Member State report / Art8 / 2018 / D6 / Italy / Mediterranean: Adriatic 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 | D6 Sea-floor integrity/D1 Benthic habitats |
Member State | Italy |
Region/subregion | Mediterranean: Adriatic Sea |
Reported by | ISPRA - Italian National Institute for Environmental Protection and Research |
Report date | 2020-10-01 |
Report access | MSFD_2018_ART8_GES_IT_2020-07-31.xml |
Mediterranean Sea: Adriatic Sea (IT-AS-0001)
GES component |
D6
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D6
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D6
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D6
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D6
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D6
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D6
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D6
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D6
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D6
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D6
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D6
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D6
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D6
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D6
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D6
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D6
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D6
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Feature |
Benthic broad habitats
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Other benthic habitats
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Other benthic habitats
|
Other benthic habitats
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Other benthic habitats
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Other benthic habitats
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Other benthic habitats
|
Other benthic habitats
|
Other benthic habitats
|
Other benthic habitats
|
Other benthic habitats
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Other benthic habitats
|
Other benthic habitats
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Other benthic habitats
|
Other benthic habitats
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Other benthic habitats
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Physical disturbance to seabed
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Physical loss of the seabed
|
Element |
Coralligenous habitat |
Coralligenous habitat |
Coralligenous habitat |
Maerl beds |
Maerl beds |
Maerl beds |
Posidonia beds (Posidonion oceanicae) |
Posidonia beds (Posidonion oceanicae) |
Posidonia beds (Posidonion oceanicae) |
Soft bottom non biogenic habitat |
Soft bottom non biogenic habitat |
Soft bottom non biogenic habitat |
White Corals |
White Corals |
White Corals |
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Element code |
CORALLIG |
CORALLIG |
CORALLIG |
MAERL |
MAERL |
MAERL |
1120 |
1120 |
1120 |
SOFT-BOTT |
SOFT-BOTT |
SOFT-BOTT |
WHITECOR |
WHITECOR |
WHITECOR |
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Element code source |
Link to other vocabulary or code lists that may be relevant
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Link to other vocabulary or code lists that may be relevant
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Link to other vocabulary or code lists that may be relevant
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Link to other vocabulary or code lists that may be relevant
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Link to other vocabulary or code lists that may be relevant
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Link to other vocabulary or code lists that may be relevant
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Link to other vocabulary or code lists that may be relevant
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Link to other vocabulary or code lists that may be relevant
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Link to other vocabulary or code lists that may be relevant
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Link to other vocabulary or code lists that may be relevant
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Link to other vocabulary or code lists that may be relevant
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Link to other vocabulary or code lists that may be relevant
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Link to other vocabulary or code lists that may be relevant
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Link to other vocabulary or code lists that may be relevant
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Link to other vocabulary or code lists that may be relevant
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Element 2 |
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Element 2 code |
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Element 2 code source |
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Element source |
EU |
EU |
EU |
EU |
EU |
EU |
EU |
EU |
EU |
EU |
EU |
EU |
EU |
EU |
EU |
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Criterion |
D6C1
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D6C3
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D6C4
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D6C5
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D6C3
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D6C4
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D6C5
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D6C3
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D6C4
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D6C5
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D6C3
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D6C4
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D6C5
