exposure index remains mostly low.3/ For 70% of the major benthic habitat types, the area of habitat potentially subject to a medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures.4/ Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
|
The D7 assessment, based on data on anthropogenic activities, highlighted significant variations in exposure to pressures:1/ The coastal zone and the plateau area are 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 (15% of the Western Mediterranean marine sub-region). However, the exposure index remains mostly low.3/ For 70% of the major benthic habitat types, the area of habitat potentially subject to a medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures.4/ Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
|
The D7 assessment, based on data on anthropogenic activities, highlighted significant variations in exposure to pressures:1/ The coastal zone and the plateau area are 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 (15% of the Western Mediterranean marine sub-region). However, the exposure index remains mostly low.3/ For 70% of the major benthic habitat types, the area of habitat potentially subject to a medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures.4/ Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
|
The D7 assessment, based on data on anthropogenic activities, highlighted significant variations in exposure to pressures:1/ The coastal zone and the plateau area are 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 (15% of the Western Mediterranean marine sub-region). However, the exposure index remains mostly low.3/ For 70% of the major benthic habitat types, the area of habitat potentially subject to a medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures.4/ 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 |
Related pressures |
|||||||||||||||||
Related targets |
MO Z200 (MWE-FR-MS-MO-Z200)
GES component |
D7
|
D7
|
D7
|
D7
|
D7
|
D7
|
D7
|
D7
|
D7
|
D7
|
D7
|
D7
|
D7
|
D7
|
D7
|
D7
|
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
Feature |
Hydrographical changes
|
Hydrographical changes
|
Hydrographical changes
|
Hydrographical changes
|
Hydrographical changes
|
Hydrographical changes
|
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 turbidity regime |
Changes in waves regime |
Circalittoral coarse sediment |
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 mud |
Offshore circalittoral sand |
Element code |
ExpPresCurrents |
ExpPresSalinity |
ExpPresSeabedNature |
ExpPresTemperature |
ExpPresTurbidity |
ExpPresWaves |
HabBenCircalitCoarSed |
HabBenCircalitRock |
HabBenCircalitSand |
HabBenInfralitCoarSed |
HabBenInfralitMud |
HabBenInfralitRock |
HabBenInfralitSand |
HabBenOffshCoarSed |
HabBenOffshMud |
HabBenOffshSand |
Element code source |
Link to other vocabulary or code lists that may be relevant
|
Link to other vocabulary or code lists that may be relevant
|
Link to other vocabulary or code lists that may be relevant
|
Link to other vocabulary or code lists that may be relevant
|
Link to other vocabulary or code lists that may be relevant
|
Link to other vocabulary or code lists that may be relevant
|
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 |
EU |
EU |
EU |
EU |
EU |
EU |
EU |
EU |
EU |
EU |
Criterion |
D7C1
|
D7C1
|
D7C1
|
D7C1
|
D7C1
|
D7C1
|
D7C2
|
D7C2
|
D7C2
|
D7C2
|
D7C2
|
D7C2
|
D7C2
|
D7C2
|
D7C2
|
D7C2
|
Parameter |
Extent
|
Extent
|
Extent
|
Extent
|
Extent
|
Extent
|
Extent
|
Extent
|
Extent
|
Extent
|
Extent
|
Extent
|
Extent
|
Extent
|
Extent
|
Extent
|
Parameter other |
||||||||||||||||
Threshold value upper |
||||||||||||||||
Threshold value lower |
||||||||||||||||
Threshold qualitative |
Not available yet
|
Not available yet
|
Not available yet
|
Not available yet
|
Not available yet
|
Not available yet
|
Not available yet
|
Not available yet
|
Not available yet
|
Not available yet
|
Not available yet
|
Not available yet
|
Not available yet
|
Not available yet
|
Not available yet
|
Not available yet
|
Threshold value source |
||||||||||||||||
Threshold value source other |
||||||||||||||||
Value achieved upper |
||||||||||||||||
Value achieved lower |
||||||||||||||||
Value unit |
||||||||||||||||
Value unit other |
||||||||||||||||
Proportion threshold value |
||||||||||||||||
Proportion value achieved |
110.0 |
10.0 |
12611.0 |
10.0 |
12605.0 |
110.0 |
375.0 |
23.0 |
631.0 |
11.0 |
54.0 |
34.0 |
409.0 |
10195.0 |
710.0 |
|
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 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 |
Parameter achieved |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Description parameter |
The metric considered for this parameter is the area of exposure for each pressure considered (overall or 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 110 km2 . The areas of exposure according to the four levels of exposure index are: No exposure: 14805 km² Low exposure index: 93 km² Medium exposure index: 14 km² High exposure index: 3 km² Note that no threshold is currently available to assess whether or not the parameter has been reached.