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D6C3
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D6C4
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D6C5
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D6C2
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D6C1
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Parameter |
Extent
|
Extent
|
Extent
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Habitat condition
|
Extent
|
Extent
|
Habitat condition
|
Extent
|
Extent
|
Habitat condition
|
Extent
|
Extent
|
Habitat condition
|
Extent
|
Extent
|
Habitat condition
|
Extent
|
Extent
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Parameter other |
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Threshold value upper |
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Threshold value lower |
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Threshold qualitative |
The habitat must be mantained at the current extent |
The habitat must be mantained at the current extent |
The habitat must be mantained at the current extent |
The habitat must be mantained at the current extent |
The habitat must be mantained at the current extent |
The habitat must be mantained at the current extent |
The habitat must be mantained at the current extent |
The habitat must be mantained at the current extent |
The habitat must be mantained at the current extent |
At least 10% of the areas currently exploitable by benthic impacting fishing gears must not suffer of further adverse impacts |
At least 10% of the areas currently exploitable by benthic impacting fishing gears must not suffer of further adverse impacts |
At least 10% of the areas currently exploitable by benthic impacting fishing gears must not suffer of further adverse impacts |
The habitat must be mantained at the current extent |
The habitat must be mantained at the current extent |
The habitat must be mantained at the current extent |
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Threshold value source |
National
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National
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National
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National
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National
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National
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National
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National
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National
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National
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National
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National
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National
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National
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National
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Threshold value source other |
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Value achieved upper |
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Value achieved lower |
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Value unit |
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Value unit other |
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Proportion threshold value |
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Proportion value achieved |
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Proportion threshold value unit |
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Trend |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Parameter achieved |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Description parameter |
in the next monitoring cycle data will allow to assess the feature |
in the next monitoring cycle data will allow to assess the feature |
in the next monitoring cycle data will allow to assess the feature |
in the next monitoring cycle data will allow to assess the feature |
in the next monitoring cycle data will allow to assess the feature |
in the next monitoring cycle data will allow to assess the feature |
in the next monitoring cycle data will allow to assess the feature |
in the next monitoring cycle data will allow to assess the feature |
in the next monitoring cycle data will allow to assess the feature |
in the next monitoring cycle data will allow to assess the feature |
in the next monitoring cycle data will allow to assess the feature |
in the next monitoring cycle data will allow to assess the feature |
in the next monitoring cycle data will allow to assess the feature |
in the next monitoring cycle data will allow to assess the feature |
in the next monitoring cycle data will allow to assess the feature |
in the next monitoring cycle data will allow to assess the feature |
in the next monitoring cycle data will allow to assess the feature |
in the next monitoring cycle data will allow to assess the feature |
Related indicator |
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Criteria status |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Description criteria |
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Element status |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
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Description element |
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Integration rule type parameter |
Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Integration rule description parameter |
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Integration rule type criteria |
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Integration rule description criteria |
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GES extent threshold |
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GES extent achieved |
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GES extent unit |
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GES achieved |
Not assessed |
GES expected to be achieved later than 2020, no Article 14 exception reported |
GES expected to be achieved later than 2020, no Article 14 exception reported |
GES expected to be achieved later than 2020, no Article 14 exception reported |
GES expected to be achieved later than 2020, no Article 14 exception reported |
GES expected to be achieved later than 2020, no Article 14 exception reported |
GES expected to be achieved later than 2020, no Article 14 exception reported |
GES expected to be achieved later than 2020, no Article 14 exception reported |
GES expected to be achieved later than 2020, no Article 14 exception reported |
GES expected to be achieved later than 2020, no Article 14 exception reported |
GES expected to be achieved later than 2020, no Article 14 exception reported |
GES expected to be achieved later than 2020, no Article 14 exception reported |
GES expected to be achieved later than 2020, no Article 14 exception reported |
GES expected to be achieved later than 2020, no Article 14 exception reported |
GES expected to be achieved later than 2020, no Article 14 exception reported |
GES expected to be achieved later than 2020, no Article 14 exception reported |
GES expected to be achieved later than 2020, no Article 14 exception reported |
GES expected to be achieved later than 2020, no Article 14 exception reported |
Description overall status |
State-of-the-art monitoring data, bibliographical sources and modelling seabed habitat map does not allow to assess each of the benthic broad habitat types. Spatial resolution gives information on the presence but it is not enough to assess the spatial extent of each habitat type which is adversely affected |
Data on the extension of the soft bottom biogenic substrates (Maerl) are not available; therefore it is not possible to establish nor if such substrates are subjected to a pressure that generates physical damage / physical loss nor is it possible to establish a significant pressure threshold. A lack of data regarding the extension of biogenic substrates with adequate spatial resolution has been found. In fact, the mapping of the habitats available today, which is essential to monitor any changes, is the one published in EMODNET (European Marine Observation and Data Network) which provides a habitat map based on modeling, and does not have an effective habitat classification for our purposes (for example, Maerl flow into the class of debris), or a detail useful for comparison with data on fishing activities that interact actively with substate (trawling, fishing with rapid and hydraulic dredgers). |
Data on the extension of the soft bottom biogenic substrates (Maerl) are not available; therefore it is not possible to establish nor if such substrates are subjected to a pressure that generates physical damage / physical loss nor is it possible to establish a significant pressure threshold. A lack of data regarding the extension of biogenic substrates with adequate spatial resolution has been found. In fact, the mapping of the habitats available today, which is essential to monitor any changes, is the one published in EMODNET (European Marine Observation and Data Network) which provides a habitat map based on modeling, and does not have an effective habitat classification for our purposes (for example, Maerl flow into the class of debris), or a detail useful for comparison with data on fishing activities that interact actively with substate (trawling, fishing with rapid and hydraulic dredgers). |
Data on the extension of the soft bottom biogenic substrates (Maerl) are not available; therefore it is not possible to establish nor if such substrates are subjected to a pressure that generates physical damage / physical loss nor is it possible to establish a significant pressure threshold. A lack of data regarding the extension of biogenic substrates with adequate spatial resolution has been found. In fact, the mapping of the habitats available today, which is essential to monitor any changes, is the one published in EMODNET (European Marine Observation and Data Network) which provides a habitat map based on modeling, and does not have an effective habitat classification for our purposes (for example, Maerl flow into the class of debris), or a detail useful for comparison with data on fishing activities that interact actively with substate (trawling, fishing with rapid and hydraulic dredgers). |
Data on the extension of the soft bottom biogenic substrates (Maerl) are not available; therefore it is not possible to establish nor if such substrates are subjected to a pressure that generates physical damage / physical loss nor is it possible to establish a significant pressure threshold. A lack of data regarding the extension of biogenic substrates with adequate spatial resolution has been found. In fact, the mapping of the habitats available today, which is essential to monitor any changes, is the one published in EMODNET (European Marine Observation and Data Network) which provides a habitat map based on modeling, and does not have an effective habitat classification for our purposes (for example, Maerl flow into the class of debris), or a detail useful for comparison with data on fishing activities that interact actively with substate (trawling, fishing with rapid and hydraulic dredgers). |