|
The metric considered for this parameter is the area of exposure for each pressure considered (overall or as a function of the level of the exposure index). The areas potentially affected by a change in 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: 14915 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 12611 km2 . The areas of exposure according to the four levels of exposure index are: No Exposure: 2304 km² Low Exposure Index: 12507 km² Medium Exposure Index: 104 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: 14915 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 the turbidity regime correspond to a total area of 12605 km2 . The areas of exposure according to the four levels of exposure index are: No exposure: 2310 km² Low exposure index: 12516 km² Medium exposure index: 90 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 110 km2 . The areas of exposure according to the four levels of exposure index are: No Exposure: 14805 km² Low Exposure Index: 107 km² Medium Exposure Index: 3 km² High Exposure Index: 0 km² Note that no threshold is currently available to assess whether or not the parameter has been reached.
|
The metric considered for this parameter is the area of 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 375 km2 (31% 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: 822 km².low risk of modification: 0 km².medium risk of modification: 375 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 23 km2 (57% 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: 17 km², low risk of modification: 23 km², medium risk of modification: 0 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 631 km2 (or 49% 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: 667 km².low risk of modification: 0 km².medium risk of modification: 605 km².high risk of modification: 26 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 11 km2 (31% 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: 26 km², low risk of modification: 0 km², medium risk of modification: 9 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 0 km2 (i.e. 0% 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: 3 km², low risk of modification: 0 km², medium risk of modification: 0 km², high risk of modification: 0 km², and no threshold is currently available to assess whether or not the parameter has been reached.
|
The metric considered for this parameter is the area of habitat potentially at risk (overall or based on the level of risk). The spatial extent of potential habitat alteration related to permanent changes in hydrographic conditions in this MRU is 54 km2 (33% 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: 109 km², low risk of modification: 51 km², medium risk of modification: 0 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 associated with permanent changes in hydrographic conditions in this MRU is 34 km2 (75% 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: 11 km², low risk of modification: 34 km², medium risk of modification: 0 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 409 km2 (or 99% 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: 3 km².low risk of modification: 55 km².medium risk of modification: 354 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 by level of risk). The spatial extent of potential habitat alteration due to permanent changes in hydrographic conditions in this MRU is 10195 km2 (>99% of assessed habitat). In addition, the indicator makes it possible to assess the intensity of the risk of modification: negligible or nil risk of modification: 23 km², low risk of modification: 2378 km², medium risk of modification: 7759 km², high risk of modification: 58 km², it should be noted that no threshold is currently available to assess whether or not the parameter has been reached.
|
The metric considered for this parameter is the area of habitat potentially at risk (overall or based on the level of risk). The spatial extent of potential habitat alteration associated with permanent changes in hydrographic conditions in this MRU is 710 km2 (55% 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: 576 km².low risk of modification: 419 km².medium risk of modification: 290 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 |
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 changes in current, wave, background, turbidity, thermal and salinity regimes. Indeed, the results show that the pressures associated with a change in current and wave regime have very little effect on the intermediate zone (1% of the total area of the MRU). Pressures related to a change in the bottom nature and turbidity regime potentially affect a very large area (>84% of the MRU). Exposure indices calculated for the change in background are mostly low, and more important for the change in turbidity regime are mostly medium. Finally, pressures related to a change in thermal and salinity regime affect less than 1% of the MRU.