Data on the extension of the soft bottom biogenic substrates (Maerl) are not available; therefore it is not possible to establish nor if such substrates are subjected to a pressure that generates physical damage / physical loss nor is it possible to establish a significant pressure threshold. A lack of data regarding the extension of biogenic substrates with adequate spatial resolution has been found. In fact, the mapping of the habitats available today, which is essential to monitor any changes, is the one published in EMODNET (European Marine Observation and Data Network) which provides a habitat map based on modeling, and does not have an effective habitat classification for our purposes (for example, Maerl flow into the class of debris), or a detail useful for comparison with data on fishing activities that interact actively with substate (trawling, fishing with rapid and hydraulic dredgers). |
Data on the extension of the soft bottom biogenic substrates (Maerl) are not available; therefore it is not possible to establish nor if such substrates are subjected to a pressure that generates physical damage / physical loss nor is it possible to establish a significant pressure threshold. A lack of data regarding the extension of biogenic substrates with adequate spatial resolution has been found. In fact, the mapping of the habitats available today, which is essential to monitor any changes, is the one published in EMODNET (European Marine Observation and Data Network) which provides a habitat map based on modeling, and does not have an effective habitat classification for our purposes (for example, Maerl flow into the class of debris), or a detail useful for comparison with data on fishing activities that interact actively with substate (trawling, fishing with rapid and hydraulic dredgers). |
Data on the extension of the soft bottom biogenic substrates (Maerl) are not available; therefore it is not possible to establish nor if such substrates are subjected to a pressure that generates physical damage / physical loss nor is it possible to establish a significant pressure threshold. A lack of data regarding the extension of biogenic substrates with adequate spatial resolution has been found. In fact, the mapping of the habitats available today, which is essential to monitor any changes, is the one published in EMODNET (European Marine Observation and Data Network) which provides a habitat map based on modeling, and does not have an effective habitat classification for our purposes (for example, Maerl flow into the class of debris), or a detail useful for comparison with data on fishing activities that interact actively with substate (trawling, fishing with rapid and hydraulic dredgers). |
Data on the extension of the soft bottom biogenic substrates (Maerl) are not available; therefore it is not possible to establish nor if such substrates are subjected to a pressure that generates physical damage / physical loss nor is it possible to establish a significant pressure threshold. A lack of data regarding the extension of biogenic substrates with adequate spatial resolution has been found. In fact, the mapping of the habitats available today, which is essential to monitor any changes, is the one published in EMODNET (European Marine Observation and Data Network) which provides a habitat map based on modeling, and does not have an effective habitat classification for our purposes (for example, Maerl flow into the class of debris), or a detail useful for comparison with data on fishing activities that interact actively with substate (trawling, fishing with rapid and hydraulic dredgers). |
Data on the extension of the soft bottom biogenic substrates (Maerl) are not available; therefore it is not possible to establish nor if such substrates are subjected to a pressure that generates physical damage / physical loss nor is it possible to establish a significant pressure threshold. A lack of data regarding the extension of biogenic substrates with adequate spatial resolution has been found. In fact, the mapping of the habitats available today, which is essential to monitor any changes, is the one published in EMODNET (European Marine Observation and Data Network) which provides a habitat map based on modeling, and does not have an effective habitat classification for our purposes (for example, Maerl flow into the class of debris), or a detail useful for comparison with data on fishing activities that interact actively with substate (trawling, fishing with rapid and hydraulic dredgers). |
Data on the extension of the soft bottom biogenic substrates (Maerl) are not available; therefore it is not possible to establish nor if such substrates are subjected to a pressure that generates physical damage / physical loss nor is it possible to establish a significant pressure threshold. A lack of data regarding the extension of biogenic substrates with adequate spatial resolution has been found. In fact, the mapping of the habitats available today, which is essential to monitor any changes, is the one published in EMODNET (European Marine Observation and Data Network) which provides a habitat map based on modeling, and does not have an effective habitat classification for our purposes (for example, Maerl flow into the class of debris), or a detail useful for comparison with data on fishing activities that interact actively with substate (trawling, fishing with rapid and hydraulic dredgers). |
Data on the extension of the soft bottom biogenic substrates (Maerl) are not available; therefore it is not possible to establish nor if such substrates are subjected to a pressure that generates physical damage / physical loss nor is it possible to establish a significant pressure threshold. A lack of data regarding the extension of biogenic substrates with adequate spatial resolution has been found. In fact, the mapping of the habitats available today, which is essential to monitor any changes, is the one published in EMODNET (European Marine Observation and Data Network) which provides a habitat map based on modeling, and does not have an effective habitat classification for our purposes (for example, Maerl flow into the class of debris), or a detail useful for comparison with data on fishing activities that interact actively with substate (trawling, fishing with rapid and hydraulic dredgers). |