|
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017) no threshold is to be specified for D7C1: the status of the D7C1 criterion is therefore not reported. However, the assessment of the D7C1 criterion has provided a first estimate of the exposure indices for spatial areas potentially affected by changes in current, wave, background, turbidity, thermal and salinity regimes. Indeed, the results show that the pressures associated with a change in current and wave regime have very little effect on the intermediate zone (1% of the total area of the MRU). Pressures related to a change in the bottom nature and turbidity regime potentially affect a very large area (>84% of the MRU). Exposure indices calculated for the change in background are mostly low, and more important for the change in turbidity regime are mostly medium. Finally, pressures related to a change in thermal and salinity regime affect less than 1% of the MRU.
|
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017) no threshold is to be specified for D7C1: the status of the D7C1 criterion is therefore not reported. However, the assessment of the D7C1 criterion has provided a first estimate of the exposure indices for spatial areas potentially affected by changes in current, wave, background, turbidity, thermal and salinity regimes. Indeed, the results show that the pressures associated with a change in current and wave regime have very little effect on the intermediate zone (1% of the total area of the MRU). Pressures related to a change in the bottom nature and turbidity regime potentially affect a very large area (>84% of the MRU). Exposure indices calculated for the change in background are mostly low, and more important for the change in turbidity regime are mostly medium. Finally, pressures related to a change in thermal and salinity regime affect less than 1% of the MRU.
|
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017) no threshold is to be specified for D7C1: the status of the D7C1 criterion is therefore not reported. However, the assessment of the D7C1 criterion has provided a first estimate of the exposure indices for spatial areas potentially affected by changes in current, wave, background, turbidity, thermal and salinity regimes. Indeed, the results show that the pressures associated with a change in current and wave regime have very little effect on the intermediate zone (1% of the total area of the MRU). Pressures related to a change in the bottom nature and turbidity regime potentially affect a very large area (>84% of the MRU). Exposure indices calculated for the change in background are mostly low, and more important for the change in turbidity regime are mostly medium. Finally, pressures related to a change in thermal and salinity regime affect less than 1% of the MRU.
|
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017) no threshold is to be specified for D7C1: the status of the D7C1 criterion is therefore not reported. However, the assessment of the D7C1 criterion has provided a first estimate of the exposure indices for spatial areas potentially affected by changes in current, wave, background, turbidity, thermal and salinity regimes. Indeed, the results show that the pressures associated with a change in current and wave regime have very little effect on the intermediate zone (1% of the total area of the MRU). Pressures related to a change in the bottom nature and turbidity regime potentially affect a very large area (>84% of the MRU). Exposure indices calculated for the change in background are mostly low, and more important for the change in turbidity regime are mostly medium. Finally, pressures related to a change in thermal and salinity regime affect less than 1% of the MRU.
|
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017) no threshold is to be specified for D7C1: the status of the D7C1 criterion is therefore not reported. However, the assessment of the D7C1 criterion has provided a first estimate of the exposure indices for spatial areas potentially affected by changes in current, wave, background, turbidity, thermal and salinity regimes. Indeed, the results show that the pressures associated with a change in current and wave regime have very little effect on the intermediate zone (1% of the total area of the MRU). Pressures related to a change in the bottom nature and turbidity regime potentially affect a very large area (>84% of the MRU). Exposure indices calculated for the change in background are mostly low, and more important for the change in turbidity regime are mostly medium. Finally, pressures related to a change in thermal and salinity regime affect less than 1% of the MRU.
|
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017), the D7C2 assessment must be carried out for each habitat type that is affected by changing hydrographic conditions and the D7C2 results are not integrated. On the other hand, no threshold has been defined so far for the parameter "Extent" and therefore the status of D7C2 is not reported, but the assessment of D7C2 has provided a first estimate of the spatial extent of benthic habitats potentially subject to cumulative risks of alteration, based on the indices of exposure to hydrographic pressures generated by human activities. Thus, the "Coastal circalittoral coarse sediment" habitat presents a large area at medium risk (31% of the total habitat area).