Data on the extension of the soft bottom biogenic substrates (Maerl) are not available; therefore it is not possible to establish nor if such substrates are subjected to a pressure that generates physical damage / physical loss nor is it possible to establish a significant pressure threshold. A lack of data regarding the extension of biogenic substrates with adequate spatial resolution has been found. In fact, the mapping of the habitats available today, which is essential to monitor any changes, is the one published in EMODNET (European Marine Observation and Data Network) which provides a habitat map based on modeling, and does not have an effective habitat classification for our purposes (for example, Maerl flow into the class of debris), or a detail useful for comparison with data on fishing activities that interact actively with substate (trawling, fishing with rapid and hydraulic dredgers). |
Data on the extension of the soft bottom biogenic substrates (Maerl) are not available; therefore it is not possible to establish nor if such substrates are subjected to a pressure that generates physical damage / physical loss nor is it possible to establish a significant pressure threshold. A lack of data regarding the extension of biogenic substrates with adequate spatial resolution has been found. In fact, the mapping of the habitats available today, which is essential to monitor any changes, is the one published in EMODNET (European Marine Observation and Data Network) which provides a habitat map based on modeling, and does not have an effective habitat classification for our purposes (for example, Maerl flow into the class of debris), or a detail useful for comparison with data on fishing activities that interact actively with substate (trawling, fishing with rapid and hydraulic dredgers). |
Data on the extension of the soft bottom biogenic substrates (Maerl) are not available; therefore it is not possible to establish nor if such substrates are subjected to a pressure that generates physical damage / physical loss nor is it possible to establish a significant pressure threshold. A lack of data regarding the extension of biogenic substrates with adequate spatial resolution has been found. In fact, the mapping of the habitats available today, which is essential to monitor any changes, is the one published in EMODNET (European Marine Observation and Data Network) which provides a habitat map based on modeling, and does not have an effective habitat classification for our purposes (for example, Maerl flow into the class of debris), or a detail useful for comparison with data on fishing activities that interact actively with substate (trawling, fishing with rapid and hydraulic dredgers). |
Data on the extension of the soft bottom biogenic substrates (Maerl) are not available; therefore it is not possible to establish nor if such substrates are subjected to a pressure that generates physical damage / physical loss nor is it possible to establish a significant pressure threshold. A lack of data regarding the extension of biogenic substrates with adequate spatial resolution has been found. In fact, the mapping of the habitats available today, which is essential to monitor any changes, is the one published in EMODNET (European Marine Observation and Data Network) which provides a habitat map based on modeling, and does not have an effective habitat classification for our purposes (for example, Maerl flow into the class of debris), or a detail useful for comparison with data on fishing activities that interact actively with substate (trawling, fishing with rapid and hydraulic dredgers). |
Data on the extension of the soft bottom biogenic substrates (Maerl) are not available; therefore it is not possible to establish nor if such substrates are subjected to a pressure that generates physical damage / physical loss nor is it possible to establish a significant pressure threshold. A lack of data regarding the extension of biogenic substrates with adequate spatial resolution has been found. In fact, the mapping of the habitats available today, which is essential to monitor any changes, is the one published in EMODNET (European Marine Observation and Data Network) which provides a habitat map based on modeling, and does not have an effective habitat classification for our purposes (for example, Maerl flow into the class of debris), or a detail useful for comparison with data on fishing activities that interact actively with substate (trawling, fishing with rapid and hydraulic dredgers). |
Data on the extension of the soft bottom biogenic substrates (Maerl) are not available; therefore it is not possible to establish nor if such substrates are subjected to a pressure that generates physical damage / physical loss nor is it possible to establish a significant pressure threshold. A lack of data regarding the extension of biogenic substrates with adequate spatial resolution has been found. In fact, the mapping of the habitats available today, which is essential to monitor any changes, is the one published in EMODNET (European Marine Observation and Data Network) which provides a habitat map based on modeling, and does not have an effective habitat classification for our purposes (for example, Maerl flow into the class of debris), or a detail useful for comparison with data on fishing activities that interact actively with substate (trawling, fishing with rapid and hydraulic dredgers). |
Assessments period |
2012-2017 |
2012-2017 |
2012-2017 |
2012-2017 |
2012-2017 |
2012-2017 |
2012-2017 |
2012-2017 |
2012-2017 |
2012-2017 |
2012-2017 |
2012-2017 |
2012-2017 |
2012-2017 |
2012-2017 |
2012-2017 |
2012-2017 |
2012-2017 |
Related pressures |
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Related targets |
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