|
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017), the D7C2 assessment must be carried out for each habitat type that is affected by changing hydrographic conditions and the D7C2 results are not integrated. On the other hand, no threshold has been defined so far for the parameter "Extent" and therefore the status of D7C2 is not reported, but the assessment of D7C2 has provided a first estimate of the spatial extent of benthic habitats potentially subject to cumulative risks of alteration, based on the indices of exposure to hydrographic pressures generated by human activities. For example, the "Coastal circalittoral biogenic rocks and reefs" habitat presents a large area at low risk (57% 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, 2% of the total area of "Coastal circalittoral sands" habitat appears to be at high risk and 47% at medium risk.
|
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017), the D7C2 assessment must be carried out for each habitat type that is affected by changing hydrographic conditions and the D7C2 results are not integrated. On the other hand, no threshold has been defined so far for the parameter "Extent" and therefore the status of D7C2 is not reported, but the assessment of D7C2 has provided a first estimate of the spatial extent of benthic habitats potentially subject to cumulative risks of alteration, based on the indices of exposure to hydrographic pressures generated by human activities. Thus, "Coarse sediment infralittoral" habitat has the largest area at high risk (33% of the total habitat area) and a medium risk area of 11% of the habitat.
|
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017), the D7C2 assessment must be carried out for each habitat type that is affected by changing hydrographic conditions and the D7C2 results are not integrated. On the other hand, no threshold has been defined so far for the parameter "Extent" and therefore the status of D7C2 is not reported, but the assessment of D7C2 has provided a first estimate of the spatial extent of benthic habitats potentially subject to cumulative risks of alteration, based on the indices of exposure to hydrographic pressures generated by human activities. Thus, the "infralittoral mud flats" habitat does not appear to be at risk of alteration in the intermediate zone (100% of the total area of habitat subject to negligible or no 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 "Rocks and biogenic infralittoral reefs" habitat presents a low area at high risk (2% of the total habitat area), and 31% at low risk.
|
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017), the D7C2 assessment must be carried out for each habitat type that is affected by changing hydrographic conditions and the D7C2 results are not integrated. On the other hand, no threshold has been defined so far for the parameter "Extent" and therefore the status of D7C2 is not reported, but the assessment of D7C2 has provided a first estimate of the spatial extent of benthic habitats potentially subject to cumulative risks of alteration, based on the indices of exposure to hydrographic pressures generated by human activities. Thus, the "infralittoral sands" habitat presents a large area at low risk (75% 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, almost all of the "coarse circalittoral offshore sediment" habitat is impacted in the intermediate zone. It presents a large area at medium risk (86% of the total habitat area) and 13% at low risk.
|
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017), the D7C2 assessment must be carried out for each habitat type that is affected by changing hydrographic conditions and the D7C2 results are not integrated. On the other hand, no threshold has been defined so far for the parameter "Extent" and therefore the status of D7C2 is not reported, but the assessment of D7C2 has provided a first estimate of the spatial extent of benthic habitats potentially subject to cumulative risks of alteration, based on the indices of exposure to hydrographic pressures generated by human activities. Thus, the " circalittoral mud flats of the open sea " habitat is impacted in its entirety in the intermediate zone. It presents a large area at medium risk (76% of the total habitat area), 1% appears to be at high risk and 23% at low risk.
|
In accordance with the advice given in Guidance 14 (Walmsley, S.F., Weiss, A., Claussen, U., Connor, D. 2017 Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive, Integration of assessment results. ABPmer Report No R.2733, produced for the European Commission, DG Environment, February 2017), the D7C2 assessment must be carried out for each habitat type that is affected by changing hydrographic conditions and the D7C2 results are not integrated. On the other hand, no threshold has been defined so far for the parameter "Extent" and therefore the status of D7C2 is not reported, but the assessment of D7C2 has provided a first estimate of the spatial extent of benthic habitats potentially subject to cumulative risks of alteration, based on the indices of exposure to hydrographic pressures generated by human activities. Thus, 22.5% of the total area of offshore circalittoral sands habitat appears to be at medium risk and 32.5% at low risk.
|
Element status |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Description element |
The assessment of criterion D7C1 contributes to the assessment of criterion D7C2. Thus, the accumulation of quantified pressures (i.e., exposure indices) under D7C1 is incorporated into the calculation of the risk of modification of each habitat for the D7C2 assessment.
|
The assessment of criterion D7C1 contributes to the assessment of criterion D7C2. Thus, the accumulation of quantified pressures (i.e., exposure indices) under D7C1 is incorporated into the calculation of the risk of modification of each habitat for the D7C2 assessment.
|
The assessment of criterion D7C1 contributes to the assessment of criterion D7C2. Thus, the accumulation of quantified pressures (i.e., exposure indices) under D7C1 is incorporated into the calculation of the risk of modification of each habitat for the D7C2 assessment.
|
The assessment of criterion D7C1 contributes to the assessment of criterion D7C2. Thus, the accumulation of quantified pressures (i.e., exposure indices) under D7C1 is incorporated into the calculation of the risk of modification of each habitat for the D7C2 assessment.
|
The assessment of criterion D7C1 contributes to the assessment of criterion D7C2. Thus, the accumulation of quantified pressures (i.e., exposure indices) under D7C1 is incorporated into the calculation of the risk of modification of each habitat for the D7C2 assessment.
|
The assessment of criterion D7C1 contributes to the assessment of criterion D7C2. Thus, the accumulation of quantified pressures (i.e., exposure indices) under D7C1 is incorporated into the calculation of the risk of modification of each habitat for the D7C2 assessment.
|
In the absence of a threshold for the "Extent" parameter, the state of the habitat could not be provided. Furthermore, according to Decision 2017/848/EU, the results of the assessment of criterion D7C2 (estimated extent of adverse effects by habitat type in each assessment area) are used for the assessment of criterion D6C5. However, in the absence of an operational indicator at the level of Descriptor 6 - Benthic Habitats, these results could not be taken into account in the assessment of D6C5.
|
In the absence of a threshold for the "Extent" parameter, the state of the habitat could not be provided. Furthermore, according to Decision 2017/848/EU, the results of the assessment of criterion D7C2 (estimated extent of adverse effects by habitat type in each assessment area) are used for the assessment of criterion D6C5. However, in the absence of an operational indicator at the level of Descriptor 6 - Benthic Habitats, these results could not be taken into account in the assessment of D6C5.
|
In the absence of a threshold for the "Extent" parameter, the state of the habitat could not be provided. Furthermore, according to Decision 2017/848/EU, the results of the assessment of criterion D7C2 (estimated extent of adverse effects by habitat type in each assessment area) are used for the assessment of criterion D6C5. However, in the absence of an operational indicator at the level of Descriptor 6 - Benthic Habitats, these results could not be taken into account in the assessment of D6C5.
|
In the absence of a threshold for the "Extent" parameter, the state of the habitat could not be provided. Furthermore, according to Decision 2017/848/EU, the results of the assessment of criterion D7C2 (estimated extent of adverse effects by habitat type in each assessment area) are used for the assessment of criterion D6C5. However, in the absence of an operational indicator at the level of Descriptor 6 - Benthic Habitats, these results could not be taken into account in the assessment of D6C5.
|
In the absence of a threshold for the "Extent" parameter, the state of the habitat could not be provided. Furthermore, according to Decision 2017/848/EU, the results of the assessment of criterion D7C2 (estimated extent of adverse effects by habitat type in each assessment area) are used for the assessment of criterion D6C5. However, in the absence of an operational indicator at the level of Descriptor 6 - Benthic Habitats, these results could not be taken into account in the assessment of D6C5.
|
In the absence of a threshold for the "Extent" parameter, the state of the habitat could not be provided. Furthermore, according to Decision 2017/848/EU, the results of the assessment of criterion D7C2 (estimated extent of adverse effects by habitat type in each assessment area) are used for the assessment of criterion D6C5. However, in the absence of an operational indicator at the level of Descriptor 6 - Benthic Habitats, these results could not be taken into account in the assessment of D6C5.
|
In the absence of a threshold for the "Extent" parameter, the state of the habitat could not be provided. Furthermore, according to Decision 2017/848/EU, the results of the assessment of criterion D7C2 (estimated extent of adverse effects by habitat type in each assessment area) are used for the assessment of criterion D6C5. However, in the absence of an operational indicator at the level of Descriptor 6 - Benthic Habitats, these results could not be taken into account in the assessment of D6C5.
|
In the absence of a threshold for the "Extent" parameter, the state of the habitat could not be provided. Furthermore, according to Decision 2017/848/EU, the results of the assessment of criterion D7C2 (estimated extent of adverse effects by habitat type in each assessment area) are used for the assessment of criterion D6C5. However, in the absence of an operational indicator at the level of Descriptor 6 - Benthic Habitats, these results could not be taken into account in the assessment of D6C5.
|
In the absence of a threshold for the "Extent" parameter, the state of the habitat could not be provided. Furthermore, according to Decision 2017/848/EU, the results of the assessment of criterion D7C2 (estimated extent of adverse effects by habitat type in each assessment area) are used for the assessment of criterion D6C5. However, in the absence of an operational indicator at the level of Descriptor 6 - Benthic Habitats, these results could not be taken into account in the assessment of D6C5.
|
In the absence of a threshold for the "Extent" parameter, the state of the habitat could not be provided. Furthermore, according to Decision 2017/848/EU, the results of the assessment of criterion D7C2 (estimated extent of adverse effects by habitat type in each assessment area) are used for the assessment of criterion D6C5. However, in the absence of an operational indicator at the level of Descriptor 6 - Benthic Habitats, these results could not be taken into account in the assessment of D6C5.
|
Integration rule type parameter |
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Integration rule description parameter |
||||||||||||||||
Integration rule type criteria |
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Integration rule description criteria |
||||||||||||||||
GES extent threshold |
||||||||||||||||
GES extent achieved |
||||||||||||||||
GES extent unit |
||||||||||||||||
GES achieved |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Description overall status |
The D7 assessment, based on data on anthropogenic activities, highlighted significant variations in exposure to pressures:1/ The coastal zone and the plateau area are 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 (15% of the Western Mediterranean marine sub-region). However, the exposure index remains mostly low.3/ For 70% of the major benthic habitat types, the area of habitat potentially subject to a medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures.4/ Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
|
The D7 assessment, based on data on anthropogenic activities, highlighted significant variations in exposure to pressures:1/ The coastal zone and the plateau area are 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 (15% of the Western Mediterranean marine sub-region). However, the exposure index remains mostly low.3/ For 70% of the major benthic habitat types, the area of habitat potentially subject to a medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures.4/ Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
|
The D7 assessment, based on data on anthropogenic activities, highlighted significant variations in exposure to pressures:1/ The coastal zone and the plateau area are 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 (15% of the Western Mediterranean marine sub-region). However, the exposure index remains mostly low.3/ For 70% of the major benthic habitat types, the area of habitat potentially subject to a medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures.4/ Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
|
The D7 assessment, based on data on anthropogenic activities, highlighted significant variations in exposure to pressures:1/ The coastal zone and the plateau area are 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 (15% of the Western Mediterranean marine sub-region). However, the exposure index remains mostly low.3/ For 70% of the major benthic habitat types, the area of habitat potentially subject to a medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures.4/ Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
|
The D7 assessment, based on data on anthropogenic activities, highlighted significant variations in exposure to pressures:1/ The coastal zone and the plateau area are 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 (15% of the Western Mediterranean marine sub-region). However, the exposure index remains mostly low.3/ For 70% of the major benthic habitat types, the area of habitat potentially subject to a medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures.4/ Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
|
The D7 assessment, based on data on anthropogenic activities, highlighted significant variations in exposure to pressures:1/ The coastal zone and the plateau area are 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 (15% of the Western Mediterranean marine sub-region). However, the exposure index remains mostly low.3/ For 70% of the major benthic habitat types, the area of habitat potentially subject to a medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures.4/ Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
|
The D7 assessment, based on data on anthropogenic activities, highlighted significant variations in exposure to pressures:1/ The coastal zone and the plateau area are 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 (15% of the Western Mediterranean marine sub-region). However, the exposure index remains mostly low.3/ For 70% of the major benthic habitat types, the area of habitat potentially subject to a medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures.4/ Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
|
The D7 assessment, based on data on anthropogenic activities, highlighted significant variations in exposure to pressures:1/ The coastal zone and the plateau area are 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 (15% of the Western Mediterranean marine sub-region). However, the exposure index remains mostly low.3/ For 70% of the major benthic habitat types, the area of habitat potentially subject to a medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures.4/ Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
|
The D7 assessment, based on data on anthropogenic activities, highlighted significant variations in exposure to pressures:1/ The coastal zone and the plateau area are 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 (15% of the Western Mediterranean marine sub-region). However, the exposure index remains mostly low.3/ For 70% of the major benthic habitat types, the area of habitat potentially subject to a medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures.4/ Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
|
The D7 assessment, based on data on anthropogenic activities, highlighted significant variations in exposure to pressures:1/ The coastal zone and the plateau area are 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 (15% of the Western Mediterranean marine sub-region). However, the exposure index remains mostly low.3/ For 70% of the major benthic habitat types, the area of habitat potentially subject to a medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures.4/ Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
|
The D7 assessment, based on data on anthropogenic activities, highlighted significant variations in exposure to pressures:1/ The coastal zone and the plateau area are 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 (15% of the Western Mediterranean marine sub-region). However, the exposure index remains mostly low.3/ For 70% of the major benthic habitat types, the area of habitat potentially subject to a medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures.4/ Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
|
The D7 assessment, based on data on anthropogenic activities, highlighted significant variations in exposure to pressures:1/ The coastal zone and the plateau area are 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 (15% of the Western Mediterranean marine sub-region). However, the exposure index remains mostly low.3/ For 70% of the major benthic habitat types, the area of habitat potentially subject to a medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures.4/ Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
|
The D7 assessment, based on data on anthropogenic activities, highlighted significant variations in exposure to pressures:1/ The coastal zone and the plateau area are 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 (15% of the Western Mediterranean marine sub-region). However, the exposure index remains mostly low.3/ For 70% of the major benthic habitat types, the area of habitat potentially subject to a medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures.4/ Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
|
The D7 assessment, based on data on anthropogenic activities, highlighted significant variations in exposure to pressures:1/ The coastal zone and the plateau area are 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 (15% of the Western Mediterranean marine sub-region). However, the exposure index remains mostly low.3/ For 70% of the major benthic habitat types, the area of habitat potentially subject to a medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures.4/ Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
|
The D7 assessment, based on data on anthropogenic activities, highlighted significant variations in exposure to pressures:1/ The coastal zone and the plateau area are 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 (15% of the Western Mediterranean marine sub-region). However, the exposure index remains mostly low.3/ For 70% of the major benthic habitat types, the area of habitat potentially subject to a medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures.4/ Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
|
The D7 assessment, based on data on anthropogenic activities, highlighted significant variations in exposure to pressures:1/ The coastal zone and the plateau area are 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 (15% of the Western Mediterranean marine sub-region). However, the exposure index remains mostly low.3/ For 70% of the major benthic habitat types, the area of habitat potentially subject to a medium to high risk of modification is greater than 30% of the total area of habitat, as a result of cumulative exposure to hydrographic pressures.4/ Finally, it is important to specify that the incompleteness and uncertainties associated with the input data, as well as the use of expert opinion and subjective decision rules, imply a significant propagation of uncertainty throughout the treatment carried out. The results should therefore be taken with caution.
|
Assessments period |
2012-2018 |
2012-2018 |
2012-2018 |
2012-2018 |
2012-2018 |
2012-2018 |
2012-2018 |
2012-2018 |
2012-2018 |
2012-2018 |
2012-2018 |
2012-2018 |
2012-2018 |
2012-2018 |
2012-2018 |
2012-2018 |
Related pressures |
||||||||||||||||
Related targets |